2025-068 Cooper Creek USACE September 05,2025 Report No. 2025-068
INFORMAL STAFF REPORT
TO MAYOR AND CITY COUNCIL
SUBJECT:
This informal staff report will provide information regarding the City's participation in the United
States Army Corps of Engineers' (USACE) study of the Cooper Creek watershed through the
Continuing Authorities Program(CAP) Section 205 and include an overview of the results of the
study.
BACKGROUND:
The USACE CAP Section 205 is a program which allows the USACE to partner with a nonfederal
sponsor to plan and construct small flood damage reduction projects that have not previously been
specifically authorized by Congress and are not part of a larger project. The purpose of the CAP
is to plan and implement projects of limited size, cost, scope and complexity.
The City of Denton Environmental Services and Sustainability Department submitted a letter on
June 29, 2023, to the USACE Fort Worth requesting assistance for a study to address flooding in
the Cooper Creek watershed. The USACE Fort Worth District chose Cooper Creek for a feasibility
study authorized under the CAP Section 205. The purpose of this feasibility study was to evaluate
potential flood reduction projects at a high level. If a cost-effective project was identified,it would
advance to design and construction under the CAP. The estimated cost of the study was $600,000.
CAP requires a cost share of a 50% match after the first $100,000. The Federal share for this
project was estimated at $350,000 and the City of Denton's share of the projected costs was
estimated at $250,000. On March 5, 2024, City Council approved agenda item ID24-243 which
allowed the City Manager to enter into a Feasibility Cost Sharing Agreement (FCSA) with the
USACE and contribute $250,000 for the City's portion of the cost share.
DISCUSSION:
As USACE staff performed the feasibility analysis within Cooper Creek, City staff offered
continual support and input, regularly met with USACE staff to provide information on historic
flooding issues, utility conflicts, real estate acquisition processes, previous drainage studies, etc.
During the feasibility analysis USACE staff created updated hydrologic and hydraulic models of
the Cooper Creek watershed. The USACE also evaluated a wide variety of potential actions to
reduce flood damage near the creek; including additional regional detention, channel
improvements, bridge and culvert modifications, elevating at-risk structures, and structure
buyouts.
The feasibility analysis was concluded in February 2025. The USACE was unable to find potential
projects that achieved a positive cost-benefit ratio score and recommended that no Federal action
be taken. The USACE completed a closeout report that included the updated hydrologic and
hydraulic models developed by the USACE that were provided to City staff for future use. It is
important to note that many of the alternatives considered would have a positive effect on reducing
flood risk within the Cooper Creek watershed, and while the alternatives did not achieve a positive
cost-benefit ratio using the USACE methodology they may still inform future capital
September 05,2025 Report No. 2025-068
improvements in the area. Upon close-out of the feasibility analysis $118,030.43 in unspent funds
were returned to the City.
ATTACHMENTS:
CAP Section 205 Fact Sheet
ID 24-243 ordinance
Cooper Creek CAP 205 Closeout Report
STAFF CONTACT:
Mike Linder
Senior Engineer—Engineering
Mike.Lindergcityofdenton.com
(940)-349-8942
PARTICIPATING DEPARTMENTS: Engineering
STAFF TIME TO COMPLETE REPORT: 6 hours
CONTINUING AUTHORITIES PROGRAM
me Section 205 -Small Flood Risk Management Projects
U.S. ARMY CORPS OF ENGINEERS
Scope and Authority
• The U.S.Army Corps of Engineers(USACE)can partner with a non-
federal sponsor(sponsor)to plan and construct small flood damage
reduction projects that have not previously been specifically authorized
by Congress and are not part of a larger project.
•Projects may be structural(e.g.,levees,flood walls,diversion -
channels,pumping plants and bridge modifications)or non-structural -
(e.g.,floodproofing,relocation of structures and flood warning }
systems).
•Authority is provided by Section 205 of the Flood Control Act of -
1948(P.L. 80-858),as amended,also referred to as Section 205 under
the Continuing Authorities Program.
Project Development Process
•Feasibility Study-Upon receipt of a written Letter of Intent(LOI) from a potential sponsor and when funding is
available,USACE initiates a Federal Interest Determination, at federal expense,to determine if a potential project meets
program requirements and federal participation is justified. If a federal interest is verified, a feasibility study will be
advanced to identify and comprehensively evaluate alternatives and recommend a plan for implementation. If the
feasibility study cost exceeds $100,000,USACE and sponsor sign a Feasibility Cost Share Agreement and a project
management plan that describes the study cost share arrangement, study scope, schedule, and study cost estimate(See
Project Costs).
•Design and Construction-A project is approved for construction if the detailed feasibility study determines it is
technically feasible,environmentally acceptable,and cost effective.Before engineering design and construction can begin,
USACE and sponsor negotiate and sign a Project Partnership Agreement that describes the cost share arrangement and
operations and maintenance responsibilities(See Project Costs).
Project Costs
The maximum federal expenditure per project is$15 million,including feasibility study,design and construction costs.
Feasibility Study •The study is initiated with up to$100,000 in federal funds.
•Costs exceeding$100,000 are cost shared 50 percent federal and 50 percent sponsor.
• Sponsor's cost share may include cash,work-in-kind or a combination of both.
Design and Construction •Most projects are cost-shared 65 percent federal and 35 percent sponsor but sponsor cost
could increase to 50%with high costs for lands, easements,rights-of-way,relocations, and
dredged material disposal areas(LERRDs).
• Sponsor must provide all LERRDs needed for project construction and maintenance.
•At least 5 percent of the cost share requirement must be provided in cash.
Operation and Maintenance • Sponsor is responsible for all project operation and maintenance costs when the project is
completed.
How to Request a Project
A template LOI to request a study under the Continuing Authorities Program is available on the USACE Planning web site.
U.S. ARMY CORPS OF ENGINEERS
Questions?Contact your local USACE District:
https://usace.maps.arcgis.com/apps/webappviewer/index.html?id=7344e62432694199af7790aa47a32fdd
ORDINANCE NO. 24-243
AN ORDINANCE OF THE CITY OF DENTON APPROVING AND AUTHORIZING THE
CITY MANAGER TO EXECUTE AN AGREEMENT WITH THE DEPARTMENT OF THE
ARMY FORT WORTH DISTRICT UNDER THE CONTINUING AUTHORITIES PROGRAM
(CAP) SECTION 205 TO STUDY,DETERMINE CAUSE, AND FIND A SOLUTION TO THE
FLOODING OF COOPER CREEK AND THE ADJACENT AREAS; AND DECLARING AN
EFFECTIVE DATE.
WHEREAS, the CAP supports smaller community projects and allows the Fort Worth
District to plan, design, and construct projects of limited size, cost, scope, and complexity; and
WHEREAS, the CAP is ideal for funding projects for flood risk management, ecosystem
restoration, erosion control, and streambank protection; and
WHEREAS, Cooper Creek, located in the Elm Fork Trinity River watershed, is
experiencing accelerated erosion, loss of riparian trees, and damage to private property during
large rain events; and
WHEREAS,the City of Denton submitted a Letter of Request on June 29, 2023,to the US
Army Corps of Engineers(USACE)providing notice of the issue and requesting assistance; and
WHEREAS,the USACE has conducted a site investigation and determined federal interest
in the project; and
WHEREAS, the US Department of the Army (Government) has projected the cost of the
study to be $600,000, the grant provides funding for the first $100,000, and requires the Non-
Federal Sponsor to cost share at 50 percent(50%) of the remaining costs estimated at$250,000;
WHEREAS, any additional funds above the estimated amount must be remitted to the
Government after final accounting, and any excess funds shall be refunded subject to the
availability of funds;
NOW THEREFORE,
THE COUNCIL OF THE CITY OF DENTON HEREBY ORDAINS:
SECTION 1. The recitals are hereby incorporated and made part of this ordinance for all
purposes.
SECTION 2. The City Manager or their designee is hereby authorized to execute the
agreement with the Department of the Army attached hereto as Exhibit"A" authorizing the City,
through the Environmental Services and Sustainability Department, to spend its share of the cost
of the study in accordance with the authorized purposes cited in the agreement.
SECTION 3. This ordinance shall become effective immediately upon its passage and
approval.
The motion to approve this ordinance was made by (�C&.a Kjjpr'bI . and seconded
by Ct, 11 c Gt , the ordinance was passed and approved by the following
vote
Aye Nay Abstain Absent
Mayor Gerard Hudspeth: J
Vicki Byrd,District 1:
Brian Beck,District 2: ✓
Paul Meltzer,District 3: ✓
Joe Holland,District 4: L/
Brandon Chase McGee,At Large Place 5:
Chris Watts,At Large Place 6:
PASSED AND APPROVED this the s day of ...), , 2024.
GERA HUDSPETH,MAYOR
ATTEST:
JESUS SALAZAR, CITY SECRETARY
B JJ-� �� O• '�'
APPROVED AS TO LEGAL FORM: 4L •• .;�•�}�
MACK REINWAND, CITYDigitally signed ATTORNEY e
SDk do-corn,do-citycMenton,
do-cod ad,ou-Department Users and
Groups,ou-General Government,
2KeIler auu4Kler�Yofdent comBY: p0 '
AGREEMENT
BETWEEN
THE DEPARTMENT OF THE ARMY
AND
CITY OF DENTON, TEXAS
FOR THE
COOPER CREEK, CONTINUING AUTHORITIES PROGRAM SECTION 205
THIS AGREEMENT is entered into this day of , by and
between the Department of the Army (hereinafter the "Government"), represented by the District
Commander for Fort Worth District(hereinafter the "District Commander") and the City of
Denton, Texas (hereinafter the"Non-Federal Sponsor"),represented by the City Manager.
WITNESSETH,THAT:
WHEREAS, Section 205 of the Flood Control Act of 1948, as amended(33 U.S.C.
701 s)] authorizes the study of Cooper Creek located within the city of Denton, Texas to address
flooding issues;
WHEREAS, Section 105(a) of the Water Resources Development Act(WRDA) of 1986,
as amended(33 U.S.C. 2215(a)), specifies the cost-sharing requirements; and
WHEREAS, the Government and the Non-Federal Sponsor have the full authority and
capability to perform in accordance with the terms of this Agreement.
NOW, THEREFORE,the parties agree as follows:
ARTICLE I - DEFINITIONS
A. The term"Study"means the activities and tasks required to identify and evaluate
alternatives and the preparation of a Detailed Project Report that, as appropriate, recommends a
coordinated and implementable solution for the flooding issues on Cooper Creek and the
adjacent areas in the City of Denton, Denton County, Texas.
B. The term"study costs"means all costs incurred by the Government and Non-Federal
Sponsor after the effective date of this Agreement that are directly related to performance of the
Study and cost shared in accordance with the terms of this Agreement. The term includes the
Government's costs for preparing the project management plan("PMP"); for plan formulation
and evaluation, including costs for economic, engineering, real estate, and environmental
analyses; for preparation of a floodplain management plan if undertaken as part of the Study; for
preparing and processing the Detailed Project Report; for supervision and administration; for
Agency Technical Review and other review processes required by the Government;and for
response to any required Independent External Peer Review; and the Non-Federal Sponsor's
creditable costs for in-kind contributions, if any. The term does not include any costs for dispute
resolution;participation by the Government and Non-Federal Sponsor in the Study Coordination
Team to discuss significant issues and actions;audits; an Independent External Peer Review panel,
if required; or negotiating this Agreement. The term also does not include the first$100,000 of
costs for the Study incurred by the Government,whether before or after execution of this
Agreement.
C. The term"PMP"means the project management plan, and any modifications thereto,
developed in consultation with the Non-Federal Sponsor,that specifies the scope, cost,and schedule
for Study activities and tasks,including the Non-Federal Sponsor's in-kind contributions, and that
guides the performance of the Study.
D. The term"in-kind contributions"means those planning activities (including data
collection and other services)that are integral to the Study and would otherwise have been
undertaken by the Government for the Study and that are identified in the PMP and performed or
provided by the Non-Federal Sponsor after the effective date of this Agreement and in
accordance with the PMP.
E. The term"maximum Federal study cost"means the $1,500,000 Federal cost limit for
the Study, unless the Government has approved a higher amount, and includes the first $100,000
of costs for the Study incurred by the Government.
F. The term"fiscal year"means one year beginning on October 1'and ending on
September 30th of the following year.
ARTICLE II- OBLIGATIONS OF THE PARTIES
A. In accordance with Federal laws, regulations, and policies,the Government shall
conduct the Study using funds appropriated by the Congress and funds provided by the Non-
Federal Sponsor. In carrying out its obligations under this Agreement,the Non-Federal Sponsor
shall comply with all the requirements of applicable Federal laws and implementing regulations,
including but not limited to, if applicable, Section 601 of the Civil Rights Act of 1964, as
amended(42 U.S.C.2000d), and Department of Defense Directive 5500.11 issued pursuant
thereto;the Age Discrimination Act of 1975 (42 U.S.C. 6102); and the Rehabilitation Act of
1973, as amended (29 U.S.C. 794), and Army Regulation 600-7 issued pursuant thereto.
B. The Non-Federal Sponsor shall contribute 50 percent of study costs in accordance
with the provisions of this paragraph and provide required funds in accordance with Article III.
1. After considering the estimated amount of credit for in-kind contributions, if
any,that will be afforded in accordance with paragraph C. of this Article and the first$100,000
of the costs incurred by the Government that are excluded from study costs,the Government
shall provide the Non-Federal Sponsor with a written estimate of the amount of funds required
from the Non-Federal Sponsor to meet its share of study costs for the remainder of the initial
fiscal year of the Study. No later than 15 calendar days after such notification,the Non-Federal
Sponsor shall provide the full amount of such funds to the Government in accordance with
Article III.C.
2. No later than August 1st prior to each subsequent fiscal year of the Study, the
Government shall provide the Non-Federal Sponsor with a written estimate of the amount of
funds required from the Non-Federal Sponsor during that fiscal year to meet its cost share. No
later than September 1st prior to that fiscal year,the Non-Federal Sponsor shall provide the full
amount of such required funds to the Government in accordance with Article III.C.
C. The Government shall include in study costs and credit towards the Non-Federal
Sponsor's share of such costs,the costs, documented to the satisfaction of the Government,that
the Non-Federal Sponsor incurs in providing or performing in-kind contributions, including
associated supervision and administration, after the effective date of this Agreement. Such costs
shall be subject to audit in accordance with Article VI to determine reasonableness, allocability,
and allowability, and crediting shall be in accordance with the following procedures,
requirements, and limitations:
1. As in-kind contributions are completed and no later than 60 calendar days after
such completion,the Non-Federal Sponsor shall provide the Government appropriate
documentation, including invoices and certification of specific payments to contractors,
suppliers, and the Non-Federal Sponsor's employees. Failure to provide such documentation in
a timely manner may result in denial of credit. The amount of credit afforded for in-kind
contributions shall not exceed the Non-Federal Sponsor's share of study costs.
2. No credit shall be afforded for interest charges, or any adjustment to reflect
changes in price levels between the time the in-kind contributions are completed, and credit is
afforded; for the value of in-kind contributions obtained at no cost to the Non-Federal Sponsor;
for any items provided or performed prior to completion of the PMP; or for costs that exceed the
Government's estimate of the cost for such item.
D. To the extent practicable and in accordance with Federal laws, regulations, and
policies,the Government shall afford the Non-Federal Sponsor the opportunity to review and
comment on contract solicitations prior to the Government's issuance of such solicitations;
proposed contract modifications, including change orders; and contract claims prior to resolution
thereof. Ultimately,the contents of solicitations, award of contracts, execution of contract
modifications, and resolution of contract claims shall be exclusively within the control of the
Government.
E. The Non-Federal Sponsor shall not use Federal program funds to meet any of its
obligations under this Agreement unless the Federal agency providing the funds verifies in
writing that the funds are authorized to be used for the Study. Federal program funds are those
funds provided by a Federal agency,plus any non-Federal contribution required as a matching
share therefor.
F. Except as provided in paragraph C. of this Article,the Non-Federal Sponsor shall not
be entitled to any credit or reimbursement for costs it incurs in performing its responsibilities
under this Agreement.
G. If Independent External Peer Review(IEPR) is required for the Study, the Government
shall conduct such review in accordance with Federal laws,regulations, and policies. The
Government's costs for an IEPR panel shall not be included in study costs or the maximum Federal
study cost.
H. In addition to the ongoing,regular discussions between the parties regarding Study
delivery,the Government and the Non-Federal Sponsor may establish a Study Coordination
Team to discuss significant issues or actions. The Government's costs for participation on the
Study Coordination Team shall not be included in the study costs but shall be included in
calculating the maximum Federal study cost. The Non-Federal Sponsor's costs for participation
on the Study Coordination Team shall not be included in study costs and shall be paid solely by
the Non-Federal Sponsor without reimbursement or credit by the Government.
ARTICLE III -PROVISION OF NON-FEDERAL COST SHARE
A. As of the effective date of this Agreement, study costs are projected to be $600,000,
with the Government's share of such costs projected to be $350,000 and the Non-Federal
Sponsor's share of such costs projected to be $250,000, which includes creditable in-kind
contributions projected to be $0, and the amount of funds required to meet its cost share
projected to be $250,000. These amounts are estimates only that are subject to adjustment by the
Government and are not to be construed as the total financial responsibilities of the Government
and the Non-Federal Sponsor.
B. The Government shall provide the Non-Federal Sponsor with monthly reports setting
forth the estimated study costs and the Government's and Non-Federal Sponsor's estimated
shares of such costs; costs incurred by the Government, using both Federal and Non-Federal
Sponsor funds,to date;the amount of funds provided by the Non-Federal Sponsor to date; the
estimated amount of any creditable in-kind contributions; and the estimated remaining cost of the
Study.
C. The Non-Federal Sponsor shall provide to the Government required funds by
delivering a check payable to "FAO, USAED, Fort Worth District(M2)to the District
Commander, or verifying to the satisfaction of the Government that the Non-Federal Sponsor has
deposited such required funds in an escrow or other account acceptable to the Government, with
interest accruing to the Non-Federal Sponsor, or by providing an Electronic Funds Transfer of
such required funds in accordance with procedures established by the Government.
D. The Government shall draw from the funds provided by the Non-Federal Sponsor to
cover the non-Federal share of study costs as those costs are incurred. If the Government
determines at any time that additional funds are needed from the Non-Federal Sponsor to cover
the Non-Federal Sponsor's required share of study costs,the Government shall provide the Non-
Federal Sponsor with written notice of the amount of additional funds required. Within 60
calendar days of such notice,the Non-Federal Sponsor shall provide the Government with the
full amount of such additional funds.
E. Upon completion of the Study and resolution of all relevant claims and appeals, the
Government shall conduct a final accounting and furnish the Non-Federal Sponsor with the
written results of such final accounting. Should the final accounting determine that additional
funds are required from the Non-Federal Sponsor, the Non-Federal Sponsor,within 60 calendar
days of written notice from the Government, shall provide the Government with the full amount
of such additional funds by delivering a check payable to "FAO, USAED,Fort Worth District
(M2)to the District Commander, or by providing an Electronic Funds Transfer of such required
funds in accordance with procedures established by the Government. Should the final
accounting determine that the Non-Federal Sponsor has provided funds in excess of its required
amount,the Government shall refund the excess amount, subject to the availability of funds.
Such final accounting does not limit the Non-Federal Sponsor's responsibility to pay its share of
study costs, including contract claims or any other liability that may become known after the
final accounting.
ARTICLE IV- TERMINATION OR SUSPENSION
A. Upon 30 calendar days written notice to the other party, either party may elect at any
time,without penalty,to suspend or terminate future performance of the Study. Furthermore,
unless an extension is approved by the Assistant Secretary of the Army (Civil Works),the Study
may be terminated if a Detailed Project Report is not completed for the Study within 3 years
after the effective date of this Agreement.
B. In the event of termination,the parties shall conclude their activities relating to the
Study. To provide for this eventuality,the Government may reserve a percentage of available
funds as a contingency to pay the costs of termination, including any costs of resolution of
contract claims, and resolution of contract modifications.
C. Any suspension or termination shall not relieve the parties of liability for any
obligation incurred. Any delinquent payment owed by the Non-Federal Sponsor pursuant to this
Agreement shall be charged interest at a rate,to be determined by the Secretary of the Treasury,
equal to 150 per centum of the average bond equivalent rate of the 13 week Treasury bills
auctioned immediately prior to the date on which such payment became delinquent, or auctioned
immediately prior to the beginning of each additional 3 month period if the period of
delinquency exceeds 3 months.
ARTICLE V- DISPUTE RESOLUTION
As a condition precedent to a parry bringing any suit for breach of this Agreement, that
parry must first notify the other party in writing of the nature of the purported breach and seek in
good faith to resolve the dispute through negotiation. If the parties cannot resolve the dispute
through negotiation,they may agree to a mutually acceptable method of non-binding alternative
dispute resolution with a qualified third party acceptable to the parties. Each parry shall pay an
equal share of any costs for the services provided by such a third party as such costs are incurred.
The existence of a dispute shall not excuse the parties from performance pursuant to this
Agreement.
ARTICLE VI -MAINTENANCE OF RECORDS AND AUDIT
A. The parties shall develop procedures for the maintenance by the Non-Federal Sponsor
of books,records, documents, or other evidence pertaining to costs and expenses for a minimum
of three years after the final accounting. The Non-Federal Sponsor shall assure that such
materials are reasonably available for examination, audit, or reproduction by the Government.
B. The Government may conduct, or arrange for the conduct of, audits of the Study.
Government audits shall be conducted in accordance with applicable Government cost principles
and regulations. The Government's costs of audits for the Study shall not be included in study
costs but shall be included in calculating the maximum Federal study cost.
C. To the extent permitted under applicable Federal laws and regulations, the
Government shall allow the Non-Federal Sponsor to inspect books, records, documents, or other
evidence pertaining to costs and expenses maintained by the Government, or at the Non-Federal
Sponsor's request, provide to the Non-Federal Sponsor or independent auditors any such
information necessary to enable an audit of the Non-Federal Sponsor's activities under this
Agreement. The Non-Federal Sponsor shall pay the costs of non-Federal audits without
reimbursement or credit by the Government.
ARTICLE VII -RELATIONSHIP OF PARTIES
In the exercise of their respective rights and obligations under this Agreement,the
Government, and the Non-Federal Sponsor each act in an independent capacity, and neither is to
be considered the officer, agent, or employee of the other. Neither parry shall provide,without
the consent of the other party, any contractor with a release that waives or purports to waive any
rights a party may have to seek relief or redress against that contractor.
ARTICLE VIII -NOTICES
A. Any notice,request, demand, or other communication required or permitted to be
given under this Agreement shall be deemed to have been duly given if in writing and delivered
personally or mailed by registered or certified mail, with return receipt, as follows:
If to the Non-Federal Sponsor:
City Manager
City of Denton
215 E.McKinney St,
Denton, TX 76201
If to the Government:
District Commander
U.S.Army Corps of Engineers, Fort Worth District
819 Taylor Street
Fort Worth,TX 76102
B. A party may change the recipient or address to which such communications are to be
directed by giving written notice to the other party in the manner provided in this Article.
ARTICLE IX - CONFIDENTIALITY
To the extent permitted by the laws governing each parry,the parties agree to maintain
the confidentiality of exchanged information when requested to do so by the providing parry.
ARTICLE X-THIRD PARTY RIGHTS, BENEFITS, OR LIABILITIES
Nothing in this Agreement is intended,nor may be construed,to create any rights, confer
any benefits, or relieve any liability, of any kind whatsoever in any third person not a party to
this Agreement.
ARTICLE XI- OBLIGATIONS OF FUTURE APPROPRIATIONS
The Non-Federal Sponsor intends to fulfill fully its obligations under this Agreement.
Nothing herein shall constitute,nor be deemed to constitute, an obligation of future
appropriations by the City of Denton,where creating such an obligation would be inconsistent
with constitutional or statutory limitation on committing future appropriations. If the
Non-Federal Sponsor is unable to, or does not, fulfill its obligations under this Agreement,the
Government may exercise any legal rights it has to protect the Government's interests.
IN WITNESS WHEREOF,the parties hereto have executed this Agreement,which shall
become effective upon the date it is signed by the District Commander.
DEPARTMENT OF THE ARMY CITY OF DENTON
BY: BY:
Calvin A.Kroeger Sara Hensley
Colonel,U.S.Army City Manager
Commanding
DATE: DATE:
AGREEMENT
BETWEEN
THE DEPARTMENT OF THE ARMY
AND
CITY OF DENTON,TEXAS
FOR THE
COOPER CREEK, CONTINUING AUTHORITIES PROGRAM SECTION 205
THIS AGREEMENT is entered into this 5L day of KPy�1 ,g2A, by and
between the Department of the Army (hereinafter the"Government"), represented by the District
Commander for Fort Worth District(hereinafter the"District Commander")and the City of
Denton, Texas (hereinafter the"Non-Federal Sponsor"), represented by the City Manager.
WITNESSETH, THAT:
WHEREAS, Section 205 of the Flood Control Act of 1948, as amended (33 U.S.C.
701 s)] authorizes the study of Cooper Creek located within the city of Denton, Texas to address
flooding issues;
WHEREAS, Section 105(a)of the Water Resources Development Act(WRDA)of 1986,
as amended (33 U.S.C. 2215(a)), specifies the cost-sharing requirements; and
WHEREAS,the Government and the Non-Federal Sponsor have the full authority and
capability to perform in accordance with the terms of this Agreement.
NOW, THEREFORE, the parties agree as follows:
ARTICLE I - DEFINITIONS
A. The term"Study"means the activities and tasks required to identify and evaluate
alternatives and the preparation of a Detailed Project Report that, as appropriate, recommends a
coordinated and implementable solution for the flooding issues on Cooper Creek and the
adjacent areas in the City of Denton, Denton County, Texas.
B. The term"study costs"means all costs incurred by the Government and Non-Federal
Sponsor after the effective date of this Agreement that are directly related to performance of the
Study and cost shared in accordance with the terms of this Agreement. The term includes the
Government's costs for preparing the project management plan ("PMP"); for plan formulation
and evaluation, including costs for economic, engineering, real estate, and environmental
analyses; for preparation of a floodplain management plan if undertaken as part of the Study; for
preparing and processing the Detailed Project Report; for supervision and administration; for
Agency Technical Review and other review processes required by the Government;and for
response to any required Independent External Peer Review;and the Non-Federal Sponsor's
creditable costs for in-kind contributions, if any. The term does not include any costs for dispute
resolution; participation by the Government and Non-Federal Sponsor in the Study Coordination
Team to discuss significant issues and actions;audits;an Independent External Peer Review panel,
if required; or negotiating this Agreement. The term also does not include the first$100,000 of
costs for the Study incurred by the Government,whether before or after execution of this
Agreement.
C. The term"PMP"means the project management plan, and any modifications thereto,
developed in consultation with the Non-Federal Sponsor,that specifies the scope,cost,and schedule
for Study activities and tasks, including the Non-Federal Sponsor's in-kind contributions,and that
guides the performance of the Study.
D. The term "in-kind contributions"means those planning activities (including data
collection and other services)that are integral to the Study and would otherwise have been
undertaken by the Government for the Study and that are identified in the PMP and performed or
provided by the Non-Federal Sponsor after the effective date of this Agreement and in
accordance with the PMP.
E. The term "maximum Federal study cost"means the $1,500,000 Federal cost limit for
the Study, unless the Government has approved a higher amount, and includes the first$100,000
of costs for the Study incurred by the Government.
F. The term "fiscal year"means one year beginning on October 11 and ending on
September 30th of the following year.
ARTICLE II - OBLIGATIONS OF THE PARTIES
A. In accordance with Federal laws, regulations, and policies,the Government shall
conduct the Study using funds appropriated by the Congress and funds provided by the Non-
Federal Sponsor. In carrying out its obligations under this Agreement,the Non-Federal Sponsor
shall comply with all the requirements of applicable Federal laws and implementing regulations,
including but not limited to, if applicable, Section 601 of the Civil Rights Act of 1964, as
amended (42 U.S.C. 2000d),and Department of Defense Directive 5500.11 issued pursuant
thereto; the Age Discrimination Act of 1975 (42 U.S.C. 6102); and the Rehabilitation Act of
1973, as amended (29 U.S.C. 794), and Army Regulation 600-7 issued pursuant thereto.
B. The Non-Federal Sponsor shall contribute 50 percent of study costs in accordance
with the provisions of this paragraph and provide required funds in accordance with Article III.
1. After considering the estimated amount of credit for in-kind contributions, if
any, that will be afforded in accordance with paragraph C. of this Article and the first$100,000
of the costs incurred by the Government that are excluded from study costs, the Government
shall provide the Non-Federal Sponsor with a written estimate of the amount of funds required
from the Non-Federal Sponsor to meet its share of study costs for the remainder of the initial
fiscal year of the Study. No later than 15 calendar days after such notification, the Non-Federal
Sponsor shall provide the full amount of such funds to the Government in accordance with
Article III.C.
2. No later than August 1'prior to each subsequent fiscal year of the Study,the
Government shall provide the Non-Federal Sponsor with a written estimate of the amount of
funds required from the Non-Federal Sponsor during that fiscal year to meet its cost share. No
later than September 1 It
prior to that fiscal year,the Non-Federal Sponsor shall provide the full
amount of such required funds to the Government in accordance with Article ❑I.C.
C. The Government shall include in study costs and credit towards the Non-Federal
Sponsor's share of such costs, the costs,documented to the satisfaction of the Government, that
the Non-Federal Sponsor incurs in providing or performing in-kind contributions, including
associated supervision and administration, after the effective date of this Agreement. Such costs
shall be subject to audit in accordance with Article VI to determine reasonableness, ailocability,
and allowability, and crediting shall be in accordance with the following procedures,
requirements, and limitations:
1. As in-kind contributions are completed and no later than 60 calendar days after
such completion,the Non-Federal Sponsor shall provide the Government appropriate
documentation, including invoices and certification of specific payments to contractors,
suppliers, and the Non-Federal Sponsor's employees. Failure to provide such documentation in
a timely manner may result in denial of credit. The amount of credit afforded for in-kind
contributions shall not exceed the Non-Federal Sponsor's share of study costs.
2. No credit shall be afforded for interest charges, or any adjustment to reflect
changes in price levels between the time the in-kind contributions are completed,and credit is
afforded; for the value of in-kind contributions obtained at no cost to the Non-Federal Sponsor;
for any items provided or performed prior to completion of the PMP; or for costs that exceed the
Government's estimate of the cost for such item.
D. To the extent practicable and in accordance with Federal laws, regulations,and
policies, the Government shall afford the Non-Federal Sponsor the opportunity to review and
comment on contract solicitations prior to the Government's issuance of such solicitations;
proposed contract modifications, including change orders; and contract claims prior to resolution
thereof. Ultimately, the contents of solicitations,award of contracts, execution of contract
modifications, and resolution of contract claims shall be exclusively within the control of the
Government.
E. The Non-Federal Sponsor shall not use Federal program funds to meet any of its
obligations under this Agreement unless the Federal agency providing the funds verifies in
writing that the funds are authorized to be used for the Study. Federal program funds are those
funds provided by a Federal agency, plus any non-Federal contribution required as a matching
share therefor.
F. Except as provided in paragraph C. of this Article, the Non-Federal Sponsor shall not
be entitled to any credit or reimbursement for costs it incurs in performing its responsibilities
under this Agreement.
G. If Independent External Peer Review(IEPR) is required for the Study,the Government
shall conduct such review in accordance with Federal laws,regulations,and policies. The
Government's costs for an IEPR panel shall not be included in study costs or the maximum Federal
study cost.
H. In addition to the ongoing, regular discussions between the parties regarding Study
delivery, the Government and the Non-Federal Sponsor may establish a Study Coordination
Team to discuss significant issues or actions. The Government's costs for participation on the
Study Coordination Team shall not be included in the study costs but shall be included in
calculating the maximum Federal study cost. The Non-Federal Sponsor's costs for participation
on the Study Coordination Team shall not be included in study costs and shall be paid solely by
the Non-Federal Sponsor without reimbursement or credit by the Government.
ARTICLE III - PROVISION OF NON-FEDERAL COST SHARE
A. As of the effective date of this Agreement, study costs are projected to be$600,000,
with the Government's share of such costs projected to be $350,000 and the Non-Federal
Sponsor's share of such costs projected to be$250,000, which includes creditable in-kind
contributions projected to be $0, and the amount of funds required to meet its cost share
projected to be $250,000. These amounts are estimates only that are subject to adjustment by the
Government and are not to be construed as the total financial responsibilities of the Government
and the Non-Federal Sponsor.
B. The Government shall provide the Non-Federal Sponsor with monthly reports setting
forth the estimated study costs and the Government's and Non-Federal Sponsor's estimated
shares of such costs; costs incurred by the Government, using both Federal and Non-Federal
Sponsor funds, to date; the amount of funds provided by the Non-Federal Sponsor to date;the
estimated amount of any creditable in-kind contributions; and the estimated remaining cost of the
Study.
C. The Non-Federal Sponsor shall provide to the Government required funds by
delivering a check payable to"FAO, USAED, Fort Worth District(M2)to the District
Commander, or verifying to the satisfaction of the Government that the Non-Federal Sponsor has
deposited such required funds in an escrow or other account acceptable to the Government,with
interest accruing to the Non-Federal Sponsor,or by providing an Electronic Funds Transfer of
such required funds in accordance with procedures established by the Government.
D. The Government shall draw from the funds provided by the Non-Federal Sponsor to
cover the non-Federal share of study costs as those costs are incurred. If the Government
determines at any time that additional funds are needed from the Non-Federal Sponsor to cover
the Non-Federal Sponsor's required share of study costs, the Government shall provide the Non-
Federal Sponsor with written notice of the amount of additional funds required. Within 60
calendar days of such notice,the Non-Federal Sponsor shall provide the Government with the
full amount of such additional funds.
E. Upon completion of the Study and resolution of all relevant claims and appeals,the
Government shall conduct a final accounting and furnish the Non-Federal Sponsor with the
written results of such final accounting. Should the final accounting determine that additional
funds are required from the Non-Federal Sponsor, the Non-Federal Sponsor,within 60 calendar
days of written notice from the Government, shall provide the Government with the full amount
of such additional funds by delivering a check payable to"FAO, USAED, Fort Worth District
(M2)to the District Commander, or by providing an Electronic Funds Transfer of such required
funds in accordance with procedures established by the Government. Should the final
accounting determine that the Non-Federal Sponsor has provided funds in excess of its required
amount, the Government shall refund the excess amount, subject to the availability of funds.
Such final accounting does not limit the Non-Federal Sponsor's responsibility to pay its share of
study costs, including contract claims or any other liability that may become known after the
final accounting.
ARTICLE IV-TERMINATION OR SUSPENSION
A. Upon 30 calendar days written notice to the other party, either party may elect at any
time,without penalty, to suspend or terminate future performance of the Study. Furthermore,
unless an extension is approved by the Assistant Secretary of the Army(Civil Works),the Study
may be terminated if a Detailed Project Report is not completed for the Study within 3 years
after the effective date of this Agreement.
B. In the event of termination,the parties shall conclude their activities relating to the
Study. To provide for this eventuality, the Government may reserve a percentage of available
funds as a contingency to pay the costs of termination, including any costs of resolution of
contract claims, and resolution of contract modifications.
C. Any suspension or termination shall not relieve the parties of liability for any
obligation incurred. Any delinquent payment owed by the Non-Federal Sponsor pursuant to this
Agreement shall be charged interest at a rate,to be determined by the Secretary of the Treasury,
equal to 150 per centum of the average bond equivalent rate of the 13 week Treasury bills
auctioned immediately prior to the date on which such payment became delinquent, or auctioned
immediately prior to the beginning of each additional 3 month period if the period of
delinquency exceeds 3 months.
ARTICLE V - DISPUTE RESOLUTION
As a condition precedent to a party bringing any suit for breach of this Agreement, that
party must first notify the other party in writing of the nature of the purported breach and seek in
good faith to resolve the dispute through negotiation. If the parties cannot resolve the dispute
through negotiation, they may agree to a mutually acceptable method of non-binding alternative
dispute resolution with a qualified third party acceptable to the parties. Each party shall pay an
equal share of any costs for the services provided by such a third party as such costs are incurred.
The existence of a dispute shall not excuse the parties from performance pursuant to this
Agreement.
ARTICLE VI - MAINTENANCE OF RECORDS AND AUDIT
A. The parties shall develop procedures for the maintenance by the Non-Federal Sponsor
of books, records, documents, or other evidence pertaining to costs and expenses for a minimum
of three years after the final accounting. The Non-Federal Sponsor shall assure that such
materials are reasonably available for examination, audit,or reproduction by the Government.
B. The Government may conduct, or arrange for the conduct of, audits of the Study.
Government audits shall be conducted in accordance with applicable Government cost principles
and regulations. The Government's costs of audits for the Study shall not be included in study
costs but shall be included in calculating the maximum Federal study cost.
C. To the extent permitted under applicable Federal laws and regulations, the
Government shall allow the Non-Federal Sponsor to inspect books, records, documents,or other
evidence pertaining to costs and expenses maintained by the Government, or at the Non-Federal
Sponsor's request, provide to the Non-Federal Sponsor or independent auditors any such
information necessary to enable an audit of the Non-Federal Sponsor's activities under this
Agreement. The Non-Federal Sponsor shall pay the costs of non-Federal audits without
reimbursement or credit by the Government.
ARTICLE VII - RELATIONSHIP OF PARTIES
In the exercise of their respective rights and obligations under this Agreement, the
Government, and the Non-Federal Sponsor each act in an independent capacity, and neither is to
be considered the officer, agent,or employee of the other. Neither party shall provide, without
the consent of the other party, any contractor with a release that waives or purports to waive any
rights a party may have to seek relief or redress against that contractor.
ARTICLE VIII -NOTICES
A. Any notice, request, demand, or other communication required or permitted to be
given under this Agreement shall be deemed to have been duly given if in writing and delivered
personally or mailed by registered or certified mail,with return receipt, as follows:
If to the Non-Federal Sponsor:
City Manager
City of Denton
215 E. McKinney St,
Denton, TX 76201
If to the Govemmcnt:
District Commander
U.S.Army Corps of Engineers, Fort Worth District
819 Taylor Street
Fort Worth,TX 76102
B. A party may change the recipient or address to which such communications are to be
directed by giving written notice to the other party in the manner provided in this Article.
ARTICLE IX-CONFIDENTIALITY
To the extent permitted by the laws governing each parry,the parties agree to maintain
the confidentiality of exchanged information when requested to do so by the providing party.
ARTICLE X-THIRD PARTY RIGHTS,BENEFITS,OR LIABILITIES
Nothing in this Agreement is intended,nor may be construed,to create any rights,confer
any benefits,or relieve any liability,of any kind whatsoever in any third person not a party to
this Agreement.
ARTICLE XI-OBLIGATIONS OF FUTURE APPROPRIATIONS
The Non-Federal Sponsor intends to fulfill fully its obligations under this Agreement.
Nothing herein shall constitute,nor be deemed to constitute,an obligation of future
appropriations by the City of Denton,where creating such an obligation would be inconsistent
with constitutional or statutory limitation on committing future appropriations. If the
Non-Federal Sponsor is unable to,or does not,fulfill its obligations under this Agreement,the
Government may exercise any legal rights it has to protect the Government's interests.
IN WITNESS WHEREOF,the parties hereto have executed this Agreement,which shall
become effective upon the date it is signed by the District Commander.
DEPARThfl NET OF THE ARMY CITY OF DENT
BY:�i`I'f• BY:
Calvin A.Kroeger Hensley Fir
Colonel,U.S.Army City Manager J'*"
Commanding
DATE: DE ofAeft XOtf- DATE: /1+,4kcX 2�6 262
Closeout Report
CAP - Cooper Creek, Denton, Texas,
Section 205
Fort Worth District, Southwestern
Division
135
February 2025
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DEPARTMENT OF THE ARMY
U.S.ARMY CORPS OF ENGINEERS, FORT WORTH DISTRICT
P. O. BOX 17300
FORT WORTH, TEXAS 76102
Closeout Report
CAP — Cooper Creek, Denton, Texas, Section 205
Fort Worth District, Southwestern Division
February 2025
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Executive Summary
This report examines the need for construction of flood risk management measures along
Cooper Creek in Denton, Texas and determines the feasibility of Federal participation in the
potential improvements.
Cooper Creek is located In the northern part of the City of Denton, Texas. The creek flows in a
southeasterly direction though the city and terminates at Lewisville Lake. The creek is generally
small but well defined, mostly unimproved channel with several tributaries. The main channel
has an average depth of 6 feet, a top width of 50 feet and a slope of 25 feet per mile. The creek
is normally dry with flow occurring during periods of heavy rainfall. There are several culvert
crossings that have limited capacity and cause backwater conditions within the stream channel.
The 100-year floodplain generally extends beyond the stream. Existing detention ponds were
constructed within Cooper Creek watershed to reduce flood damages along the creek. There is
some channel erosion along Cooper Creek due to high velocities in the channel.
This study evaluated a number of alternatives based on economics, engineering, environmental,
and other factors. No Alternative was identified that produced positive net National Economic
Development benefits. Comprehensive benefits were analyzed, however, the lack of benefits
across all categories led the team to recommend no Federal action. The non-Federal partner
(City of Denton) supports the recommendation.
ES-1
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ES-2
Table of Contents
1. INTRODUCTION ...................................................................................................................1
1.1. Authority........................................................................................................................1
1.2. Scope of the Study........................................................................................................1
1.3. Related Studies and Reports ........................................................................................2
2. EXISTING CONDITIONS ......................................................................................................4
2.1. Existing Infrastructure....................................................................................................4
2.2. Physical Environment....................................................................................................4
2.2.1. Climate ..................................................................................................................4
2.2.2. Hydrology ..............................................................................................................4
2.2.3. Geology.................................................................................................................6
2.2.4. Soils.......................................................................................................................6
2.2.5. Surface Water .......................................................................................................7
2.2.6. Floodplains............................................................................................................7
2.2.7. Water Quality.........................................................................................................8
2.2.8. Wetlands ...............................................................................................................9
2.2.9. Air Quality..............................................................................................................9
2.2.10. Noise ...................................................................................................................10
2.2.11. Hazardous, Toxic and Radioactive Waste (HTRW) ............................................10
2.3. Biological Resources...................................................................................................11
2.3.1. Vegetation ...........................................................................................................11
2.3.2. Aquatic Resources ..............................................................................................11
2.3.3. Wildlife.................................................................................................................12
2.3.4. Federal and State Threatened and Endangered Species...................................13
2.4. Recreational Resources..............................................................................................14
2.5. Socio-Economic Conditions ........................................................................................14
2.6. Incorporating the Needs and Considerations of All At-Risk Communities ..................15
2.7. Cultural Resources......................................................................................................16
3. FUTURE WITHOUT PROJECT CONDITIONS...................................................................18
3.1. Physical Environmental...............................................................................................18
3.2. Economic Conditions...................................................................................................18
3.2.1. Planned Development.........................................................................................20
3.3. Biological Environment................................................................................................20
3.4. Cultural Resources......................................................................................................20
i
3.5. HTRW..........................................................................................................................21
3.6. Summary of Future Without Project Conditions..........................................................21
4. PLANNING CRITERIA/ PURPOSE AND NEED FOR THE PROPOSED aCTION ............22
4.1. Problem Statements....................................................................................................22
4.2. Federal Objective........................................................................................................22
4.3. Study Objectives .........................................................................................................22
4.4. Opportunities...............................................................................................................22
4.5. Constraints..................................................................................................................22
4.5.1. Universal Constraints ..........................................................................................22
4.5.2. Specific Study Constraints ..................................................................................22
4.6. Planning Criteria..........................................................................................................23
4.6.1. Acceptability ........................................................................................................23
4.6.2. Completeness .....................................................................................................23
4.6.3. Effectiveness.......................................................................................................23
4.6.4. Efficiency.............................................................................................................23
4.6.5. Study Specific Evaluation Criteria .......................................................................23
5. FORMULATION AND EVALUATION OF ALTERNATIVES ................................................24
5.1. Plan Formulation Rationale.........................................................................................24
5.2. Management Measures...............................................................................................24
5.2.1. Development of Alternatives ...............................................................................26
5.3. Preliminary Array of Alternatives and First Screening.................................................27
5.4. Alternatives Carried Forward.......................................................................................28
5.4.1. Alternative 1: No Action.......................................................................................28
5.4.2. Alternative 2: Detention Basin Alone...................................................................28
5.4.3. Alternative 3: Detention Basin and channel improvements.................................28
5.4.4. Alternative 4: Detention Basin and nonstructural measure .................................28
5.4.5. Alternative 5: Detention Basin and Bridge Culvert Modifications ........................28
5.4.6. Alternative 6: Bridge Culvert Modifications alone................................................28
5.4.7. Alternative 7: Bridge culvert modification and a nonstructural measure..............29
5.4.8. Alternative 8: Channel Improvements and Bridge culvert modifications .............29
5.4.9. Alternative 9: Roadway improvements and a nonstructural measure.................29
5.4.10. Alternative 11: Buyouts alone..............................................................................29
5.4.11. Alternative 13: Raising structures in place alone.................................................29
5.4.12. Additional Alternatives.........................................................................................29
5.5. Second Screening of Alternatives...............................................................................29
ii
5.6. Final Array of Alternatives ...........................................................................................31
6. EVALUATION AND COMPARISON OF FINAL ARRAY .....................................................32
6.1. Detailed Alternative Descriptions ................................................................................32
6.1.1. Alternative 1: No Action.......................................................................................32
6.1.2. Alternative 2: Detention Basin Alone...................................................................32
6.1.3. Alternative 3: (3A1) Detention (2C1) + channelization at Windsor Drive.............35
6.1.4. Alternative 5: (5A1) Detention (2C1) and bridge improvements at Sherman Drive
36
6.1.5. Alternative 8: (8A1) Channelization and bridge improvement at Windsor Drive..39
6.1.6. Alternative 11: Buyouts Alone .............................................................................39
6.1.7. Alternative 13: Raising Structures in Place .........................................................40
6.1.8. Alternative 17: (17A1) Detention (2C1)+bridge
improvements(8A1)+channelization(8A1)............................................................................40
6.2. Costs of Final Array of Alternatives.............................................................................41
6.3. Economic Analysis of Final Array of Alternatives........................................................42
6.4. National Criteria...........................................................................................................43
6.5. Comprehensive Benefits Analysis...............................................................................45
7. TENTATIVELY sELECTED pLAN .......................................................................................46
8. CONCLUSION.....................................................................................................................46
9. RECOMMENDATIONS .......................................................................................................47
10. REFERENCES................................................................................................................48
11. ACRONYMS ...................................................................................................................50
Appendices
A. Cost Engineering
B. Environmental
C. Economics
D. Hydraulics and Hydrology
E. Civil Engineering
F. Geotechnical
G. Real Estate
H. Hazardous, Toxic, Radioactive Waste
iii
FIGURES
Figure 1 - Cooper Creek Study Area ............................................................................................1
Figure 2 - Cooper Creek Project Area (red outline) ......................................................................2
Figure 3 - Cooper Creek Watershed.............................................................................................5
Figure 4 - Cooper Creed Soils Map 2024 .....................................................................................7
Figure 5 - FEMA Flood Insurance Map for Cooper Creek Project Area........................................8
Figure 6 - Cooper Creek Wetland Map.........................................................................................9
Figure 7 - Climate and Economic Justice Screening Tool Results for the Cooper Creek Project
Area ............................................................................................................................................16
Figure 8 - Flood Inundation at the 0.10 Annual Exceedance Probability Event (10-year
FrequencyEvent)........................................................................................................................19
Figure 9 - Flood Inundation at the 0.002 Annual Exceedance Probability Event (500-year
FrequencyInterval).....................................................................................................................20
Figure 10 - Location of alternative 2A1 .......................................................................................33
Figure 11 - Location of alternative 2C1 .......................................................................................34
Figure 12 - Location of alternative 21D1 .......................................................................................35
Figure 13 - Location of alternative 3A1 .......................................................................................36
Figure 14 - Location of alternative 5A1 .......................................................................................37
Figure 15 - Layout of proposed bridge improvements for alternative 5A1 ..................................38
Figure 16 - Location of alternative 8A1 .......................................................................................39
Figure 17 - Cooper Creek Impact Area Associated with Alternative 11 and Alternative 13........40
Figure 18 - Location of alternative 17A1 .....................................................................................41
iv
TABLES
Table 1 - Aquatic Species Potentially Occurring in the Cooper Creek Project Area...................11
Table 2 - Common Wildlife Species in the Vicinity of the Cooper Creek Project Area................12
Table 3 - Federal Listed Species Identified on the IPaC for Cooper Creek................................13
Table 4 - Population Data for Denton, Texas..............................................................................15
Table 5 - Single Event Flood Depths and Damages for Structures with Modeled Damages
(Monetary Values in $Millions)....................................................................................................18
Table 6 - Cooper Creek Measures Considered ..........................................................................25
Table 7 - Cooper Creek Preliminary Array of Alternatives..........................................................27
Table 8 - Cooper Creek Initial Array of Alternatives with Screening...........................................30
Table 9 - Cooper Creek Alternative Costs (FY25 dollars)...........................................................41
Table 10 - Cooper Creek Economic Analysis (FY25 dollars)......................................................42
Table 11 - Cooper Creek National Criteria Evaluation................................................................44
Table 12 - Cooper Creek Comprehensive Benefits Summary....................................................45
v
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vi
1 . INTRODUCTION
1.1. Authority
The feasibility study is being conducted under authority granted by Section 205 of the Flood
Control Act of 1948 (Public Law 80-858), as amended, as administered under the U.S Army
Corps of Engineers Continuing Authorities Program (CAP).
1.2. Scope of the Study
The study examines the feasibility and environmental effects of implementing flood risk
management measures along Cooper Creek in Denton, Texas. The City of Denton is located in
central Denton County, which is in the northcentral portion of the state. Latitude: 33°13'45" N by
Longitude: 97007'25" W. The study area is shown in Figure 1 with the project area shown below
in Figure 2. The non-Federal partner for the feasibility study is the City of Denton. Denton,
Texas is located in Texas Congressional District 13 which is represented by Congressman
Ronny Jackson and Senators John Cornyn and Ted Cruz.
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Figure 2 - Cooper Creek Project Area (red outline)
This report documents the studies and coordination conducted to determine whether the
Federal Government should participate in flood risk management measures along Cooper
Creek at Denton, Texas. The study of potential flood risk management measures considered a
wide range of alternatives and the environmental consequences of those alternatives, but
focused mainly on actions that would provide efficient and effective management of flood risk to
the surrounding community. Although flood risk management is a high priority mission for the
United States Army Corps of Engineers (USACE), flood risks due to high flows along Cooper
Creek do not generate sufficient benefits to allow USACE to recommend a project to Congress.
USACE can only recommend to Congress flood risk management measures cost-shared by
non-Federal partners. The City of Denton has provided a letter of intent dated 29 June 2023
which includes the non-Federal sponsor (NFS) intention to cost share in Federally constructed
flood risk management measures along Cooper Creek. The partnership of Federal and non-
Federal interests in flood risk management measures helps ensure that those measures will
effectively serve both local and national needs.
1.3. Related Studies and Reports
February 1982. United States Army Corps of Engineers. Detailed Project Report Cooper Creek
Denton, Texas. Previous study on Cooper Creek terminated due to lack of benefits.
December 2003. DEH Consulting. Preliminary Analysis of City of Denton Drainage Capital
Improvement Plan. Analysis developing preliminary plan for the City of Denton Drainage Capital
Improvement Plan and prioritizing the projects according to the need and benefit of the public.
July 2009. Jacobs Engineering. Cooper Creek Flood Mitigation Preliminary Engineering Final
Report. Discussed flood mitigation options and costs along Cooper Creek.
2
December 2009. Freese Nichols. Cooper Creek and Pecan Creek Tributary PEC-4 Regional
Drainage Studies. Study to determine an effective approach to managing the 100-year
floodplain within Cooper Creek and Pecan Creek watersheds.
August 2012. Olsson Associates. Drainage Report Replacement Bridge 716.40 Choctaw
Subdivision Cooper Creek, Denton, Texas. Report to support application for a City of Denton
Floodplain Development Permit for the replacement of an aging timber railroad bridge with a
modern concrete bridge by the Union Pacific Railroad.
Mar 2020. KCE Engineering. Mockingbird Multi-Family Flood Study Denton, Texas. Study to
determine the existing 100-year floodplain along a tributary to Cooper Creek adjacent to a
proposed multi-family development and determine is floodplain reclamation is required and
possible for the development.
April 2023. Pacheco Koch. Avondale Park Channel Stabilization Project-Design Alternatives
Feasibility Report City of Denton, Denton County, Texas. Analyzed, proposed, and designed
channel stabilization and erosion protection improvements along Cooper Creek in Avondale
Park. Three alternatives were conceptually designed.
3
2. EXISTING CONDITIONS
This chapter presents a description of the resources and baseline conditions that could be
affected from implementing the proposed alternative in compliance with National Environmental
Policy Act (NEPA), the Council on Environmental Quality (CEQ), and 32 Code of Federal
Regulations (CFR) 775 guidelines. The level of detail used in describing a resource is
commensurate with the anticipated level of potential environmental impact. The study area
occurs along Cooper Creek which flows through the City of Denton, Texas. Cooper Creek is
located in central Denton County, which is in the northcentral portion of the state (Figure 1).
Cooper Creek runs through a developed area of Denton, Texas. Recurrent flooding of Cooper
Creek induces damages to adjacent properties, increases risk to human health and safety, and
inundates roadways resulting in road closures, traffic delays and increased emergency
response times. At least one known fatality has been attributed to flood waters from Cooper
Creek. In addition, high flow events are contributing to erosion downstream of Avondale Park
with the channel encroaching on residential lots and fence lines.
2.1. Existing Infrastructure
The study area of Cooper Creek spans across the city of Denton, Texas, and includes multiple
crossings of interest, primarily within areas of heavy residential development. Beginning
downstream, Cooper Creek crosses Mingo Road. Mingo Road currently is overtopped during
flooding events, affecting emergency response and evacuation times, but does not create
backwater affects nor damage to any structures directly upstream from the crossing. The
Nottingham Drive crossing is just downstream of Avondale park; flooding seems to cause
minimal structural damages at this point, however, there is evidence of bank erosion
downstream of this location. At East Sherman Drive, a bend occurs directly at the crossing with
the low-lying area occurring just upstream and to the north of the crossing. Sanitary sewer lines
currently run parallel to the creek but may be relocated by the City prior to or concurrently with
this project. Overloading and surcharging of the local storm drain system is likely during flooding
events, with this location having the most properties experiencing flooding. The upstream limit of
the project area does not appear to include any structures that experience flooding and will
likely not fall within the scope of the study.
2.2. Physical Environment
2.2.1. Climate
The climate of the study area is humid subtropical with warm to hot summers and mild
winters. The average annual high temperature is about 76 degrees Fahrenheit, with an
average summer high of about 96 degrees for the months of June, July, and August, and
an average annual winter low temperature of 54 degrees. Periods of freezing
temperatures are infrequent and rainfall averages about 38 inches annually (U.S.
Climate, 2024). Severe weather occurs periodically in the form of severe thunderstorms,
tornadoes, flood-producing extreme precipitation events, and occasional winter ice
storm (Runkle et al, 2022).
2.2.2. Hydrology
Cooper Creek is located In the northern part of the City of Denton, Texas. The creek flows in a
southeasterly direction though the city and terminates at Lewisville Lake. The watershed of
Cooper Creek is about 6.1 miles long and conveys a drainage area of approximately 9.64
4
square miles. The creek is generally small but well defined, mostly unimproved channel with
several tributaries. The main channel has an average depth of 6 feet, a top width of 50 feet and
a slope of 25 feet per mile. The creek is normally dry with flow occurring during periods of heavy
rainfall. The Cooper Creek watershed is shown in Figure 3.
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Figure 3- Cooper Creek Watershed
Cooper Creek is generally a trapezoidal, unlined earthen channel. There are several culvert
crossings that have limited capacity and cause backwater conditions within the stream channel.
The 100-year floodplain generally extends beyond the stream banks and into the residential
yards. Existing detention ponds were constructed within Cooper Creek watershed to reduce
flood damages along the creek. There is some channel erosion along Cooper Creek due to high
velocities in the channel.
At present, most of the development within Cooper Creek watershed is residential (mostly
single-family), with a few schools and parks scattered within the watershed. While the
watershed is nearly fully developed, there are a few areas in the upstream reaches of Cooper
Creek and its tributaries that are presently undeveloped and future development of these areas
may worsen the backwater problems, causing additional flooding along Cooper Creek.
Commercial development is widely scattered throughout the lower end of the watershed and
has only minimal flood damage potential. Much of the vegetative cover is in its natural state
except where residential development has encroached upon the creek in the upper end of the
watershed.
5
2.2.3. Geology
The project area is in a region known as the Eastern Cross Timbers Ecoregion. The region
extends southward from the Red River through eastern Denton County and along the boundary
between Dallas and Tarrant counties. It then stretches through Johnson County to the Brazos
River and into Hill County (Butler, 2022). The region includes rolling hills, cuestas, and ridges.
Soils within the Cross Timbers are mostly sandy, loamy, and are underlain by sand, shale, clay,
sandstone, calcareous shale, and limestone. Today, livestock farming is the main land use, but
some cropland also occurs (Texas Parks and Wildlife Department (TPWD)-A 2024). The City of
Denton sits on top of the Grayson Marl rock formation. Grayson Marl, mostly marl, is light-
greenish-gray to medium-gray, weathers to grayish yellow. Thickness of Grayson Marl in Texas
is between 15 and 60 feet (United States Geological Service (USGS), 2024).
2.2.4. Soils
The Farmland Protection Policy Act (FPPA) (Public Law 97-98, Title XV, Subtitle I,
Section 1539-1549 requires federal actions to minimize unnecessary and irreversible
conversion of farmland to nonagricultural uses, specifically prime farmlands. The Act
defines prime farmlands as "...land that has the best combination of physical and
chemical characteristics for producing food, feed, fiber, forage, oilseed, and other
agricultural crops with minimum inputs of fuel, fertilizer, pesticides, and labor, and
without intolerable soil erosion..." The Natural Resources Conservation Service (NRCS)
is responsible for designating soils as prime farmland soils.
The project area consists of a variety of ground cover types with the majority consisting
of disturbed soils covered by urban development as the City of Denton has grown
around the banks of Cooper Creek. The proposed footprint of the project does not
include land or soil suitable for agricultural activities. Based on the Soil Survey of
Denton County, Texas (Soil Conservation Service, 1988), soils surrounding the project
area are classified in the Sanger and Wilson-Urban land complex soil series, which are
classified as a clay-loke and well-drained soils weathered from claystone with low
slopes (Figure 4). According to Soil Survey Geographic Database (SSURGO)
information acquired from the Natural Resources Conservation Service (NRCS 2024),
soils within the Sanger and Wilson-Urban series are not considered prime farmlands
(Soil Survey Staff, 2024).
6
'.► _ K - VI-
out
AW M
Soil Types
Sanger-Urban land complex,1-5%slope
J- Wilson-Urban land complex,0-2%slope _
r `
Dallas Cooper Creek Soils Map
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Figure 4- Cooper Creed Soils Map 2024
2.2.5. Surface Water
Cooper Creek lies in the Elm Fork Trinity Watershed (Hydrologic Unit Code (HUC) 12030103).
Streams in the watershed vary from slow, meandering streams flowing to smaller, riffle and pool
types in the smaller watersheds. Cooper Creek is a 6.3-mile-long tributary to the Trinity River
which eventually leads into Lewisville Lake.
The project area consists of a shallow stream about 10 feet wide. Flow through the site is
generally slow moving and perennial. Despite erosion occurring in the area, turbidity is low, and
the water clarity is good. The stream bed is composed of some clays and silts towards the
center of the channel, while red clays are found along the shoreline and at the East Sherman
Drive bridge.
2.2.6. Floodplains
The project area is classified as Zone AE Regulatory Floodway on the Federal Emergency
Management Flood Insurance Rate Map as part of the Denton County Unincorporated Areas
(48121 C0360G) (Figure 5). Immediately in the project area, floodplain characteristics are
restricted on either side by residential housing communities (Federal Emergency Management
Agency (FEMA) 2023).
7
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Figure 5 - FEMA Flood Insurance Map for Cooper Creek Project Area
2.2.7. Water Quality
Regional water quality is influenced by lithology, soil composition and land use activities. In
Denton County, rugged upland areas have been cleared for urban use. Community housing,
businesses, and recreation are important land uses. Cooper Creek is part of the Upper Elm Fork
Trinity Watershed. Water quality in the Trinity River Basin is generally good while average
stream gradients and dissolved oxygen levels are typically lower than waters in the lower basin,
whereas turbidity, total suspended solids, total organic carbon, total phosphorus and
biochemical oxygen demand values are typically higher (TWDB, 2024).
Section 303(d) of the Clean Water Act (CWA) requires states to identify waters where existing
pollution controls are not stringent enough to achieve state water quality standards and
establish a priority ranking of these waters. The Texas Commission on Environmental Quality is
responsible for assessing water quality monitoring data and developing 303(d) list every two
years in accordance with the CWA. The Texas Draft 2024 303(d) List represents the most
recent evaluation of water quality data. Cooper Creek is not listed as an impaired waterbody for
any appraised metrics. There are no waterbodies upstream of Cooper Creek that would
contribute to the understanding of its water quality (Texas Commission on Environmental
Quality (TCEQ), 2024).
8
2.2.8. Wetlands
Wetlands are often defined as areas where the frequent and prolonged presence of water at or
near the soil surface drives the natural system including the type of soils (i.e. hydric soils) that
form, the plants that grow and the fish and/or wildlife that use the habitat. The existing project
footprint (Figure 6) covers approximately 27.3 acres with 1.1 acres occurring within Freshwater
Forested/Shrub Wetland and 5 acres of that occurring in Riverine wetlands.
mco WeY = Z 3 Elementary 660ft
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o Denton
Cooper Creek Wetland Map
,\
NPlano
2024
Dallas i i,��n c ,.i., .v1I
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Figure 6 - Cooper Creek Wetland Map
2.2.9. Air Quality
The U.S. Environmental Protection Agency (EPA) has the primary responsibility for regulating
air quality nationwide. The Clean Air Act (42 United States Code (U.S.C.) 7401 et seq.), as
amended, requires the EPA to set National Ambient Air Quality Standards (NAAQS) for wide-
spread pollutants from numerous and diverse sources considered harmful to public health and
the environment. The Clean Air Act established two types of national air quality standards
classified as either"primary" or"secondary." Primary standards set limits to protect public
health, including the health of at-risk populations such as people with pre-existing heart or lung
diseases (such as asthma), children, and older adults. Secondary standards set limits to protect
public welfare, including protection against visibility impairment, damage to animals, crops,
vegetation, and buildings.
EPA has set NAAQS for six principal pollutants, which are called "criteria" pollutants. These
criteria pollutants include carbon monoxide (CO), nitrogen dioxide (NO2), ozone (03), particulate
matter less than 10 microns (PM,o), particulate matter less than 2.5 microns (PM2.5), sulfur
dioxide (S02) and lead (Pb). If the concentration of one or more criteria pollutant in a geographic
area is found to exceed the regulated "threshold" level for one or more of the NAAQS, the area
9
may be classified as a non-attainment area. Areas with concentrations of criteria pollutants that
are below the levels established by the NAAQS are considered either attainment or
unclassifiable areas.
The project area is located within Denton County, Texas and is part of an area designated as
non-attainment, meaning concentrations of criteria pollutants are above the levels established
by the NAAQS (EPA 2024). Due to the area's NAAQS non-attainment status, if the study were
to continue a General Conformity determination would be required.
2.2.10. Noise
Federal and local governments have established noise guidelines and regulations for the
purpose of protecting citizens from potential hearing damage and from various other adverse
physiological, psychological, and social effects associated with noise. The Federal Interagency
Committee on Urban Noise developed land-use compatibility guidelines for noise in terms of
day-night average sound level (DNL). It is recommended that no residential uses, such as
homes, multifamily dwellings, dormitories, hotels, and mobile home parks, be located where the
noise is expected to exceed a DNL of 65 decibels (dBA). For outdoor activities, the EPA
recommends DNL of 55 dBA as the sound level below which there is no reason to suspect that
the general population would be at risk from any of the effects of noise (EPA, 1974). Noise-
sensitive receptors are facilities or areas where excessive noise may disrupt normal activity,
cause annoyance, or loss of business. Land uses such as residential, religious, educational,
recreational, and medical facilities are more sensitive to increased noise levels than commercial
and industrial land uses.
Review of the project area show that it is in an urban area comprised of residential homes and
businesses. There would be temporary noise disturbance from construction associated with the
project.
2.2.11. Hazardous, Toxic and Radioactive Waste (HTRW)
In order to complete a feasibility level HTRW evaluation for the Cooper Creek CAP 205, a
records search was conducted following the rules and guidance of ER 1165-2-132: HTRW
Guidance for Civil Works Projects, and American Society for Testing and Materials (ASTM)
E1527-13: Standard Practice for Environmental Site Assessment: Phase 1 Environmental Site
Assessment Process. In the records review, files, maps and other documents that provide
environmental information about the project area are obtained and reviewed. To complete the
records review, USACE reviewed publicly available databases and sources, using the proposed
footprint of the project, along with an approximate 1-mile search distance for each of the
sources. The records search revealed several HTRW sites in the vicinity of the project area,
although none of these sites have the potential to affect the proposed project. See the future
without project, alternative analyses, and the HTRW appendix for more information about risks
from these sites.
Cooper Creek has several potential HTRW sites in relative proximity (one mile) to the proposed
project footprint, including 6 registered petroleum storage tanks, an oil and gas pipeline, as well
as 1 Resource Conservation and Recovery Act (RCRA) Corrective Action site and 4 Toxic
Release Inventory sites located adjacent within a mile of the target area. With populations
increasing worldwide, more development and thus an increase in HTRW instances, is expected
in future decades that could potentially have negative impacts on Cooper Creek. However, the
current identified sites within one mile of the proposed project have an extremely low potential to
impact the project as they are not located directly in the creek.
10
Although not classified as HTRW, pipelines and oil wells play an important role in the existing
HTRW conditions in and around Cooper Creek. The oil and natural gas pipelines that cross
Cooper Creek will need to be avoided. Refer to the HTRW Appendix for locations of known
pipelines in and around the project area. The project alternatives involving disruption of the
sediment may need to consider the locations of these oil and gas pipelines. The identified
potential HTRW sites are not in the creek itself which eliminates potential impacts.
2.3. Biological Resources
2.3.1. Vegetation
The study area is located within the Cross Timbers and Prairies ecoregion, which covers the
upper center portion of the state of Texas. Grassland species such as little bluestem,
Indiangrass and big bluestem are common. Texas mulberry, American elm and Osage orange
are more common here than they were to the east. In the west, live oak becomes more
important, replacing the post oak of the east. Decreasing moisture discourages clusters of trees,
and trees form isolated stands. Flameleaf sumac, redbud, Mexican plum and Eastern red cedar
become more prevalent. Wildlife is a mixture of eastern forest and prairie species.
2.3.2. Aquatic Resources
Cooper Creek has habitat conditions that can support many species of fish and invertebrates
(Table 1). Fish communities characteristically in the area include a sunfish and minnow-
dominated community along with darters and occasional catfishes and an assemblage of
macroinvertebrates. No protected or sensitive species are known to occur in the creek.
Table 1 -Aquatic Species Potentially Occurring in the Cooper Creek Project Area
Common Name IF- Scientific NarTre
Microcaddisfly Paucicalcaria ozarkensis
Nearctic Paduniellan Caddisfly Paduniella nearctica
Mayfly Paraleptophlebia calcarica
Elevated Spring Amphipod Stygobromus elatus
Boston Mountains Crayfish Cambarus causeyi
Alabama Shad Alosa alabamae
White perch Pomoxis annularis
Pyramid Pigtoe Pleurobema rubrum
Purple Lilliput Toxolasma lividum
Isopod Lirceus bicuspidatus
Queen Snake Regina septemvittata
11
Common Name Scientific Name—
Alligator Gar Atractosteus spatula
American Eel Anguilla rostrata
2.3.3. Wildlife
Considerable urban growth and expansion throughout the area surrounding Cooper Creek has
caused local wildlife to become fragmented. Cooper Creek serves as a green corridor that
provides ample habitat for several common species of birds and mammals. Table 2 provides a
partial list of common bird and mammal species known to occur in areas near the project area
that may use the project area for foraging, nesting, resting, or migration.
Table 2 - Common Wildlife Species in the Vicinity of the Cooper Creek Project Area
Ir Common Name IL r Scientific Name Common Name Scientific Name
Birds
Black vulture Coragyps atratus Ring-neck duck Aythya collaris
Blue jay Cyanocitta cristata Wood duck Aix sponsa
Cardinal Cardinalis Mockingbird Mimus polyglottos
Common Geothlypis trichas Mourning dove Zenaida macroura
yellowthroat
Eastern phoebe Sayornis phoebe Robin Turdus migratorius
Eastern wood- Contopus virens Turkey vulture Cathartes aura
pewee
Great horned owl Bubo virginianus Red-tailed hawk Buteo jamaicensis
Mammals
Little brown bat Myotis lucifugus Opossum Didelphis virginiana
Eastern gray Sciurus Raccoon Procyon lotor
squirrel carolinensis
White-tailed deer Odocoileus Nine-banded Dasypus
virginianus armadillo novemcinctus
Eastern cottontail Sylvilagus Eastern chipmunk Tamias striatus
floridanus
Woodchuck Marmota monax Beaver Castor canadensis
12
6 Common Name Scientific Name Common Name Scientific Name
Striped skunk Mephitis Bobcat Felis rufus
2.3.4. Federal and State Threatened and Endangered Species
The United States Fish and Wildlife Service (USFWS) Information for Planning and Consultation
(IPaC) tool was utilized to determine species listed under the Endangered Species Act that may
occur in or near the Cooper Creek study area (USFWS, 2024). A total of five Federally
threatened or endangered species were identified; however, the project area only contains
suitable habitat for one species (Table 3). No Federally designated critical habitat for any of the
listed species is present in the action area. The bald eagle has been delisted but the protections
provided by the Bald and Golden Eagle Protection Act and the Migratory Bird Treaty Act remain
in effect.
Table 3 - Federal Listed Species Identified on the IPaC for Cooper Creek
HabitatSuitable Habitat in the
Species Name Status
Mammals
Summer habitat: wide variety of
forested/wooded habitats for
roosting. Roost among leaves of
live or recently dead deciduous Summer Habitat: Yes
Tricolored Bat hardwood trees, but may also be
PE
Perimyotis subflavus found in Spanish moss, pine
trees, and occasionally Winter Habitat: No
manmade structures.
Winter habitat (hibernacula):
caves or abandoned mines.
Birds
Dense marshes and wetlands
with nest sites found primarily
located in shallow diatom ponds No -Urban area with
Whooping crane E that contain bulrush. During sparse forested riparian
Grus americana migration, whooping cranes use area lacking
a variety of habitats; however, wetlands/marshes
wetland mosaics appear to be
the most suitable.
No- Open areas around
Piping plover T Coastal shorelines and open the creek are grassy and
Charadrius melodus mudflats and sandy areas. disturbed. Lack sandy
areas.
13
HabitatSpecies Name Status Description
Action Area
Wintering and migration habitats
are muddy or sandy coastal No - shorelines are
Rufa red knot areas, specifically, bays and urbanized and surrounded
T estuaries, tidal flats, and
Calidris canutus rufa unimproved tidal inlets with sand by patches of Riparian
spits, islets, shoals, and Forest
sandbars
E= Endangered T= Threatened PE= Proposed Endangered PT= Proposed
Threatened C= Candidate
Source: U.S. Fish and Wildlife Service IPAC website and Arkansas Ecological Service Office
database
2.4. Recreational Resources
Occasional fishing, hiking or wildlife watching may occur immediately along the creek; however,
the creek is bordered on all sides by private land making other recreational activities unavailable
due to restricted land access.
2.5. Socio-Economic Conditions
Socioeconomics is defined as the basic attributes and resources associated with the human
environment, particularly population, demographics, and economic development. Demographics
entail population characteristics and include data pertaining to race, gender, income, housing,
poverty status, and educational attainment. Economic development or activity typically includes
employment, wages, business patterns, an area's industrial base, and its economic growth.
The socio-economic characteristics of Denton, Texas, the nearest town located near the project
study area are presented in Table 4. The City of Denton had a population of 158,349 living in
52,000 households in 2022. The racial makeup of the city was 67.8 percent White, 11.5 percent
African American, 0.8 percent Native American, 3.5 percent Asian, 0.0 percent other, and 11.1
percent from two or more races. Of the total population, 24.1 percent were of Hispanic or Latino
origin. Roughly 15.7 percent of families in the city live below the poverty line (U.S. Census
Bureau, 2022).
14
Table 4- Population Data for Denton, Texas
Population Denton, Texas Population 158,349
Total Households 52,000
White 67.8%
Black or African American 11.5%
Native American or Alaska Native 0.8%
Asian 3.5%
Native Hawaiian or Other Pacific Islander 0.0%
Other Race 0.0%
Two or More Races 11.1%
Hispanic 24.1%
Under 5 years 4.9%
5 to 19 years 18.5%
20 to 64 years 64.4%
Over 64 years 12.2%
High School Diploma 91.5%
Bachelor's Degree or Higher 40.0%
Median Household Income $71,717
2.6. Incorporating the Needs and Considerations of All At-Risk
Communities
An analysis using the Climate and Economic Justice Screening Tool (CEJST) was conducted to
identify at risk communities in or near the project area (Figure 7). The tool identifies at risk
communities if they are in a census tract that meets the thresholds for at least one of the tool's
categories of burden, or if they are on land within the boundaries of Federally Recognized
Tribes. The CEJST showed that a portion of the area surrounding the project area was
characterized as being at risk.
15
Tract information
denton.LK • -~ I �z� Number:48121020503
County:Denton County
State:Texas
Population:6,727
t
+ 4k Tract denunMhks
Race 1'Ethnicity (Show�)
Age (2hW-)
rdeatinad as disadvantatedt
48 - -
AK
This tract is considered
HI - disadvantaged because it meets 1
PR burden threshold AND the
associated socioeconomic
GLI threshold.
AS SOW I99dback O
MP
VI
Climate change +
Energy +
Health +
Housing +
Legacy pollution +
Figure 7 - Climate and Economic Justice Screening Tool Results for the Cooper Creek Project
Area
2.7. Cultural Resources
The study area is located on the southern plains in north Texas in the City of Denton along
Cooper Creek. The study area is heavily developed for residential and commercial use and the
banks and channel of Copper Creek have been modified to control erosion. There are
numerous cultural resources recorded within the region that include the National Register of
Historic Places (NRHP) listed properties, archeological sites, cemeteries, and historical
markers. A preliminary assessment of the cultural resources within one kilometer of the
proposed study area was conducted using a desktop review of the databases maintained by the
Texas Historical Commission and the Texas Archeological Research Laboratory for cultural
resources as well as a review of historic aerial imagery. The assessment identified one
previously recorded cultural resource, the Fairhaven Retirement Home, a NRHP listed property,
approximately 950 meters from the proposed study area. There are no other previously
recorded cultural resources.
Only two previous archeological surveys are within one kilometer of the study area. Both
surveys were conducted in 1993 for the Federal Highway Administration along United States
(U.S.) Highway 77 and North Locust Street. While there have been numerous cultural resource
investigations conducted in the surrounding region, there are no other previous investigations in
the proposed study area or within one kilometer.
The primary considerations concerning cultural resources are threats to buried archeological
deposits because of earthmoving activities. However, most of the study area has been
16
developed for residential and commercial use. The soils within the study area are mapped as
Sanger-Urban land complex and Wilson-Urban land complex, both clayey soils originating from
alluvium from weathered slopes and bedrock. Although the area has not been previously
investigated, the residential and commercial development and the presence of urban soils in the
study area suggest that the probability for intact archeological sites to occur in the area is low.
17
3. FUTURE WITHOUT PROJECT CONDITIONS
3.1. Physical Environmental
The watershed is nearly fully developed, however, there are a few areas in the upstream
reaches of Cooper Creek and its tributaries that are presently undeveloped. Commercial
development is widely scattered throughout the lower end of the watershed and has only
minimal flood damage potential. Future development of these areas may worsen the backwater
problems, causing additional flooding along Cooper Creek. Temperature, drought, and rainfall
intensity in the study area are projected to increase in the future, while streamflow trends are
projected to decrease (USACE 2015).
3.2. Economic Conditions
To illustrate the extent of flooding, Table 5 displays single event damages (unweighted by
probability) for the suite of flood events included in an FDA analysis. At higher frequency events,
depths relative to first floor structure elevations and estimated damages are limited, while at
lower frequencies, they are higher and at the extreme (0.002 Annual Exceedance Probability
(AEP)) structure and content damages total $7.8 million. Total Expected Annual Damage (EAD)
across the range of modeled flood events is roughly $907,000.
Table 5- Single Event Flood Depths and Damages for Structures with Modeled Damages
(Monetary Values in $Millions)
ProbabilityAEP AEP AEP AEP . AEP AEP
Depth Relative to First Floor Elevations
Mean 1 0.80 0.40 0.20 1 0.06 0.24 1 0.41 0.52 0.64
Standard Deviation 0.00 0.64 0.68 0.69 0.72 0.73 0.79 0.86
Maximum 0.16 1.06 1.48 1.98 2.54 3.07 3.57 4.23
Minimum 1.82 1.93 1.92 1.82 1.89 1.51 1.46 1.95
Single Event Damages $millions
Structures $0.20 $0.85 $1.50 $2.31 $2.86 $3.46 $4.01 $4.90
Content and vehicles $0.15 $0.56 $0.95 $1.43 $1.73 $2.06 $2.36 $2.88
Total $0.34 $1.42 $2.45 $3.75 $4.59 $5.53 $6.37 $7.78
18
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Event)
19
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Figure 9 - Flood Inundation at the 0.002 Annual Exceedance Probability Event(500-year Frequency
Interval)
3.2.1. Planned Development
The project area is mostly fully developed along Cooper Creek. There are minimal development
opportunities within the project area that are not currently designated as Regulatory Floodway
by FEMA. Along Stuart Road, there are openings for possible minor residential development; it
can be reasonably assumed that this would not significantly affect flooding currently highlighted
along Cooper Creek. The same can be assumed for the expansion of impermeable surfaces
that would come with the expansion of Avondale park and commercial development just
downstream of Mingo Road.
3.3. Biological Environment
Under the No Action Alternative, Biological Resources are expected to remain the same as
described in the Existing Conditions Section of this report.
3.4. Cultural Resources
There are no previously recorded cultural resources located within the proposed project area
and the formation processes that currently affect these sites will continue into a future without
the project. Undiscovered cultural resources could be at risk of displacement or degradation
from flood events and future development in the region. These formation processes may result
in partial or total loss of historic properties.
20
3.5. HTRW
No Recognized Environmental Conditions were identified within one mile of the project area that
could be reasonably expected to affect the Cooper Creek CAP 205 project. Although not
classified as HTRW under USACE regulations, several oil and gas infrastructure sites were
identified within the surrounding area. As a result of these findings, pipelines and wells within
the project vicinity and along potential site access routes should be precisely located during
PED to ensure no unintended interaction occurs with the existing oil and gas facilities.
Despite the lack of identified sites that could be reasonably expected to affect the project, there
is always a possibility that previously unidentified HTRW could be uncovered, even when a
proposed project is entirely within a preexisting project footprint. An updated HTRW survey will
be required should the project be reconsidered and funded at a future time. Additionally, care
should be taken to identify and address HTRW concerns that may arise in a timely manner, so
as not to affect proposed project timelines.
3.6. Summary of Future Without Project Conditions
If No Action is taken to address flooding along Cooper Creek, the most likely future condition of
the area is as follows:
• Recurrent flooding of Cooper Creek will continue to cause damages to adjacent
properties.
• Increased risk to human health and safety as a result of inundated roadways,
road closures, traffic delays, and increased emergency vehicle response
times.
• If no action is taken at Cooper Creek, the streambank will continue to erode downstream
of Avondale Park and cause encroachments on residential lots and fence lines.
21
4. PLANNING CRITERIA / PURPOSE AND NEED FOR THE
PROPOSED ACTION
4.1. Problem Statements
• Recurrent flooding of Cooper Creek induces damages to adjacent properties
• Recurrent flooding of Cooper Creek presents risks to human health and safety
4.2. Federal Objective
The Federal objective of water and related land resources project planning is to contribute to
national economic development consistent with protecting the nation's environment pursuant to
national environmental statutes, applicable EOs, and other Federal planning requirements.
4.3. Study Objectives
• Reduce risk of flood induced damages in the vicinity of Cooper Creek over the 50-year
period of analysis.
• Reduce risk to human health and safety in the vicinity of Cooper Creek over the 50-year
period of analysis.
4.4. Opportunities
• An opportunity exists to reduce bank erosion induced by high flows in Cooper Creek,
especially Avondale Park and downstream of Avondale Park.
• An opportunity exists to combine new recreation features with a flood risk management
plan
• An opportunity exists to provide the public educational information about their flood risk
• An opportunity exists to evaluate existing habitat and possibly use engineering with
nature (bioengineering)
• An opportunity exists to improve water quality (sediment and bacteria)
• An opportunity exists to improve emergency response time in the vicinity of Cooper
Creek over the 50-year period of analysis
4.5. Constraints
4.5.1. Universal Constraints
• Avoid or mitigate for historic and cultural resources (impacts now are mainly from
erosion)
• Avoid or mitigate for environmental resources and impacts
4.5.2. Specific Study Constraints
• Lands on either side of Cooper Creek and its tributaries is almost completely developed.
• Utilities run parallel to Cooper Creek
22
• NFS existing and future projects to Cooper Creek may affect plan formulation and
economic analysis during feasibility
• City requires that improvements have no negative impacts on other properties
4.6. Planning Criteria
Federal Principles and Guidelines establish four criteria for evaluation of water resources
projects. Those criteria and their definitions are listed below.
4.6.1. Acceptability
Acceptability is defined as "the viability and appropriateness of an alternative from the
perspective of the Nation's general public and consistency with existing Federal laws,
authorities, and public policies. It does not include local or regional preferences for particular
solutions or political expediency."
4.6.2. Completeness
Completeness is defined as "the extent to which an alternative provides and accounts for all
features, investments, and/or other actions necessary to realize the planned effects, including
any necessary actions by others. It does not necessarily mean that alternative actions need to
be large in scope or scale."
4.6.3. Effectiveness
Effectiveness is defined as "the extent to which an alternative alleviates the specified problems
and achieves the specified opportunities."
4.6.4. Efficiency
Efficiency is defined as "the extent to which an alternative alleviates the specified problems and
realizes the specified opportunities at the least cost."
4.6.5. Study Specific Evaluation Criteria
A project that effectively serves both Federal and non-Federal interests must be sited, planned,
and operated so that it safely and efficiently meets user needs. To this end, the project delivery
team PDT economic analysis incorporated the criterion of flood damages prevented to analyze
alternatives in conjunction with the National Criteria.
23
5. FORMULATION AND EVALUATION OF ALTERNATIVES
5.1. Plan Formulation Rationale
Plan formulation is the process of building alternative plans that meet planning objectives and
avoid planning constraints. Alternatives are a set of one or more management measures
functioning together to address one or more planning objectives. A management measure is a
feature or activity that can be implemented at a specific geographic location to address one or
more planning objectives. A feature is a "structural" element that requires construction or
assembly on-site whereas an activity is defined as a "nonstructural" action. Each alternative
plan shall be formulated in consideration of criteria stated in Section 4.6.
5.2. Management Measures
A list of management measures is listed below. The PDT conducted a screening process based
on listed criteria with results shown in Table 6.
• Detention basin — Excavated area adjacent to or within Cooper Creek to reduce flood
risk and lower the peak discharge by detaining the stormwater runoff for a specific short
period of time
• Channel improvements— Straightening the channel or increasing channel capacity by
excavating the channel to be deeper and/or wider
• Buyouts- Provide owners an opportunity to sell structures in flood-prone areas for fair
market value
• Wet floodproofing- Implementation of modifications that allow protection from hydrostatic
pressure damage during flooding (thus reducing probability of structural failure), but
allows flood waters into (and out of) the structure
• Raising structures in place-A nonstructural measure that would elevate existing
structures to reduce risk of flood damages
• Crossing improvements (including bridge culvert modifications)— Raise the roadway
profile and/or increase the hydraulic capacity of the roadway crossing and lower the
water surface elevation by adding or modifying the box culvert/ bridge at Sherman Drive,
Mingo Road, and/or Blagg Road
• Modify outlet control structures at existing detention basin- An outlet at the detention
basin that controls the volume of water/time unit flowing downstream
• Energy Dissipators- Within detention basin or channel-Devices that protect downstream
areas by reducing the velocity, energy, and turbulence of the flow within the channel
• Weirs in existing detention basins-A hydraulic structure is used for regulating the flow of
water to prevent flooding, stabilize water levels, and improve the quality of aquatic life in
the water
• Realign channel a- Straighten channel to allow more water to flow at a faster velocity
• Realign channel b- Create meanders to decrease the velocity of the water in the channel
• Dry floodproofing- Structural or non-structural modifications or additions which prevent
flood waters from entering or encroaching on structures
24
• Warning system- Real-time monitoring and automatic alerts based on water level and
flow/volume at Cooper Creek
• Rezoning and repurpose areas in vicinity of Cooper Creek- Rezone or repurpose
through local ordinances to prevent development of flood-prone areas in the vicinity of
Cooper Creek
• Levee or floodwall- Natural or artificial wall used to prevent overflow of channel and
reduce flood risk from flooding events
• Tunnel- An underground floodway that is used to divert excess floodwater from the
surface
• Bypass channel-A secondary channel to carry flow around problem areas in the main
channel
• Diversion channel-A secondary channel to reduce flow in and carry flow away from the
main channel
• Cistern- A large rainwater storage tank used to help reduce storm water runoff and can
be used for additional purposes.
• Stormwater system improvements-Actions to improve the flow of water through the
city's stormwater system
• Imperviousness reduction- Actions to improve surface to retain more water during high
flow events
Table 6- Cooper Creek Measures Considered
Measure Evaluation
Structural
Detention Basin* Carried Forward
Channel Improvements* Carried Forward
Crossing Improvements (including
bridge/culvert modifications)* Carried Forward
Modify Outlet Structure at Existing Detention Ineffective existing outlet structures already
Basins close to ground level, levees or floodwalls
would be needed
Energy Dissipaters* It will likely not reduce water surface
elevations
Weirs in Existing Detention Basins Expensive to implement and likely would not
significantly reduce flood risk
Realign Channel A- Straighten Channel Likely to be ineffective as the channel is
already fairly straight
25
Measure Evaluation
Realign Channel B - Create Meander*s Constrained by development on both sides of
the channel
Constraint by development on both sides of
Levee or Floodwall the channel and there would not be enough
room to construct
Flood damages would not support positive
Tunnel net benefits due to the high cost of
implementing a tunnel
Bypass Channel Limited space and cost prohibitive
Diversion Channel Limited space and cost prohibitive
Cistern Higher cost than detention area with similar
benefits
Stormwater System Improvements Not within USACE authority
Impervious Reduction Not within USACE authority
Non-Structural
Buyouts Carried Forward
Wet Floodproofing Carried Forward
Raising Structures in Place Carried Forward
Dry Floodproofing Not recommended by the National Non-
structural Committee
Would not address the objectives and due to
Warning System proximity of structures to Creek and flashy
nature of flooding, would not allow ample
time to evacuate
Rezoning and Repurposing Areas in the Not be practical as land to either side of
Vicinity of Cooper Creek Cooper Creek is already developed or utilized
for recreation or other purposes
*Includes natural and nature-based (NNB) features
5.2.1. Development of Alternatives
The PDT held a rapid iteration on 9 May 2024 and incorporated the results of this iteration into a
planning charrette with the non-Federal sponsor (NFS) on 11 June 2024. During these
meetings, the team developed the problems, opportunities, objectives and constraints and held
26
brainstorming sessions to identify measures which were then screened and combined into
preliminary array of fifteen alternatives. Subsequent planning iterations identified three
additional alternatives to create the initial array of alternatives. During the subsequent iterations
the initial array (to include the additional alternatives) were screened to a final array of eight
alternatives.
5.3. Preliminary Array of Alternatives and First Screening
During the planning charrette the preliminary alternatives (Table 7) were identified and
evaluated by the PDT.
Table 7 - Cooper Creek Preliminary Array of Alternatives
Alternative Evaluation
Alternative 1 — No Action Carried Forward
Alternative 2 — Detention Basin alone Carried Forward
Alternative 3 — Detention Basin and channel Carried Forward
improvements
Alternative 4— Detention Basin and
nonstructural measure Carried Forward
Alternative 5— Detention Basin and Bridge
Culvert Modifications Carried Forward
Alternative 6 — Bridge Culvert Modifications Carried Forward
alone
Alternative 7— Bridge culvert modification Carried Forward
and a nonstructural measure
Alternative 8— Channel Improvements and
Bridge culvert modifications Carried Forward
Alternative 9— Roadway improvements and a Carried Forward
nonstructural measure
Incomplete solution, would require either
Alternative 10 — Channel Improvements modifications to the bridge culvert or
alone elevating the roadway or the appropriate
location of a detention basin
Alternative 11 — Buyouts alone Carried Forward
Alternative 12 —Wet floodproofing alone Structures in the area are slab on grade with
no basements,
27
Alternative Evaluation
Alternative 13 — Raising structures in place
Carried Forward
alone
Alternative 14 — Roadway improvements Incomplete Solution and outside USACE
alone authority
Incomplete solution, would require either
Alternative 15— Channel Improvements and modifications to the bridge culvert or
nonstructural measure elevating the roadway or the appropriate
location of a detention basin
* Alternatives 2,3,4, 5, and 8 include NNB features in the form of native plantings.
5.4. Alternatives Carried Forward
The initial evaluation and screening resulted in the following initial array of alternatives.
5.4.1. Alternative 1: No Action
The No Action plan is the plan without Federal action at the project site.
5.4.2. Alternative 2: Detention Basin Alone
Alternative 2 would consist of designing and constructing a detention basin in the vicinity of
Cooper Creek.
5.4.3. Alternative 3: Detention Basin and channel improvements
This alternative would include a detention basin in the vicinity of Cooper Creek and channel
improvements such as straightening the channel immediately adjacent to Sherman Drive and
deepening or widening the channel.
5.4.4. Alternative 4: Detention Basin and nonstructural measure
Alternative 4 combines a detention basin with at least one non-structural measure. Non-
structural measures considered for this project include wet floodproofing, raising structures in
place and buyouts.
5.4.5. Alternative 5: Detention Basin and Bridge Culvert Modifications
This alternative would consist of a detention basin as well as adding or modifying the box
culvert/ bridge at Sherman Drive, Mingo Road, and/or Blagg Road to increase hydraulic
capacity.
5.4.6. Alternative 6: Bridge Culvert Modifications alone
Alternative 6 includes adding or modifying the box culvert/ bridge at Sherman Drive, Mingo
Road, and/or Blagg Road to increase hydraulic capacity.
28
5.4.7. Alternative 7: Bridge culvert modification and a nonstructural measure
This alternative is comprised of adding or modifying the box culvert/ bridge at Sherman Drive,
Mingo Road, and/or Blagg Road to increase hydraulic capacity as well as at least one non-
structural measure. Non-structural measures considered for this project include wet
floodproofing, raising structures in place and buyouts.
5.4.8. Alternative 8: Channel Improvements and Bridge culvert modifications
Alternative 8 consists of channel improvements such as straightening the channel immediately
adjacent to Sherman Drive and deepening or widening the channel combined with adding or
modifying the box culvert/ bridge at Sherman Drive, Mingo Road, and/or Blagg Road to increase
hydraulic capacity.
5.4.9. Alternative 9: Roadway improvements and a nonstructural measure
This alternative includes raising the roadway profile of Sherman Drive, Mingo Road, and/or
Blagg Road at Cooper Creek as well as at least one non-structural measure. Non-structural
measures considered for this project include wet floodproofing, raising structures in place and
buyouts.
5.4.10. Alternative 11: Buyouts alone.
Alternative 11 would consist of determining the structures in the impact area prone to damages
with various AEP events and a complete purchase of properties at market value and demolish
costs of removing structures within the impact area.
5.4.11. Alternative 13: Raising structures in place alone.
This alternative would determine structures in the impact area which are prone to flood
damages with various AEP events and raise homes off foundation and place support columns
underneath to protect from flooding.
5.4.12. Additional Alternatives
During the third iteration of plan formulation, three (3) additional alternatives were identified and
included in the initial array of alternatives prior to screening to obtain the final array.
• Alternative 16: Bridge culvert modifications, channel improvements and a nonstructural
measure
• Alternative 17: Detention Basin, Bridge culvert modifications, channel improvements
• Alternative 18: Detention Basin, Bridge culvert modifications, channel improvements and
a nonstructural measure
5.5. Second Screening of Alternatives
Table 8 displays the second screening of alternatives, including the additional alternatives.
29
Table 8 - Cooper Creek Initial Array of Alternatives with Screening
Alternative Evaluation
Alternative 1 — No Action Carried Forward
Alternative 2 — Detention Basin alone Carried Forward for further evaluation
Alternative 3 — Detention Basin and channel
Carried Forward
improvements
Alternative 4 — Detention Basin and This combination would not produce
nonstructural measure significant additional benefits over the non-
structural alone.
Alternative 5— Detention Basin and Bridge
Culvert Modifications Carried Forward
Alternative 6 — Bridge Culvert Modifications If you increase capacity at crossing, it is still
alone limited to capacity in channel
Alternative 7— Bridge culvert modification Would effectively become non-structural
and a nonstructural measure alternative as bridge culver in effective.
Alternative 8 — Channel Improvements and
Bridge culvert modifications Carried Forward
Alternative 9 — Roadway improvements and a Likely would not fully within USACE authority.
nonstructural measure Would effectively become non-structural
alternative as bridge culver in effective
Alternative 11 — Buyouts alone Carried Forward
Alternative 13 — Raising structures in place Carried Forward
alone
Alternative 16 — Bridge culvert modifications, This combination would not produce
channel improvements and a nonstructural significant additional benefits over the non-
measure structural alone. .
Alternative 17 — Detention Basin, Bridge Carried Forward
culvert modifications, channel improvements
Alternative 18 — Detention Basin, Bridge This combination would not produce
culvert modifications, channel improvements significant additional benefits over the non-
and a nonstructural measure structural alone. .
* Alternatives 2,3,4, 5, 8, 16, 17 and 18 include NNB features in the form of native plantings.
30
5.6. Final Array of Alternatives
After screening the initial array, the final array identified by the PDT consists of seven
(7) alternatives:
• Alternative 1 — No Action
• Alternative 2 — Detention Basin alone
• Alternative 3 — Detention Basin and channel improvements
• Alternative 5— Detention Basin and Bridge Culvert Modifications
• Alternative 8 — Channel Improvements and Bridge culvert modifications
• Alternative 11 — Buyouts Alone
• Alternative 13— Raising Structures in Place Alone
• Alternative 17— Detention Basin, Bridge culvert modifications, channel improvements
31
6. EVALUATION AND COMPARISON OF FINAL ARRAY
6.1. Detailed Alternative Descriptions
6.1.1. Alternative 1: No Action
If No Action is taken to address flooding along Cooper Creek, the most likely future condition of
the area is as follows:
• Recurrent flooding of Cooper Creek will continue to cause damages to adjacent
properties.
• Increased risk to human health and safety as a result of inundated roadways, road
closures, traffic delays, and increased emergency vehicle response times.
• If no Federal action is taken at Cooper Creek, the streambank will continue to erode
downstream of Avondale Park and cause encroachments on residential lots and fence
lines.
6.1.2. Alternative 2: Detention Basin Alone
2A (2A1) Detention above Sherman Drive: This alternative seeks to utilize land already owned
by the City of Denton and minimize impacts on the environment. An area approximately 500
feet wide and 100 feet long would be excavated (4,800 cubic yards) from the park area
upstream of Sherman Drive. Figure 10 shows the location of alternative 2A1.
32
14
Figure 10 - Location of alternative 2A1
This alternative adds some floodwater storage capacity in the right overbank. 2A1 includes up to
6 feet of excavation in the right overbank. To minimize impacts on the environment, this
alternative would use native grass plantings.
2B (2C1) Detention above Stuart Road, elevation 637 feet): This alternative seeks to utilize a
large area of undeveloped land upstream of Stuart Road. This area is not owned by the City of
Denton and would result in more environmental impacts due to existing trees, however this area
has a significant amount of volume that could be used for floodwater storage. Figure 11 shows
the location of alternative 2C1.
33
Y 1
k- 5
VL
IL Ira
200ft
Figure 11 - Location of alternative 2C1
About 9 acres of land would be excavated to elevation 637 feet and result in an average
excavation depth of 7 feet (Total excavation volume is 106,000 cubic yards). The alternative
would include an earthen weir approximately 850 feet in length cut to an elevation of 640.5 feet
which would optimize the flood storage of the peak of flood hydrograph. The elevation could be
increased or decreased to focus flood shaving for different events, but the 25-year event was
the event that was selected as a compromise between frequent flood events like the 10-year
event and more infrequent flood events like the 100-year. The alternative also includes a pipe at
the downstream end to drain the detention area. This detention alternative meets study
objectives but also provides environmental benefits through creation of new fluvial floodplain
area (Nature Based Solution) and native grass plantings.
2C (2D1) Detention above Stuart Rd, elevation 634 feet: This alternative is similar to 2C1 but
has additional excavation depth, lower earthen weir elevation, and longer drainage pipe. This
alternative seeks to utilize a large area of undeveloped land upstream of Stuart Rd. This area is
not owned by the City of Denton and would result in more environmental impacts due to existing
trees, however this area has a significant amount of volume that could be used for floodwater
storage. Figure 12 shows the location of alternative 2D1.
34
� - 40 Ahi
��� • 1-�• }� i , . - .fir t
Hr t• • ,
bA
VL
� _ F ' r w
��..•ram� � `;� � _
Figure 12 - Location of alternative 2131
About 9 acres of land would be excavated to elevation 634 feet and results in an average
excavation depth of 10 feet (Total excavation volume is 151,000 cubic yards). The alternative
would include an earthen weir approximately 850 feet in length cut to an elevation of 639.8 feet
which would optimize the flood storage of the peak of flood hydrograph. The elevation could be
increased or decreased to focus flood shaving for different events, but the 25-year event was
the event that was selected as a compromise between frequent flood events like the 10-year
event and more infrequent flood events like the 100-year. The alternative also includes a pipe at
the downstream end to drain the detention area. This detention alternative meets study
objectives but also provides environmental benefits through creation of new fluvial floodplain
area (Nature Based Solution) and native grass plantings.
6.1.3. Alternative 3: (3A1) Detention (2C1) + channelization at Windsor Drive
This alternative includes the detention from alternative 2C1 and channelization around Windsor
Rd. The channelization extent for this alternative was identified as the "NED Plan" in a previous
USACE report titled "Cooper Creek, Denton Texas, Stage 2 Planning Draft Detailed Project
Report" which was from a 1981 USACE CAP Section 205 study on Cooper Creek. Figure 13
shows the location of alternative 3A1.
35
428
` JVPly
y r e I N
�� _� a `� e• � Ll r, ►i ��� y♦ '�'� `
•Al
}`•
'. e'er `fir �, •'•, 1 . , ,
Figure 13 - Location of alternative 3A1
In addition to the detention configuration described under alternative 2C1, channelization would
be performed around Windsor Drive. The channelization includes approximately 850 feet of
grass lined channel improvement with a bottom width of 30 feet and side slopes of 3 horizontal
to 1 vertical. The total excavation amount for this alternative is 110,400 cubic yards. This
detention alternative meets study objectives but also provides environmental benefits through
creation of new fluvial floodplain area (Nature Based Solution) and native grass plantings.
6.1.4. Alternative 5: (5A1) Detention (2C1) and bridge improvements at Sherman
Drive
This goal with this alternative is to reduce the water surface elevations through Cooper Creek by
adding flood storage with detention (Configuration from alternative 2C1) and increasing the
capacity through the Sherman drive bridge. The capacity increase is based on a configuration
analyzed and costed during a 2009 study performed for the City of Denton by an engineering
firm. Figure 14 shows the location of alternative 5A1.
36
J GI CI.ICV. LJl l.O;011 V11_I tlgl ♦. M� ram,^•',
Y It
�
NN IIff�TT1
I Pi
0 SO
41
NAM
per
lop
LL i
t1
-��• •"• + ,�^f•r'Z 1� . .�,;� � "� � `�'�'.�-,mil'
- __ 'i•�j .—� �crttr•.���... J��i7� .v.•,i+���+C5CC ft I I
Figure 14- Location of alternative 5A1
In addition to the detention configuration described under alternative 2C1, the Sherman Dr.
crossing capacity would be increased from a single 30-foot clear span to 2 —40 ft by 8 ft clear
spans with a single 2 ft wide pier and vertical abutments. This provides a significant increase in
flow area through the bridge (From 210 square feet to 640 square feet). Figure 15 provides an
illustration of how the existing crossing compares to the proposed crossing from 5A1.
37
t 101 Monterrey Drive
to
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m
I
I
I Reloca.e
12'water
,
Relocate
15'SS.
Relocate
15'S S
15 SS
Remove
48'Storm
6Ta �.•rsr
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r
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1404 Sherman Drive
2ti � t
Legend
Ezlsung Uttlaios Proposed UtaUtles
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Cooper Creek Flood Mitigation Study
-1 WITH DETENTION Sherman Drive
JACOBS
Figure 15- Layout of proposed bridge improvements for alternative 5A1
38
6.1.5. Alternative 8: (8A1) Channelization and bridge improvement at Windsor
Drive
The goal of this alternative is to reduce the water surface elevations through Cooper Creek by
increasing the Cooper Creek channel capacity and crossing capacity at Windsor Dr. The
channelization extent for this alternative was identified as the "National Economic Development
(NED) Plan" in a previous USACE report titled "Cooper Creek, Denton Texas, Stage 2 Planning
Draft Detailed Project Report" which was from a 1981 USACE CAP Section 205 study on
Cooper Creek. Figure 16 shows the location of alternative 8A1.
Owl
.40
i
Y
r ♦♦ � 1
1 :, u• C 500ft I I
Figure 16 - Location of alternative 8A1
Channelization would be performed around Windsor Dr. The channelization includes
approximately 850 feet of grass lined channel improvement with a bottom width of 30 feet and
side slopes of 3 horizontal to 1 vertical. The crossing capacity would be increased from 4- 8 ft x
8 ft culverts to 4 — 8 ft x 8 ft culverts and 2 — 8 ft wide by 6 ft high culverts. It is assumed that
that the 4 existing culverts would need to be demolished and replaced with 6 new culverts. The
total excavation amount for this alternative is 4,400 cubic yards. To minimize impacts on the
environment, this alternative would use native grass plantings.
6.1.6. Alternative 11: Buyouts Alone
Alternative 11 would consist of determining the structures in the impact area prone to damages
with various AEP events and a complete purchase of properties at market value and demolition
costs of removing structures within the impact area (Figure 17).
39
ice'�it!�� •� .y r ... � . -
�`r•u••� -• ,,.-ems,}ti�y�;' ��r� _
�• tip•� r 1 � .t {♦ {
•''�:. � ; � � fir j
h
ME M- 1
16
�I.`t riL • � � fM y• •
Figure 17 - Cooper Creek Impact Area Associated with Alternative 11 and Alternative 13
6.1.7. Alternative 13: Raising Structures in Place
This alternative would determine structures in the impact area are prone to flood damages with
various AEP events and raising homes off foundation and placing support columns underneath
to protect from flooding.
6.1.8. Alternative 17: (17A1) Detention (2C1)+bridge
improvements(8A1)+channelization(8A1)
The goal with this alternative is to reduce the water surface elevations through Cooper Creek by
adding flood storage with detention (Configuration from alternative 2C1) and increasing channel
and crossing capacity along Cooper Creek and through Windsor Drive (8A1). Figure 18 shows
the location of alternative 17A1.
40
� .',�,�,• o ;y�• i-.i off. _ ~� .� a
471
�
,�,,��; . ° ' '•'•_ '��,,-1 0 ,�. � Wi
LQ
W17 . loon ft I
Figure 18 - Location of alternative 17A1
In addition to the detention configuration described under alternative 2C1, channelization would
also be performed around Windsor Dr. The channelization includes approximately 850 feet of
grass lined channel improvement with a bottom width of 30 feet and side slopes of 3 horizontal
to 1 vertical. The crossing capacity would be increased from 4- 8 ft x 8 ft culverts to 4 - 8 ft x 8 ft
culverts and 2 - 8 ft wide by 6 ft high culverts. The total excavation amount for this alternative is
110,400 cubic yards.
6.2. Costs of Final Array of Alternatives
The project costs for the alternatives in the final array are provided in Table 9 below.
Table 9 - Cooper Creek Alternative Costs (FY25 dollars)
-WMP�roject Cost
Alternative 1: No Action $0
Alternative 2A (2A1): Detention above
$3,043,000
Sherman
41
Alternative Project Cost
Alternative 2B (2C1): Detention above Stuart
(elevation 637) $8,662,000
Alternative 2C (2D1): Detention above Stuart
(elevation 634) $10,112,000
Alternative 3: (3A1) Detention (2C1) +
channelization at Windsor Drive $9,194,000
Alternative 5 (5A1): Detention (2C1) + Bridge
Improvements at Sherman Drive $15,226,000
Alternative 8 (8A1): Channelization and
bridge improvement at Windsor Dr. $4,225,000
(50YR) $55,781,000
Alternative 11: Buyouts (25YR) $39,308,000
(10YR) $22,881,000
(50YR) $34,606,000
Alternative 13: Raising Structures in Place (25YR) $26,640,000
(10YR) $16,914,000
Alternative 17 (17A1): Detention (2C1) +
bridge improvement (8A1) + channelization $10,608,000
(8A1)
6.3. Economic Analysis of Final Array of Alternatives
Once the PDT had developed project costs for the final array and economics analysis was
performed (Table 10).
Table 10 - Cooper Creek Economic Analysis (FY25 dollars)
11M3-
First Costs Annual Damages Net Benefits BCR (Mean)
Costs Reduced (Mean)
(Mean)
Alt 2A1 $3,043,000 $134,474 $12,874 ($121,600) 0.10
42
Alt2C1 $8,662,000 $390,113 $301,202 ($88,911) 0.77
Alt 2D1 $10,112,000 $455,417 $335,779 ($119,638) 0.74
Alt 3A1 $9,194,000 $416,833 $335,778 ($81,055) 0.81
Alt 5A1 $15,226,431 $1,587,349 $236,631 ($1,350,718) 0.15
Alt 8A1 $4,225,000 $186,708 $85,595 ($101,113) 0.46
Alt 17A1 $10,608,000 $486,580 $337,429 ($149,151) 0.69
Elevation (50 $34,606,000 $1,540,667 $752,000 ($788,667) 0.49
YR)
Elevation $26,460,000 $1,176,031 $679,055 ($496,976) 0.58
(25YR)
Elevation (10 $16,914,000 $751,753 $542,000 ($209,753) 0.72
YR)
Buyout (50 $55,781,254 $2,200,325 $752,000 ($1,448,325) 0.34
YR)
Buyout (25 $39,307,987 $1,550,527 $679,055 ($871,472) 0.44
YR)
Buyout (10 $22,880,759 $902,545 $542,000 ($360,545) 0.60
YR)
6.4. National Criteria
The PDT utilized data collected from the study and economic analysis to perform an evaluation
of the National Criteria (Table 11).
43
Table 11 -Cooper Creek National Criteria Evaluation
ir Effective Efficient (Net
Alternative Complete D. Acceptable
Reduced)
Alternative 1: No Action N/A N/A N/A N/A
Alternative 2A (2A1): YES Least No, ($121,600) YES
Detention above Sherman effective
Alternative 213 YES, may require
(2C1):Detention above Stuart YES Effective No, ($88,911) mitigation for
(elevation 637) proposed species
Alternative 2C (2D1): YES, may require
Detention above Stuart YES Effective No, ($119,638) mitigation for
(elevation 634) proposed species
Alternative 3: (3A1)
Detention (2C1) + YES, may require
chann tents ion at Windsor YES Effective No, ($81,055) mitigation for
proposed species
Drive
Alternative 5 (5A1):
Detention (2C1) + Bridge Less No, YES, may require
YES
Improvements at Sherman effective ($1,350,718) mitigation for
proposed species
Drive
Alternative 8 (8A1):
Channelization and bridge YES Effective No, ($101,113) YES
improvement at Windsor Dr.
Most
effective No,
Alternative 11: Buyouts More ($1,448,325)
(50YR, 25 YR and 10 YR) YES effective No,($871,472) YES
More No, ($360,545)
effective
Most
effective No, ($788,667)
Alternative 13: Raising More
Structures in Place (50YR, YES effective No ($496,976) YES
25YR, and 10YR) More No,( $209,753)
effective
44
Effective Efficient (Net
• - • •
Complete
Alternative A
Reduced) --is
Alternative 17 (17A1):
Detention (2C1) + bridge YES, may require
YES Effective No, ($149,151) mitigation for
improvement (8A1) +
channelization (8A1) proposed species
*Damages reduced can be found in Table 10
6.5. Comprehensive Benefits Analysis
No action alternative was identified as having positive net benefits in the project area. There
are no significant differences in the RED, EQ and OSE accounts, although any alternative with a
detention basin above Stuart Road may need mitigation for the tri-colored bat (Table 12). Prior
to TSP the team discovered that a portion (approximately 26%) of the project area did include
an at risk community, based on recent updates to the CEJST tool. The team utilized this
information to analyze the alternative with the highest BCR (Alternative 3) to determine if there
were disproportionate impacts to the at risk community under the OSE account via indexing the
property values within the at risk community. The results of this analysis did not provide
sufficient benefits to allow the recommendation of an alternative action, raising the BCR from
0.81 to 0.91.
Table 12 -Cooper Creek Comprehensive Benefits Summary
Alternative
Alternative 1: No Action N/A N/A N/A N/A
Alternative 2A (2A1): Detention Temp benefits Lower
above Sherman BCR=0.10 construction None risk
HHS
Alternative 213 (2C1):Detention Temp benefits May need Lower
above Stuart (elevation 637) BCR=0.77 construction mitigation risk
HHS
Alternative 2C (2D1): Detention Temp benefits May need Lower
above Stuart (elevation 634) BCR=0.74 construction mitigation risk
HHS
Alternative 3: (3A1) Detention (2C1) Temp benefits May need Lower
+ channelization at Windsor Drive BCR=0.81 construction mitigation risk
HHS
Alternative 5 (5A1): Detention (2C1) Temp benefits May need Lower
+ channelization at Sherman Drive BCR=0.15 construction mitigation risk
HHS
45
Alternative—MEd NED RED
Alternative 8 (8A1): Channelization Temp benefits Lower
and bridge improvement at Windsor BCR=0.46 construction None risk
Dr. HHS
BCR=0.34 Lower
Alternative 11: Buyouts BCR=0.44 Temp benefits None risk
construction HHS
BCR=0.60
BCR=0.49 Lower
Alternative 13: Raising Structures in BCR=0.49 Temp benefits None risk
Place construction HHS
BCR=0.72
Alternative 17 (17A1): Detention Temp benefits May need Lower
(2C1) + bridge improvement (8A1) BCR=0.69 construction mitigation risk
+ channelization (8A1) HHS
*HHS =Human Health and Safety
7. TENTATIVELY SELECTED PLAN
The tentatively selected plan is no action. An analysis of the comprehensive benefits does not
support any of the action alternatives.
8. CONCLUSION
Analysis of the data collected during this study indicates that the benefits provided by any of the
action alternatives would not suffice to produce Federal interest to invest in the project.
Therefore, the PDT recommends no action on Cooper Creek at this time.
46
9. RECOMMENDATIONS
In view of the conclusions set forth, and after considering the expected social, economic and
environmental impacts the PDT recommends no Federal action be taken for Cooper Creek
Flood Risk Management Section 205 and completion of a closeout report. The Fort Worth
District review of existing data indicates no Federal interest exists for participation in a flood risk
management project within the study area of Cooper Creek in Denton, Texas.
At the TSP milestone meeting, the decision maker agreed with the District's recommendation of
the no action plan as the TSP for Cooper Creek, provided the following actions were taken: a.
The PDT will complete a closeout report which documents the data and findings resulting from
the study.; b. The PDT will perform a District Quality Control (DQC) review of the closeout
report.; c. The PDT will provide the closeout report to the NFS.; d. The District will follow the
feasibility study termination process in EP 1105-2-58.
Following coordination with affected non-Federal interests, City of Denton, the feasibility phase
should be terminated if analyses indicate a lack of Federal interest or a lack of public support.
The phase is officially terminated when the District Commander advises the MSC Commander
and the appropriate HQ RIT of termination of the study. The CAP database must be updated to
show project status as terminated, with the date and the reason why, and all future capability
amounts will be reduced to zero. The District Commander will also notify the non-Federal
interest, City of Denton, when the study has been officially terminated.
The recommendations contained herein reflect the information available at the time and current
Department of the Army policies governing formulation, evaluation and development of
individual projects under the US Army Corps of Engineers Continuing Authorities Program. It
does not reflect program and budgeting priorities inherent in the formulation of a national Civil
Works program nor the perspective of higher review levels within the Executive Branch.
11 MARCH 2O25
DATE CALVIN A. KROEGER
COL, EN
Commanding
47
10. REFERENCES
Butler D.R., Ecoregions of Texas 2022. https://texasalmanac.com/topics/environment/physical-
regions-texas Accessed July 3, 2024.
Environmental Protection Agency (EPA) 2024. Texas Nonattainment/Maintenance Status for
Each County by Year for All Criteria Pollutants.
https://www3.epa.gov/airquaIity/greenbook/anayo_tx.htmI
Federal Emergency Management Agency (FEMA) 2023. FEMA's National Flood Hazard Layer
Viewer. https://www.fema.gov/flood-maps/national-flood-hazard-layer.
Natural Resources Conservation Service (NRCS). 2024. SSURGO (Soil Survey Geographic
Database) for Denton County, Texas, Natural Resources Conservation Service, U.S.
Dept. of Agriculture. http://soildatamart.nres.usda.gov/. Accessed July 24, 2024.
Runkle, J., K.E. Kunkel, S.M. Champion, B.C. Stewart, D.R. Easterling, J. Nielsen-Gammon,
2022: Texas State Climate Summary 2022. NOAA Technical Report NESDIS 150-TX.
Soil Survey Staff, Natural Resources Conservation Service, United States Department of
Agriculture. Web Soil Survey. Available online at https://websoilsurvey.nres.usda.gov/.
Accessed [July/24/2024].
Texas Commission on Environmental Quality (TCEQ). 2024. 2024 Draft Texas Integrated
Report of Surface Water Quality for Clean Water Act Sections 305(b) and 303 (d).
Texas Parks and Wildlife Department - A. 2024. Texas Ecoregions.
https://tpwd.texas.gov/education/hunter-education/online-course/wildlife-
conservation/texas-ecoregions
Texas Water Development Board (TWDB), 2024. Trinity River Basin.
https://www.twdb.texas.gov/surfacewater/rivers/river basins/trinity/index.asp
United States Census Bureau. "PROFILE OF GENERAL POPULATION AND HOUSING
CHARACTERISTICS."
https://www.census.gov/quickfacts/fact/table/dentoncitytexas/HSGO10223#qf-flag-X.
Accessed on July 24, 2024.
United States Climate Data, Denton, Texas 2024.
https://www.usclimatedata.com/climate/denton/texas/united-states/ustx0353 Accessed
July 3, 2024.
United States Environmental Protection Agency (EPA). 1974. Information on Levels of
Environmental Noise Requisite to Protect Public Health and Welfare with an Adequate
Margin of Safety. EPA 550/9-74-004.
United States Fish and Wildlife Service (USFWS). 2024. Information for Planning and
Consultation tool. https://ipac.ecosphere.fws.gov
48
USACE (2015). Recent US Climate Change and Hydrology Literature Applicable to US Army
Corps of Engineers Missions —Texas-Gulf Region 12. Civil Works Technical Report,
CWTS 2015-08, USACE, Washington, DC
United States Fish and Wildlife Service (USFWS) 2023. "Monarch (Danaus plexippus) Species
Status Assessment Report." V2.1 96 pp + appendices.
United States Geological Survey, Geologic Atlas of Texas 2024.
https://webapps.usgs.gov/txgeology/Accessed July 3, 2024.
49
11 .ACRONYMS
AEP Annual Exceedance Probability
ASTM American Society for Testing and Materials
BCR Benefit Cost Ratio
BMP Best Management Practices
CAP Continuing Authorities Program
CEQ Council on Environmental Quality
CFR Code of Federal Regulations
CJEST Climate and Economic Justice Screening Tool
CWA Clean Water Act
dBA Decibel
DNL Day-Night average sound Level
EAD Expected Annual Damage
EO Executive Order
EPA Environmental Protection Agency
ER Engineering Regulation
FEMA Federal Emergency Management Agency
FPPA Farmland Protection Policy Act
FT/ft Feet/Foot
GHG Greenhouse Gases
HUC Hydrologic Unit Code
HTRW Hazardous, Toxic, Radioactive Waste
IPaC Information for Planning and Consultation
NAAQS National Ambient Air Quality Standards
NED National Economic Development
50
NEPA National Environmental Policy Act
NFS Non-Federal Sponsor
NRCS Natural Resources Conservation Service
NRHP National Registry of Historic Places
O&M Operation & Maintenance
PDT Project Delivery Team
RCRA Resource Conservation and Recovery Act
SSURGO Soil Survey Geographic Database
TCB Tri-Colored Bat
TCEQ Texas Commission on Environmental Quality
TPWD Texas Parks and Wildlife Department
tpy Tons Per Year
U.S./US United States
U.S.0 United States Code
USACE U.S. Army Corps of Engineers
USFWS United States Fish and Wildlife Service
USGS United States Geological Service
51
Appendix A: Cost Engineering
Cooper Creek, Denton, TX
Section 205
Closeout Report
February 2025
Appendix A
Cost Appendix
Project Goals and Objectives
The goal is to provide an economical flood control that can protect properties closer to Cooper
Creek in the city of Denton. The objectives include reduce risk of flood induced damages in the
vicinity of Cooper Creek over the 50-year period of analysis, reduce risk to human health and
safety in the vicinity of Cooper Creek over the 50-year period of analysis, improve emergency
response time in the vicinity of Cooper Creek over the 50-year period of analysis. The final array
of structural alternatives is made of the following 6 alternatives:
• Alternative 1— No Action
• Alternative 2— Detention Basin alone
• Alternative 3 — Detention Basin and channel improvements
• Alternative 5— Detention Basin and Bridge Culvert Modifications
• Alternative 8—Channel Improvements and Bridge culvert modifications
• Alternative 17— Detention Basin, Bridge culvert modifications, channel
improvements.
The three Non-Structural alternatives are the followings:
• Non-Structural 25 year
• Non-Structural 15 year
• No Structural 10 year
Cost estimating activities have been developed to provide the cost of each alternatives needed
to support Feasibility Studies.
Methodology
The PDT members provided all the quantities for all structural alternatives. The cost estimates
were developed in accordance with the guidance contained in ER 1110-2-1302, Civil Works Cost
Engineering, using the MCACES II V 4.4 software was used. This is the most current version of
the MCACES software. The following libraries were used:
• 2023 Cost Book,
• National Labor Seattle 2022,
• Equipment 2022 Region 06.
Each of the six alternatives in the estimate are broken out based on the Civil Works Work
Breakdown Structure (CWWBS). The Relocations CWWBS code was used for utilities.
Assumptions and Constraints
During construction, we assumed the selected prime and subcontractors after the bidding
process are all operating in Denton, TX areas. All labors, materials, tools and equipment except
long lead items or special equipment are sourced in the local construction market. We also
assumed that the equipment is prime owned. All work will be done along Cooper Creek at
specific alternative location. One overhead electrical pole was identified and needs relocation.
The current estimate doesn't take into consideration the fees associated with the relocation.
because the project is in a dense urban area, we anticipate that they will be local traffic
constraints that need to be addressed.
Risks
An Abbreviated Risk Analysis meeting was held with all PDT members to access all
Contingencies and uncertainty that may exist. The risks were determined by a collaboration of
the PDT members and issues that may arise before and during construction. All risks for each
alternative were based on available information and difficulty of the task. The computation of
the contingency for each alternative was influenced by the known variables and their
associated risk and they were incorporated in the Total Project Cost Summary. The Planning
Engineering and Design contingency for each structural and no structural alternatives is 21%.
• The contingencies of all structural alternatives run from 15 to 26% .
• The contingencies of all non-structural alternative run from 15 to 30%
PROJECT: XXXXXX
PROJECT NO: 0
LOCATION: Cooper Creek
This Estimate reflects the scope and schedule in report; Report Name and date
Civil Works Work Breakdown Structure
WBS Civil Works
NUMBER Feature &Sub-Feature Description FULL
($K)
02 RELOCATIONS $4,663.38
06 FISH &WILDLIFE FACILITIES $76
08 ROADS, RAILROADS & BRIDGES $4,588
09 CHANNELS & CANALS $5,620
19 BUILDINGS, GROUNDS & UTILITIES
CONSTRUCTION ESTIMATE TOTALS: _
$14,948
01 LANDS AND DAMAGES $32
30 PLANNING, ENGINEERING & DESIGN $460
31 CONSTRUCTION MANAGEMENT $212
PROJECT COST TOTALS: $15,652
Alt 2A1
02 RELOCATIONS $1,531
06 FISH &WILDLIFE FACILITIES
08 ROADS, RAILROADS & BRIDGES
09 CHANNELS & CANALS
19 BUILDINGS, GROUNDS & UTILITIES $322
CONSTRUCTION ESTIMATE TOTALS: $1,852
01 LANDS AND DAMAGES $32
30 PLANNING, ENGINEERING & DESIGN $460
31 CONSTRUCTION MANAGEMENT $21211
CONTRACT COST TOTALS: $2,557
v Alt 21131
02 RELOCATIONS $288II
06 FISH &WILDLIFE FACILITIES $38
08 ROADS, RAILROADS & BRIDGES
09 CHANNELS & CANALS
19 BUILDINGS, GROUNDS & UTILITIES $7,873
CONSTRUCTION ESTIMATE TOTALS: $8,19911
01 LANDS AND DAMAGES $677
30 PLANNING, ENGINEERING & DESIGN $2,426
31 CONSTRUCTION MANAGEMENT $1,14811
CONTRACT COST TOTALS: $12,450
v Alt 3A1
02 RELOCATIONS $237
06 FISH &WILDLIFE FACILITIES
08 ROADS, RAILROADS & BRIDGES
09 CHANNELS & CANALS $5,397
19 BUILDINGS, GROUNDS & UTILITIES $2,271
CONSTRUCTION ESTIMATE TOTALS: $7,906
01 LANDS AND DAMAGES $32
30 PLANNING, ENGINEERING & DESIGN $2,394
31 CONSTRUCTION MANAGEMENT $1,13411
CONTRACT COST TOTALS: $11,465
v Alt 5A1
02 RELOCATIONS $1,118
06 FISH &WILDLIFE FACILITIES
08 ROADS, RAILROADS & BRIDGES $2,943
09 CHANNELS & CANALS
19 BUILDINGS, GROUNDS & UTILITIES $6,939
CONSTRUCTION ESTIMATE TOTALS: $11,001
01 LANDS AND DAMAGES $32
30 PLANNING, ENGINEERING & DESIGN $3,190
31 CONSTRUCTION MANAGEMENT $1,51611
CONTRACT COST TOTALS: $15,739
v Alt 8A1
02 RELOCATIONS $560
06 FISH &WILDLIFE FACILITIES
08 ROADS, RAILROADS & BRIDGES $823
09 CHANNELS & CANALS $223
19 BUILDINGS, GROUNDS & UTILITIES
CONSTRUCTION ESTIMATE TOTALS: $1,606
01 LANDS AND DAMAGES $1,531
30 PLANNING, ENGINEERING & DESIGN $475
31 CONSTRUCTION MANAGEMENT $22011
CONTRACT COST TOTALS: $3,832
v Alt 17A1
02 RELOCATIONS $579
06 FISH &WILDLIFE FACILITIES
08 ROADS, RAILROADS & BRIDGES $823
09 CHANNELS & CANALS
19 BUILDINGS, GROUNDS & UTILITIES $7,087
CONSTRUCTION ESTIMATE TOTALS: $8,488
01 LANDS AND DAMAGES $2,208
30 PLANNING, ENGINEERING & DESIGN $2,529
31 CONSTRUCTION MANAGEMENT $1,20411
CONTRACT COST TOTALS: $14,429
v Non-Structural 50 yr
02 RELOCATIONS $15,794
06 FISH &WILDLIFE FACILITIES
08 ROADS, RAILROADS & BRIDGES
09 CHANNELS & CANALS
19 BUILDINGS, GROUNDS & UTILITIES
CONSTRUCTION ESTIMATE TOTALS: $15,794
11
01 LANDS AND DAMAGES $37,876
30 PLANNING, ENGINEERING & DESIGN $2,529
31 CONSTRUCTION MANAGEMENT $1,20411
CONTRACT COST TOTALS: $57,403
v Non-Structural 25 yr
02 RELOCATIONS $11,116
06 FISH &WILDLIFE FACILITIES
08 ROADS, RAILROADS & BRIDGES
09 CHANNELS & CANALS
19 BUILDINGS, GROUNDS & UTILITIES
CONSTRUCTION ESTIMATE TOTALS: $11,116
01 LANDS AND DAMAGES $25,630
30 PLANNING, ENGINEERING & DESIGN $2,529
31 CONSTRUCTION MANAGEMENT $1,20411
CONTRACT COST TOTALS: $40,479
v Non-Structural 10 yr
02 RELOCATIONS $5,948
06 FISH &WILDLIFE FACILITIES
08 ROADS, RAILROADS & BRIDGES
09 CHANNELS & CANALS
19 BUILDINGS, GROUNDS & UTILITIES
CONSTRUCTION ESTIMATE TOTALS: $5,948
01 LANDS AND DAMAGES $13,897
30 PLANNING, ENGINEERING & DESIGN $2,529
31 CONSTRUCTION MANAGEMENT $1,20411
CONTRACT COST TOTALS: $23,578
v Non-Structural Raising 50 yr
02 RELOCATIONS $18,639
06 FISH &WILDLIFE FACILITIES
08 ROADS, RAILROADS & BRIDGES
09 CHANNELS & CANALS
19 BUILDINGS, GROUNDS & UTILITIES
CONSTRUCTION ESTIMATE TOTALS: $18,639
01 LANDS AND DAMAGES
30 PLANNING, ENGINEERING & DESIGN $2,529
31 CONSTRUCTION MANAGEMENT $1,20411
CONTRACT COST TOTALS: $22,372
v Non-Structural Raising 25 yr
02 RELOCATIONS $13,119
06 FISH &WILDLIFE FACILITIES
08 ROADS, RAILROADS & BRIDGES
09 CHANNELS & CANALS
19 BUILDINGS, GROUNDS & UTILITIES
CONSTRUCTION ESTIMATE TOTALS: $13,119
01 LANDS AND DAMAGES
30 PLANNING, ENGINEERING & DESIGN $2,529
31 CONSTRUCTION MANAGEMENT $1,20411
CONTRACT COST TOTALS: $16,852
v Non-Structural Raising 10 yr
02 RELOCATIONS $11,000
06 FISH &WILDLIFE FACILITIES
08 ROADS, RAILROADS & BRIDGES
09 CHANNELS & CANALS
19 BUILDINGS, GROUNDS & UTILITIES
CONSTRUCTION ESTIMATE TOTALS: $11,000
01 LANDS AND DAMAGES II
30 PLANNING, ENGINEERING & DESIGN $2,529
31 CONSTRUCTION MANAGEMENT $1,204
CONTRACT COST TOTALS: $14,733
Appendix B : Environmental
Cooper Creek, Denton, TX
Section 205
Closeout Report
February 2025
3. EXISTING CONDITIONS
This chapter presents a description of the environmental resources and baseline conditions that
could be affected from implementing the proposed alternative in accordance with the National
Environmental Policy Act (NEPA) (42 U.S. Code [USC] 4321 et seq.) and its implementing
regulations published by the Council on Environmental Quality (CEQ) (40 Code of Federal
Regulations [CFR] §§1500 - 1508), and the Civil Works Program of the USACE's NEPA
regulation (33 CFR 230) and associated implementation guidance (ER 200-2-2). The level of
detail used in describing a resource is commensurate with the anticipated level of potential
environmental impact. The project study area occurs along Cooper Creek which flows through
the City of Denton, Texas. Cooper Creek is located in central Denton County, which is in the
northcentral portion of the state (Figure 1). Cooper Creek runs through a developed area of
Denton, Texas. Recurrent flooding of Cooper Creek induces damages to adjacent properties,
increases risk to human health and safety, and inundates roadways resulting in road closures,
traffic delays and increased emergency response times. At least one known fatality has been
attributed to flood waters from Cooper Creek. In addition, high flow events are contributing to
erosion downstream of Avondale Park with the channel encroaching on residential lots and
fence lines.
ME
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o.. - PA --
.�
M
OK r TN f� NV
AR —��
NM
GA
i
TX LA j
N
1
Figure 1. Project Study Area Map
3.1. Climate
The climate of the study area is humid subtropical with warm to hot summers and mild winters. The
average annual high temperature is about 76 degrees Fahrenheit, with an average summer high
of about 96 degrees for the months of June, July, and August, and an average annual winter low
temperature of 54 degrees. Periods of freezing temperatures are infrequent and rainfall averages
about 38 inches annually (U.S. Climate, 2024). Severe weather occurs periodically in the form of
severe thunderstorms, tornadoes, flood-producing extreme precipitation events, and occasional
winter ice storm (Runkle et al, 2022).
1
3.2. Geology
The project area is in a region known as the Eastern Cross Timbers Ecoregion. This region
extends southward from the Red River through eastern Denton County and along the boundary
between Dallas and Tarrant counties. It then stretches through Johnson County to the Brazos
River and into Hill County (Butler, 2022). The region includes rolling hills, cuestas, and ridges.
Soils within the Cross Timbers are mostly sandy, loamy, and are underlain by sand, shale, clay,
sandstone, calcareous shale, and limestone. Today, livestock farming is the main land use, but
some cropland also occurs (TPWD-A 2024). The City of Denton sits on top of the Grayson Marl
rock formation. Grayson Marl, mostly marl, is light-greenish-gray to medium-gray, weathers to
grayish-yellow. Thickness of Grayson Marl in Texas is between 15 and 60 feet (USGS, 2024).
3.3. Soils
The Farmland Protection Policy Act (FPPA) (Public Law 97-98, Title XV, Subtitle I, Section
1539-1549 requires federal actions to minimize unnecessary and irreversible conversion of
farmland to nonagricultural uses, specifically prime farmlands. The Act defines prime farmlands
as "...land that has the best combination of physical and chemical characteristics for producing
food, feed, fiber, forage, oilseed, and other agricultural crops with minimum inputs of fuel,
fertilizer, pesticides, and labor, and without intolerable soil erosion..." The Natural Resources
Conservation Service (NRCS) is responsible for designating soils as prime farmland soils.
The project area consists of a variety of ground cover types with the majority consisting of
disturbed soils covered by urban development as the City of Denton has grown around the
banks of Cooper Creek. The proposed footprint of the project does not include land or soil
suitable for agricultural activities. Based on the Soil Survey of Denton County, Texas (Soil
Conservation Service, 1988), soils surrounding the project area are classified in the Sanger and
Wilson-Urban land complex soil series, which are classified as a clayey and well-drained soils
weathered from claystone with low slopes (Figure 2). According to Soil Survey Geographic
Database (SSURGO) information acquired from the Natural Resources Conservation Service
(NRCS 2024), soils within the Sanger and Wilson-Urban series are not considered prime
farmlands (Soil Survey Staff, 2024).
2
� s
�"`- - --� �- '• ,�'• _yam
}
-Soil Types °
Sanger-Urban land complex,1-5%slope j -
- r .
-Wilson-Urban land complex,0-2%slope
'r
Dallas Cooper Creek Soils Map N
CGI;\R,I'SGS,I:.I..Cmmnnniq plops Cnnm6nv.,Lien rortlfl'rxas,(Src of Uennm,l?xas A
I.ks&IX ildbf,,ti Open S- M I3 Nh ft h. "pnn I 2024
c- !1'ecL I gi. I-,Nl'II!\1S\,CSCS EPA,NI S,I S1 Bmea lSU\t-SIRS,lrl�s
1 ,ks&RJdl&,I'.i,'I'—,Inm,G,,nm,Safe(mpl,I'\G,Nil'IIj N:\S:\I.SC S,1.1'r\,NI'S,
Coordinate Scsve WGS 1984 Web lleccatot Ansilia-Sphere 0.23
Figure 3. Cooper Creek Soils Map
3.4. Surface Water
Cooper Creek lies in the Elm Fork Trinity Watershed (HUC 12030103). Streams in this
watershed vary from slow, meandering streams flowing to smaller, riffle and pool types in the
smaller watersheds. Cooper Creek is a 6.3-mile long tributary to the Trinity River which
eventually leads into Lewisville Lake.
The project area consists of a shallow stream about 10 feet wide. Flow through the site is
generally slow moving and perennial. Despite erosion occurring in the area, turbidity is low and
the water clarity is good. The stream bed is composed of some clays and silts towards the
center of the channel, while red clays are found along the shoreline and at the East Sherman
Drive bridge.
3
3.5. Floodplains
The project area is classified as Zone AE Regulatory Floodway on the Federal Emergency
Management Flood Insurance Rate Map as part of the Denton County Unincorporated Areas
(48121C0360G) (Figure 4). Immediately in the project area, floodplain characteristics are
restricted on either side by residential housing communities (FEMA 2023).
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3.6. Water Quality
Regional water quality is influenced by lithology, soil composition and land use activities. In
Denton County, rugged upland areas have been cleared for urban use. Community housing,
businesses, and recreation are important land uses. Cooper Creek is part of the Upper Elm Fork
Trinity Watershed. Water quality in the Trinity River Basin is generally good while average
4
stream gradients and dissolved oxygen levels are typically lower than waters in the lower basin,
whereas turbidity, total suspended solids, total organic carbon, total phosphorus and
biochemical oxygen demand values are typically higher (TWDB, 2024).
Section 303(d) of the Clean Water Act (CWA) requires states to identify waters where existing
pollution controls are not stringent enough to achieve state water quality standards and
establish a priority ranking of these waters. The Texas Commission on Environmental Quality is
responsible for assessing water quality monitoring data and developing a 303(d) list every two
years in accordance with the CWA. The Texas Draft 2024 303(d) List represents the most
recent evaluation of water quality data. Cooper Creek itself is not listed as an impaired
waterbody for any appraised metrics. There are no waterbodies upstream of Cooper Creek that
would contribute to the understanding of its water quality (TCEQ, 2024).
3.7. Wetlands
Wetlands are often defined as areas where the frequent and prolonged presence of water at or
near the soil surface drives the natural system including the type of soils (i.e. hydric soils) that
form, the plants that grow and the fish and/or wildlife that use the habitat. A review of the
National Wetlands Invintory database shows that the existing project footprint (Figure 5) covers
approximately 27.3 acres with 1.1 acres occurring within Freshwater Forested/Shrub Wetland
and 5 acres of that occurring in Riverine wetlands.
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5
3.8. Biological Resources
3.8.1. Vegetation
The project study area is located within the Cross Timbers and Prairies ecoregion, which covers
the upper center portion of the state of Texas. Grassland species such as little bluestem,
Indiangrass and big bluestem are common. Texas mulberry, American elm and Osage orange
are more common here than they were to the east. In the west, live oak becomes more
important, replacing the post oak of the east. Decreasing moisture discourages clusters of trees,
and trees form isolated stands. Flameleaf sumac, redbud, Mexican plum and Eastern red cedar
become more prevalent. Wildlife is a mixture of eastern forest and prairie species.
3.6.3. Aquatic Resources
Cooper Creek has habitat conditions that can support many species of fish and invertebrates
(Table 1). Fish communities characteristically in the area include a sunfish and minnow-
dominated community along with darters and occasional catfishes and an assemblage of
macroinvertebrates. No protected or sensitive species are known to occur in the creek.
Table 1. Aquatic species potentially occurring in the project area.
Common Name Scientific Name
Microcaddisfly Paucicalcaria ozarkensis
Nearctic Paduniellan Caddisfly Paduniella nearctica
Mayfly Parale to hlebia calcarica
Elevated Spring Am hi od Stygobromus elatus
Boston Mountains Crayfish Cambarus cause i
Alabama Shad Alosa alabamae
White perch Pomoxis annularis
Pyramid Pi toe Pleurobema rubrum
Purple Lilli ut Toxolasma lividum
Iso od Lirceus bicus idatus
Queen Snake Regina se temvittata
Alligator Gar Atractosteus spatula
American Eel Anguilla rostrata
3.8.2. Wildlife
Considerable urban growth and expansion throughout the area surrounding Cooper Creek has
caused local wildlife to become fragmented. Cooper Creek serves as a green corridor that
provides ample habitat for several common species of birds and mammals. Table 2 provides a
partial list of common bird and mammal species known to occur in areas near the project area
that may use the project area for foraging, nesting, resting, or migration.
6
Table 2. Common Wildlife Species in the Vicinity of the Project Area
Common Name Scientific Name Common N—a—m—e—T Scientific Name
Birds
Black vulture Coragyps atratus Ring-neck duck Aythya collaris
Blue jay Cyanocitta cristata Wood duck Aix sponsa
Cardinal Cardinalis Mockingbird Mimus polyglottos
Common yellowthroat Geothlypis trichas Mourning dove Zenaida macroura
Eastern phoebe Sayornis phoebe Robin Turdus migratorius
Eastern wood-pewee Contopus virens Turkey vulture Cathartes aura
Great horned owl Bubo virginianus Red-tailed hawk Buteo jamaicensis
Mammals
Little brown bat Myotis lucifugus Opossum Didelphis virginiana
Eastern gray squirrel Sciurus carolinensis Raccoon Procyon lotor
White-tailed deer Odocoileus Nine-banded Dasypus
vir inianus armadillo novemcinctus
Eastern cottontail Sylvilagus floridanus Eastern chipmunk Tamias striatus
Woodchuck Marmota monax Beaver Castor canadensis
Striped skunk Mephitis Bobcat Felis rufus
3.9. Threatened and Endangered Species
The USFWS Information for Planning and Consultation (IPaC) tool was utilized to determine
species listed under the Endangered Species Act that may occur in or near the Cooper Creek
study area (USFWS, 2024). A total of five Federally threatened or endangered species and
one candidate species were identified; however, the project area only contains suitable habitat
for one species (Table 3). No Federally designated critical habitat for any of the listed species
is present in the action area. The bald eagle has been delisted but the protections provided by
the Bald and Golden Eagle Protection Act and the Migratory Bird Treaty Act remain in effect.
7
Table 3. Federally Listed Species identified on the IPaC
Species Name Status Habitat Description Suitable Habitat in the
Action Area
Mammals
Tricolored Bat PE Summer habitat: wide variety of forested/wooded habitats for Summer Habitat: Yes
Perimyotis subflavus roosting. Roost among leaves of live or recently dead deciduous
hardwood trees, but may also be found in Spanish moss, pine Winter Habitat: No
trees, and occasionally manmade structures.
Winter habitat hibernacula : caves or abandoned mines.
Birds
Whooping crane E Dense marshes and wetlands with nest sites found primarily No -Urban area with sparse
Grus americana located in shallow diatom ponds that contain bulrush. During forested riparian area lacking
migration, whooping cranes use a variety of habitats; however wetlands/marshes
wetland mosaics appear to be the most suitable.
Piping plover T Coastal shorelines and open mudflats and sandy areas. No- Open areas around the
Charadrius melodus creek are grassy and
disturbed. Lack sandy areas.
Rufa red knot T Wintering and migration habitats are muddy or sandy coastal No - shorelines are
Calidris canutus rufa areas, specifically, bays and estuaries, tidal flats, and urbanized and surrounded
unimproved tidal inlets with sand spits, islets, shoals, and by patches of Riparian
sandbars Forest
Reptiles
Alligator snapping turtle PT Freshwater rivers and lakes with deep floors. No—generally too shallow
Macrochel s temminckii
Insects
Monarch butterfly C Monarchs need healthy and abundant milkweed embedded No—grassy riparian area
Danaus plexippus within diverse nectaring habitat. Many monarchs use a variety of with potential for host plant is
roosting trees along the fall migration route. Although monarch regularly disturbed and
butterfly can occur within the project areas, they will not be mowed.
affected by construction due to the lack of milkweed presence
and unlikelihood of milkweed to occur in the sites due to the
regular mowing of the grassy areas adjacent to Cooper Creek.
E= Endangered T= Threatened PE= Proposed Endangered PT= Proposed Threatened C= Candidate
Source: U.S. Fish and Wildlife Service IPAC website and Arkansas Ecological Service Office database.
8
3.10. Recreational Resources
Occasional fishing, hiking or wildlife watching may occur immediately along the creek; however,
the creek is bordered on all sides by private land making other recreational activities unavailable
due to restricted land access.
3.11. Socioeconomics
Socioeconomics is defined as the basic attributes and resources associated with the human
environment, particularly population, demographics, and economic development. Demographics
entail population characteristics and include data pertaining to race, gender, income, housing,
poverty status, and educational attainment. Economic development or activity typically includes
employment, wages, business patterns, an area's industrial base, and its economic growth.
The socio-economic characteristics of Denton, Texas, the nearest town located near the project
study area are presented in Table 4. The City of Denton had a population of 158,349 living in
52,000 households in 2022. The racial makeup of the city was 67.8 percent White, 11.5 percent
African American, 0.8 percent Native American, 3.5 percent Asian, 0.0 percent other, and 11.1
percent from two or more races. Of the total population, 24.1 percent were of Hispanic or Latino
origin. Roughly 15.7 percent of families in the city live below the poverty line (U.S. Census
Bureau, 2022).
Table 4. Population Data for Denton, Texas
Population Metric Denton, Texas
Total Population 158,349
Total Households 52,000
White 67.8%
Black or African American 11.5%
Native American or Alaska 0.8%
Native
Asian 3.5%
Native Hawaiian or Other 0.0%
Pacific Islander
Other Race 0.0%
Two or More Races 11.1%
Hispanic 24.1%
Under 5 years 4.9%
5 to 19 years 18.5%
20 to 64 years 64.4%
Over 64 years 12.2%
High School Diploma 91.5%
Bachelor's Degree or Higher 40.0%
Median Household Income $71,717
9
3.12. Incorporating the Needs and Considerations of All at Risk Communities
An analysis using the Climate and Economic Justice Screening Tool (CEJST) was conducted
to identify at risk communities in or near the project area (Figure 6). The tool identifies at risk
communities if they are in a census tract that meets the thresholds for at least one of the
tool's categories of burden, or if they are on land within the boundaries of Federally
Recognized Tribes. The CEJST showed that a portion of the area surrounding the project
area was classified as being at risk. Categories that were found to exceed the socioeconomic
threshold included Climate Change (Projected wildfire risk and low income), energy, health,
housing, legacy pollution, transportation, water and wastewater, and workforce development.
All of these metrics were found to fall within the "low income" category.
Tmd Infonnation
Number:48121020503
County:Denton County
� State:Texas
Population 6.727
+ Tract demographics
rdent.lied as duadvantaeed'
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Figure 6. Climate and Economic Justice Screening Tool Results for the Cooper Creek
Project Area.
10
3.13. Noise
Federal and local governments have established noise guidelines and regulations for the
purpose of protecting citizens from potential hearing damage and from various other adverse
physiological, psychological, and social effects associated with noise. The Federal Interagency
Committee on Urban Noise developed land-use compatibility guidelines for noise in terms of
day-night average sound level (DNL). It is recommended that no residential uses, such as
homes, multifamily dwellings, dormitories, hotels, and mobile home parks, be located where the
noise is expected to exceed a DNL of 65 decibels (dBA). For outdoor activities, the EPA
recommends DNL of 55 dBA as the sound level below which there is no reason to suspect that
the general population would be at risk from any of the effects of noise (EPA, 1974). Noise-
sensitive receptors are facilities or areas where excessive noise may disrupt normal activity,
cause annoyance, or loss of business. Land uses such as residential, religious, educational,
recreational, and medical facilities are more sensitive to increased noise levels than are
commercial and industrial land uses.
Review of the project area show that it is in an urban area comprised of residential homes and
businesses. There would be temporary noise disturbance from construction associated with the
project.
3.14. Air Quality
The U.S. Environmental Protection Agency (EPA) has the primary responsibility for regulating
air quality nationwide. The Clean Air Act (42 U.S.C. 7401 et seq.), as amended, requires the
EPA to set National Ambient Air Quality Standards (NAAQS) for wide-spread pollutants from
numerous and diverse sources considered harmful to public health and the environment. The
Clean Air Act established two types of national air quality standards classified as either
"primary" or"secondary." Primary standards set limits to protect public health, including the
health of at-risk populations such as people with pre-existing heart or lung diseases (such as
asthma), children, and older adults. Secondary standards set limits to protect public welfare,
including protection against visibility impairment, damage to animals, crops, vegetation, and
buildings.
EPA has set NAAQS for six principal pollutants, which are called "criteria" pollutants. These
criteria pollutants include carbon monoxide (CO), nitrogen dioxide (NO2), ozone (03),
particulate matter less than 10 microns (PM10), particulate matter less than 2.5 microns
(PM2.5), sulfur dioxide (SO2) and lead (Pb). If the concentration of one or more criteria pollutant
in a geographic area is found to exceed the regulated "threshold" level for one or more of the
NAAQS, the area may be classified as a non-attainment area. Areas with concentrations of
criteria pollutants that are below the levels established by the NAAQS are considered either
attainment or unclassifiable areas.
The project area is located within Denton County, Texas and is part of an area designated as
Nonattainment, meaning concentrations of criteria pollutants are above the levels established by
the NAAQS (EPA 2024). Due to the area's NAAQS Nonattainment status, a General Conformity
determination will be required.
11
3.15. Hazardous, Toxic, and Radioactive Waste (HTRW)
No Recognized Environmental Conditions were identified within one mile of the project area that
could be reasonably expected to affect the Cooper Creek CAP 205 project. Although not
classified as HTRW under USACE regulations, several oil and gas infrastructure sites were
identified within the surrounding area. As a result of these findings, pipelines and wells within
the project vicinity and along potential site access routes should be precisely located during
PED to ensure no unintended interaction occurs with the existing oil and gas facilities.
Despite the lack of identified sites that could be reasonably expected to affect the project, there
is always a possibility that previously unidentified HTRW could be uncovered, even when a
proposed project is entirely within a preexisting project footprint. An updated HTRW survey will
be required should the project be reconsidered and funded at a future time. Additionally, care
should be taken to identify and address HTRW concerns that may arise in a timely manner, so
as not to affect proposed project timelines.
3.16. Cultural Resources
The study area is located on the southern plains in north Texas in the City of Denton along
Cooper Creek. The study area is heavily developed for residential and commercial use and the
banks and channel of Copper Creek have been modified to control erosion. There are
numerous cultural resources recorded within this region that include National Register of
Historic Places (NRHP) listed properties, archeological sites, cemeteries, and historical
markers. A preliminary assessment of the cultural resources within one kilometer of the
proposed study area was conducted using a desktop review of the databases maintained by the
Texas Historical Commission and the Texas Archeological Research Laboratory for cultural
resources as well as a review of historic aerial imagery. This assessment identified one
previously recorded cultural resource, the Fairhaven Retirement Home, a NRHP listed property,
approximately 950 meters from the proposed study area. There are no other previously
recorded cultural resources.
Only two previous archeological surveys are within one kilometer of the study area. Both
surveys were conducted in 1993 for the Federal Highway Administration along United States
(U.S.) Highway 77 and North Locust Street. While there have been numerous cultural resource
investigations conducted in the surrounding region, there are no other previous investigations in
the proposed study area or within one kilometer.
The primary considerations concerning cultural resources are threats to buried archeological
deposits because of earthmoving activities. However, most of the study area has been
developed for residential and commercial use. The soils within the study area are mapped as
Sanger-Urban land complex and Wilson-Urban land complex, both clayey soils originating from
alluvium from weathered slopes and bedrock. Although the area has not been previously
investigated, the residential and commercial development and the presence of urban soils in the
study area suggest that the probability for intact archeological sites to occur in this area is low.
12
4. Environmental Consequences
This section describes the natural and human environments that exist at the project and the
potential impacts of the No Action Alternative (Alternative 1) and the action alternatives, as
required under NEPA.
Impacts (consequences or effects) can be either beneficial or adverse and can be either directly
related to the action or indirectly caused by the action. Direct effects are caused by the action
and occur at the same time and place (40 CFR § 1508.8 [a]). Indirect effects are caused by the
action and are later in time or further removed in distance but are still reasonably foreseeable
(40 CFR § 1508.8 [b]). As discussed in this section, the alternatives may create temporary (less
than one year), short-term (up to three years), long-term (three to ten years), or permanent
impacts following the implementation of the Recommended Plan.
Whether an impact is significant depends on the context in which the impact occurs and the
intensity of the impact (40 CFR § 1508.27). The context refers to the setting in which the impact
occurs and may include society as a whole, the affected region, the affected interests, and the
locality. Impacts on each resource can vary in degree or magnitude from a slightly noticeable
change to a total change in the environment. For the purpose of this analysis, the intensity of
impacts would be classified as negligible, minor, moderate, or major. The intensity thresholds
are defined as follows:
• Negligible: A resource would not be affected or the effects would be at or below the level
of detection, and changes would not be of any measurable or perceptible consequence.
• Minor: Effects on a resource would be detectable, although the effects would be
localized, small, and of little consequence to the sustainability of the resource. Mitigation
measures, if needed to offset adverse effects, would be simple and achievable.
• Moderate: Effects on a resource would be readily detectable, long-term, localized, and
measurable. Mitigation measures, if needed to offset adverse effects, would be
extensive and likely achievable.
• Major: Effects on a resource would be obvious and long-term and would have
substantial consequences on a regional scale. Mitigation measures to offset the adverse
effects would be required and extensive, and success of the mitigation measures would
not be guaranteed.
4.1. Future Without Project Conditions — No Action Alternative
If No Action is taken to address flooding along Cooper Creek, the most likely future condition of
the area is as follows:
• Recurrent flooding of Cooper Creek will continue to cause damages to adjacent
properties.
13
• Increased risk to human health and safety as a result of inundated roadways, road
closures, traffic delays, and increased emergency vehicle response times.
• Under the No Action Alternative, physical and Biological Resources are expected to
remain the same as described in the Existing Conditions Section of this report.
• If no Federal action is taken at Cooper Creek, the streambank will continue to erode
downstream of Avondale Park and cause encroachments on residential lots and fence
lines.
4.2. Future With Project Conditions
4.2.1 Climate
The project encompasses a relatively small area when compared to the global scale.
Therefore, any changes with respect to incorporating changing conditions resulting from each
alternative would be negligible.
At the state level, Greenhouse Gasses (GHGs) are a regulated pollutant under the Prevention
of Serious Degradation program when emissions exceed thresholds. The threshold for new
source emissions is the project emissions are above the major source threshold for a regulated
pollutant that is not GHGs and will emit or have the potential to emit 75,000 tons per year (tpy)
or more CO2e.
Construction activities associated with each alternative would generate GHG emissions
because of combustion of fossil fuels while operating on- and off-road mobile sources. The
primary GHGs generated during construction are CO2, CH4, and N2O. The other GHGs such
as hydrofluorocarbons, perfluorocarbons, and sulfur hexafluoride are typically associated with
specific industrial sources and processes and would not be emitted during construction.
After construction is complete, all GHG emissions would cease, and the area would return to
baseline conditions. Overall, the total direct and indirect adverse impacts would be constrained
to very small increases in GHG emissions to the atmosphere from operation of on- and off-road
mobile sources.
4.2.2 Geology
4.2.2.1 Alternative 2 Detention Basin Alone
Construction activities associated with Alternative 2 would be shallow in nature and have
insignificant effect on the local geology. Alternative 2 would have no impact on the local
geology.
4.2.2.2 Alternatives 3, 5, 8, and 17 Detention Basin and Channel Improvements
Construction activity effects associated with Alternative 3, 5, 8, and 17 would be the same as
those for Alternative 2.
4.2.3 Soils
4.2.3.1 Alternative 2 Detention Basin Alone
Disturbances to soil would primarily be from removal of upland trees and the excavation of soil
from backhoe operation to meet detention basin specifications. Soils would be temporarily
14
exposed to erosion during construction before being planted with native grasses. Best
management practices would be put in place to reduce erosion and prevent downstream
sedimentation until exposed soils are set in place with native plantings.
All construction activities will be limited to the south easements along Cooper Creek and north
of the houses along Wolftrap Drive, which would not typically be a desirable location for farming
and would be unavailable for farming. No impacts to prime farmland are expected.
4.2.3.2 Alternative 3 Detention Basin and Channel Improvements
Disturbances to soils under Alternative 3 would be similar in scope as those mentioned in
section 4.2.1.2. In addition, disturbances to soil because of channel improvements would be
primarily caused by backhoe operations to widen and straighten the channel. Soils would be
temporarily exposed to erosion during construction before being seeded with native grasses.
Best management practices would be put in place to reduce erosion and prevent downstream
sedimentation until exposed soils are set in place with native plantings. No impacts to prime
farmland are expected.
4.2.3.3 Alternative 5 Detention Basin and Bridge Culvert Modifications
Disturbances to soils under Alternative 5 would be like those mentioned in section 4.2.1.2.
4.2.3.4 Alternative 8 Channel Improvements and Bridge Culvert Modifications
Disturbances to soils under Alternative 8 would be like those mentioned in section 4.2.1.2.
4.2.3.5 Alternative 17 Detention Basin, Bridge Culvert Modifications, Channel
Improvements
Disturbances to soils under Alternative 17 would be like those mentioned in section 4.2.1.2.
4.2.4 Surface Water
4.2.4.1 Alternative 2 Detention Basin Alone
Construction activities associated with Alternative 2 would have temporary direct and indirect
impacts to water quality by causing an increase in river turbidity. This would have further indirect
effects for a short distance downstream until the sediment is diluted. Temporary, minor adverse
effects on surface water are expected during construction but will cease once construction of
the project is complete.
4.2.4.2 Alternative 3 Detention Basin and Channel Improvements
Effects to surface water quality under Alternative 3 would be like those listed under section
4.2.4.1.
4.2.4.3 Alternative 5 Detention Basin and Bridge Culvert Modifications
Effects to surface water quality under Alternative 5 would be like those listed under section
4.2.4.1.
4.2.4.4 Alternative 8 Channel Improvements and Bridge Culvert Modifications
15
Effects to surface water quality under Alternative 8 would be like those listed under section
4.2.4.1.
4.2.4.5 Alternative 17 Detention Basin, Bridge Culvert Modifications, Channel
Improvements
Effects to surface water quality under Alternative 17 would be like those listed under section
4.2.4.1.
4.2.5 Floodplains
4.2.5.1 Alternative 2 Detention Basin Alone
Consistent with Executive Order 11988, Floodplain Management, locating Alternative 2 in the
floodplain would be the only practicable alternative. Alternative 2 would not increase the base
flood elevation to a level that would violate applicable floodplain regulations or ordinances, nor
does it degrade the natural floodplain characteristics of the project area. Adding the detention
area will minimize overbank flooding that is experienced under the existing condition. Minor
beneficial impacts to floodplains are expected.
4.2.5.2 Alternative 3 Detention Basin and Channel Improvements
Consistent with Executive Order 11988, Floodplain Management, locating Alternative 3 in the
floodplain would be the only practicable alternative. Alternative 3 would not increase the base
flood elevation to a level that would violate applicable floodplain regulations or ordinances, nor
does it degrade the natural floodplain characteristics of the project area. Improving the channel
will promote more efficient water flow along Cooper Creek and minimize overbank flooding that
is experienced under the existing condition. Minor beneficial impacts to floodplains are
expected.
4.2.5.3 Alternative 5 Detention Basin and Bridge Culvert Modifications
Effects to floodplains under Alternative 5 would be like those mentioned in section 4.2.6.2.
4.2.5.4 Alternative 8 Channel Improvements and Bridge Culvert Modifications
Effects to floodplains under Alternative 8 would be like those mentioned in section 4.2.6.2.
4.2.5.5 Alternative 17 Detention Basin, Bridge Culvert Modifications, Channel
Improvements
Effects to floodplains under Alternative 17 would be like those mentioned in section 4.2.6.2.
4.2.6 Water Quality
4.2.6.1 Alternative 2 Detention Basin Alone
Temporary localized adverse effects are expected from construction activities occurring in the
creek as described in section 4.2.4.1; however, turbidity conditions would return to baseline
conditions after construction is complete. Minor effects to water quality are expected.
4.2.6.2 Alternative 3 Detention Basin and Channel Improvements
16
Temporary localized adverse effects are expected from construction activities occurring in the
creek as described in section 4.2.4.1; however, turbidity conditions would return to baseline
conditions after construction is complete. Best management practices will be used to stabilize
the bank during construction. Stabilizing the bank would allow improved water quality by slowing
or eliminating the amount of siltation and debris that sloughs into waters from storm runoff or
high swift moving waters and reduce turbidity. Improving the water quality within the study area
would most likely benefit the surrounding watershed. Minor, long-term beneficial effects to water
quality are expected.
4.2.6.3 Alternative 5 Detention Basin and Bridge Culvert Modifications
Effects to water quality under Alternative 5 would be like those mentioned in section 4.2.5.1.
4.2.6.4 Alternative 8 Channel Improvements and Bridge Culvert Modifications
Effects to water quality under Alternative 8 would be like those mentioned in section 4.2.5.2.
4.2.6.5 Alternative 17 Detention Basin, Bridge Culvert Modifications, Channel
Improvements
Effects to water quality under Alternative 17 would be like those mentioned in section 4.2.5.2.
4.2.7 Wetlands
Consistent with Executive Order 11990, Protection of Wetlands, the construction of any of the
Alternatives would not contribute to the loss, destruction, or degradation of wetlands. The only
wetlands within the project area are riverine and they would not be altered as minimal to no
vegetation will be removed and the change in water flow would be beneficial as described in
other sections. No impacts to wetlands are expected.
4.2.8 Biological Resources
4.2.8.1 Alternative 2 Detention Basin Alone
Stream bank preparation would be required during implementation of Alternative 2. Construction
involves the removal of trees and some soil removal or relocation. Any species utilizing the trees
would have to seek other foraging, nesting, or resting habitat in the area; however, there are
sufficient trees of similar size and species in the immediate area that the loss should not
contribute to the injury or mortality of individuals. Noise and other disturbances associated with
construction would also temporarily adversely impact terrestrial species utilizing wildlife habitats
adjacent to the project site and cause individuals to avoid the area until construction is
complete.
4.2.8.2 Alternative 3 Detention Basin and Channel Improvements
Stream bank preparation would be required during implementation of Alternative 3. Construction
involves the removal of trees and some soil removal or relocation. Any species utilizing the trees
would have to seek other foraging, nesting, or resting habitat in the area; however, there are
17
sufficient trees of similar size and species in the immediate area that the loss should not
contribute to the injury or mortality of individuals. Noise and other disturbances associated with
construction would also temporarily adversely impact terrestrial species utilizing wildlife habitats
adjacent to the project site and cause individuals to avoid the area until construction is
complete.
Aquatic organisms presently utilizing shoreline or near shore habitats adjacent to the project site
would be temporarily displaced. Since the desired outcome of the project would be to alter local
hydraulics of the creek, the aquatic species adapted to the present hydraulic regime of Cooper
Creek, or near the project site, would be adversely impacted through changes in aquatic habitat.
Aquatic organisms would also likely encounter temporary impacts from vibrations and noise
caused by construction equipment and from activities caused by personnel on site.
4.2.8.3 Alternative 5 Detention Basin and Bridge Culvert Modifications
Effects to biological resources under Alternative 5 would be like those mentioned in section
4.2.8.2.
4.2.8.4 Alternative 8 Channel Improvements and Bridge Culvert Modifications
Effects to biological resources under Alternative 8 would be like those mentioned in section
4.2.8.2.
4.2.8.5 Alternative 17 Detention Basin, Bridge Culvert Modifications, Channel
Improvements
Effects to biological resources under Alternative 17 would be like those mentioned in section
4.2.8.2.
4.2.9 Threatened and Endangered Species
4.2.9.1 Alternative 2 Detention Basin Alone
Using the IPaC Consultation Package Builder and the Evaluate Determination Keys tools, the
USACE determined that the activities related to the construction and implementation of
Alternative 2 would have "No Effect" on Whooping crane, Piping plover, and Rufa red knot.
These species were shown to not have suitable habitat within or around the project area. The
USFWS will need to issue a consistency determination letter for these species on "20 November
2024", confirming the "No Effect" determination (Need to Consult). A "no effect" determination
was also made for alligator snapping turtle and Monarch butterfly based on lack of suitable
habitat as described in Table A.
For tri-colored bat, a "May effect, not likely to adversely affect" determination was made due to
suitable habitat being present and the potential for species to occur near the project area. Since
the project involves the removal of approximately 9 acres of trees, the loss of habitat would be
minor, but would have the potential to impact any nesting individuals in the project area.
Guidance provided by the Texas Fish and Wildlife Ecological Services Office states that the
effect determination for the Northern long-eared bat can guide the effect determination for
Tricolored bat (TCB) but suggests conservation measures and best management practices
(BMPs) to minimize the impacts to the species. Those recommendations have also been
incorporated into the project for TCB and include: limiting tree removal and construction to the
18
winter months while bats are at their hibernacula, when possible, or outside the pupping season
((May 15—July 31) if work cannot be done during the winter months. Additionally, best
management practices such as checking trees for cavities that the bats could use for shelter
before removing them, and working with the local Fish and Wildlife office if any bats are
encountered will be utilized if work occurs outside the winter months. Consultation with the US
Fish and Wildlife Service is necessary.
Table x. Effect Determinations for Listed Species
Species Status Effect Determination
Mammals
Tricolored bat PE May effect, not likely to
adversely affect.
Birds
Whooping crane E No effect
Piping lover T No effect
Rufa red knot T No effect
Reptiles
Alligator snapping turtle PT No effect
Insects
Monarch butterfly C No effect
4.2.9.2 Alternative 3 Detention Basin and Channel Improvements
Effects to Threatened and Endangered species under Alternative 3 would be like those
mentioned in section 4.2.9.1.
4.2.9.3 Alternative 5 Detention Basin and Bridge Culvert Modifications
Effects to Threatened and Endangered species under Alternative 5 would be like those
mentioned in section 4.2.9.1.
4.2.9.4 Alternative 8 Channel Improvements and Bridge Culvert Modifications
Based upon the analysis of each species described in Table A, USACE had determined that
Alternative 8 would have No effect for the tri-colored bat, Monarch butterfly, Whooping crane,
Piping plover, Rufa red knot, and Alligator snapping turtle, due to lack of habitat occurring in the
project area.
4.2.9.5 Alternative 17 Detention Basin, Bridge Culvert Modifications, Channel
Improvements
Effects to Threatened and Endangered species under Alternative 14 would be like those
mentioned in section 4.2.9.1.
4.2.10 Recreational Resources
Recreation Resources near the project area will temporarily be limited during construction
activities. These resources are expected to become available again once construction is
19
completed. No other impacts to Recreational Resources are expected to occur as a result of
each alternative.
4.2.11 Noise
Negligible effects from noise are expected for each alternative from heavy machinery during
construction. However, adjacent residential areas are expected to hear construction noises but
would not be of a decibel that would cause harm. Best management practices would be used to
reduce the effects of noise to the surrounding area.
4.2.12 Air Quality
Construction activities associated with each alternative are expected to have only short-term
impacts on local air quality. Such impacts would be primarily caused by increased emissions of
carbon monoxide, hydrocarbons, and nitrous oxides from vehicles entering and exiting the site
along with the operation of necessary equipment. Vehicle travel along unpaved road surfaces
and excavation of bare ground surfaces would create fugitive dust emissions. In addition to
fugitive dust, project construction activities would generate tailpipe emissions from mobile heavy
equipment and increased vehicular traffic. In a regional context, the daily equipment emissions
associated with project construction and O&M activities, even during maximum-intensity work
periods, would be minor and temporary. Impacts on air quality would not be significant.
4.2.13 Hazardous, Toxic, and Radioactive Waste (HTRW)
Based on the findings of the HTRW survey, the probability of encountering contaminated sites
or toxic substances without project construction is considered low. If construction will occur
more investigation may be necessary to determine the status and location of underground
storage tanks and other possible HTRW within the construction footprint.
4.2.14 Cultural Resources
4.2.15 Alternative 2 Detention Basin Alone
The proposed detention basin is located in the floodplain and mapped as Sanger-Urban land
complex. These soils typically mixed, poorly developed clayey soils that have been disturbed by
previous construction activities. The proposed detention basin has not been previously
investigated for cultural resources and there are no previously recorded cultural resources
identified within the footprint. Additionally, there are no standing structures or buildings within
the footprint. The project area is surrounded by residential houses that are all less than 50 years
20
old and will not be directly impacted. Due to the nature of the soils within the proposed detention
area, there is a low probability for intact cultural resources. The USACE has determined that
Alternative 2 will have no effect upon historic properties.
4.2.16 Alternative 3 Detention Basin and Channel Improvements
The proposed detention basin is located in the floodplain and mapped as Sanger-Urban land
complex. These soils typically mixed, poorly developed clayey soils that have been disturbed by
previous construction activities. The proposed detention basin has not been previously
investigated for cultural resources and there are no previously recorded cultural resources
identified within the footprint. There are no standing structures or buildings within the footprint.
The project area is surrounded by residential houses that are all less than 50 years old and will
not be directly impacted. Due to the nature of the soils within the proposed detention area, there
is a low probability for intact cultural resources. The channel of Cooper Creek has been
previously modified to stabilize the banks and therefore, there is a low probability to encounter
intact cultural resources. The USACE has determined that Alternative 3 will have no effect upon
historic properties.
4.2.17Alternative 5 Detention Basin and Bridge Culvert Modifications
Effects from the proposed detention basin under Alternative 5 would be like those mentioned in
section 4.2.12.1. This alternative proposes replacing the Sherman Road bridge and a concrete
culvert at Windsor Road where they cross Cooper Creek. The Sherman Road bridge was
originally constructed in 1921 and reconstructed in 1960 to expand the bridge to four traffic
lanes. The bridge is a reinforced concrete T-beam bridge and has not been evaluated for
eligibility for inclusion in the NRHP.
The Windsor Road culvert is a concrete culvert constructed in 1970 and under this alternative
would be expanded. The culvert has not been evaluated for eligibility for inclusion in the NRHP
and is not located within a historic district. However, the ACHP's Program Comment Issued for
Streamlining Section 106 Review for Actions Affecting Post-1945 Concrete and Steel Bridges
(Federal Register Volume 77, Number 222, pages 68790-68795) relieves the Federal Highway
Administration and other federal agencies of consideration of effects of undertakings on
common concrete and steel bridges and culverts constructed after 1945 as long as they aren't
in historic districts or previously determined eligible. The USACE has determined that there is a
potential to affect the Sherman Road bridge and that the bridge should be evaluated for NRHP
eligibility prior to construction.
4.2.18 Alternative 8 Channel Improvements and Bridge Culvert Modifications
Effects under Alternative 8 would be like those mentioned in sections 8.6.2 and 8.6.3.
4.2.19 Alternative 17 Detention Basin, Bridge Culvert Modifications, Channel
Improvements
Effects under Alternative 17 would be like those mentioned in sections 8.6.2 and 8.6.3.
4.2.20 Best Management Practices
Final project designs and specifications will use measures to avoid and minimize impacts to
natural and cultural resources. The following is a list of measures that may be used to mitigate
impacts to natural and cultural resources from construction activities:
21
• Construction Site Planning and Management including
• Stormwater Pollution Prevention Plans
• Noise controls and set construction times of operations
• Erosion, Runoff and Sediment Controls
• Good Housekeeping and Materials Management
• Higher Tiered heavy equipment use
• Project equipment and vehicles transiting between the either the
staging/laydown areas or to the construction/restoration sites will be
minimized to the extent practicable, including but not limited to using
designated routes and confining vehicle access to the immediate needs of
the project.
• An endangered species protection plan will identify personnel from contractor
staff who will act as the single point of contact responsible for daily
communicating and reporting endangered species issues throughout the
construction period to the USACE biologist and contracting officer
representative/lead engineer.
• Construction boundaries will be clearly marked both with biodegradable
flagging and within CADD drawings of awarded contract(s).
• Use of construction lighting at night shall be directed toward the construction
activity area and shielded from view outside of the action area to the
maximum extent practicable.
4.2.21 Cumulative Effects
The alternatives listed are a single and complete effort to reduce flood risk along Cooper Creek,
no future impacts are expected. The completion of this project would not increase the likelihood
of additional projects, infrastructure, or development within the area.
22
Literature Cited
Butler D.R., Ecoregions of Texas 2022. https://texasalmanac.com/topics/environment/physical-
regions-texas Accessed July 3, 2024.
Environmental Protection Agency (EPA) 2024. Texas Nonattainment/Maintenance Status for
Each County by Year for All Criteria Pollutants.
https://www3.epa.gov/airquality/greenbook/anayo_tx.html
Federal Emergency Management Agency (FEMA) 2023. FEMA's National Flood Hazard Layer
Viewer. https://www.fema.gov/flood-maps/national-flood-hazard-layer.
Natural Resources Conservation Service (NRCS). 2024. SSURGO (Soil Survey Geographic
Database) for Denton County, Texas, Natural Resources Conservation Service, U.S.
Dept. of Agriculture. http://soildatamart.nres.usda.gov/. Accessed July 24, 2024.
Runkle, J., K.E. Kunkel, S.M. Champion, B.C. Stewart, D.R. Easterling, J. Nielsen-Gammon,
2022: Texas State Climate Summary 2022. NOAA Technical Report NESDIS 150-TX.
Soil Survey Staff, Natural Resources Conservation Service, United States Department of
Agriculture. Web Soil Survey. Available online at https://websoilsurvey.nres.usda.gov/.
Accessed [July/24/2024].
Texas Commission on Environmental Quality (TCEQ). 2024. 2024 Draft Texas Integrated
Report of Surface Water Quality for Clean Water Act Sections 305(b) and 303 (d).
Texas Parks and Wildlife Department -A. 2024. Texas Ecoregions.
https://tpwd.texas.gov/education/hunter-education/online-course/wildlife-
conservation/texas-ecoregions
Texas Water Development Board (TWDB), 2024. Trinity River Basin.
https://www.twdb.texas.gov/surfacewater/rivers/river basins/trinity/index.asp
United States Census Bureau. "PROFILE OF GENERAL POPULATION AND HOUSING
CHARACTERISTICS."
https://www.census.gov/quickfacts/fact/table/dentoncitytexas/HSG010223#qf-flag-X.
Accessed on July 24, 2024.
United States Climate Data, Denton, Texas 2024.
https://www.usclimatedata.com/climate/denton/texas/united-states/ustx0353 Accessed
July 3, 2024.
United States Environmental Protection Agency (EPA). 1974. Information on Levels of
Environmental Noise Requisite to Protect Public Health and Welfare with an Adequate
Margin of Safety. EPA 550/9-74-004.
United States Fish and Wildlife Service (USFWS). 2024. Information for Planning and
Consultation tool. https://ipac.ecosphere.fws.gov
United States Fish and Wildlife Service (USFWS) 2023. "Monarch (Danaus plexippus) Species
Status Assessment Report." V2.1 96 pp + appendices.
23
United States Geological Survey, Geologic Atlas of Texas 2024.
https://webapps.usgs.gov/txgeology/Accessed July 3, 2024.
24
�t� NT Or r
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United States Department of the Interior /
FISH AND WILDLIFE SERVICE '
'RCM:i � Arlington Ecological Services Field Office �
17629 El Camino Real, Suite 211
Houston,TX 77058-3051
Phone: (817)277-1100 Fax: (817)277-1129
Email Address: arles(@fws.gov
In Reply Refer To: 11/20/2024 21:15:29 UTC
Project code: 2025-0022435
Project Name: Cooper Creek CAP
Subject: Consistency letter for 'Cooper Creek CAP' for specified federally threatened and
endangered species and designated critical habitat that may occur in your proposed
project area consistent with the Arlington Ecological Services Field Office (ESFO)
Determination Key(DKey) for project review and guidance for federally listed
species.
Dear Brandon Ford Ford:
The U.S. Fish and Wildlife Service (Service) received on November 20, 2024 your effects
determination for the 'Cooper Creek CAP' (the Action) using the Arlington ESFO DKey for
project review and guidance for federally-listed species within the Information for Planning and
Consultation(IPaC) system. The Service developed this system in accordance with the
Endangered Species Act of 1973 (ESA) (87 Stat. 884, as amended; 16 U.S.C. 1531 et seq.).
Based on your answers and the assistance of the Service's Arlington ESFO DKey, you
determined the proposed Action will have "No Effect" on the following species:
Species Listing Status Determination
Piping Plover (Charadrius melodus) Threatened No effect
Rufa Red Knot (Calidris canutus ru fa) Threatened No effect
Whooping Crane (Grus americana) Endangered No effect
Consultation Status
Thank you for informing the Service of your "No Effect" determinations for this project. No
further consultation/coordination for this project is required for these species.
This letter only covers the listed species in the above table. The following species may also occur
in the Action area:
■ Alligator Snapping Turtle Macrochelys temminckii Proposed Threatened
Project code: 2025-0022435 IPaC Record Locator: 333-153033255 11/20/2024 21:15:29 UTC
■ Monarch Butterfly Danaus plexippus Candidate
■ Tricolored Bat Perimyotis sub flavus Proposed Endangered
If you determine your project may affect additional listed or proposed listed species not covered
by the Arlington ESFO DKey, please contact our office at(817) 277-1100 or your Service point
of contact in the Arlington ESFO to discuss methods to avoid or minimize potential adverse
effects to those species. Candidate species are not afforded protection under the ESA; however,
we recommend they be considered in project planning and that conservation measures be
implemented to avoid or minimize impacts to individuals or their habitat as much as possible.
The Service recommends that your agency contact the Arlington ESFO or re-evaluate the Action
in IPaC if: 1) the scope, timing, duration, or location of the Action changes, 2) new information
reveals the Action may affect listed species or designated critical habitat, or 3) a new species is
listed or critical habitat designated. If any of the above conditions occurs, additional consultation
with the Arlington ESFO should take place before project changes are final or resources
committed.
At Risk Species: The Service's responsibilities under the ESA include evaluating species that
have been petitioned to be listed or are candidates for listing under the ESA. These "at risk"
species are not afforded protection under the ESA; however, we continue to collect information
on their status and potential threats in order to assess their biological status and address
requirements under the ESA. For these reasons, we request any information on the status of these
species (e.g., surveys) be provided to the Arlington ESFO for consideration. This may also
include any conservation measures implemented to avoid or reduce impacts to these species as a
result of proposed actions. The proposed project falls within the range of the following at risk
species:
Western chicken turtle (https:Hecos.fws.gov/ecp/species/9903)
Bald and Golden Eagle Protection Act(BGEPA): The following resources are provided to
project proponents and consulting agencies as additional information. Bald and golden eagles are
not included in this section 7(a)(2) consultation and this information does not constitute a
determination of effects by the Service.
The Service developed the National Bald Eagle Management Guidelines to advise landowners,
land managers, and others who share public and private lands with bald eagles when and under
what circumstances the protective provisions of the BGEPA may apply to their activities. The
guidelines should be consulted prior to conducting new or intermittent activity near an eagle nest.
This document may be downloaded from the following site: https://www.fws.gov/media/
national-bald-eagle-management-guidelines-0
If the recommendations detailed in the National Bald Eagle Management Guidelines cannot be
followed, you may apply for a permit to authorize removal or relocation of an eagle nest in
certain instances. The application form is located at https:Hfwsepermits.servicenowservices.com/
fws/.
DKey Version Publish Date:04/18/2024 2 of 7
Project code: 2025-0022435 IPaC Record Locator: 333-153033255 11/20/2024 21:15:29 UTC
Please note this guidance does not authorize bird mortality for species that are protected under
the Migratory Bird Treaty Act of 1918, as amended (16 U.S.C. sec. 703-712). If you believe
migratory birds will be affected by this activity, we recommend you contact our Migratory Bird
Permit Office at P.O. Box 709,Albuquerque, NM 87103, (505) 248-7882.
DKey Version Publish Date:04/18/2024 3 of 7
Project code: 2025-0022435 IPaC Record Locator: 333-153033255 11/20/2024 21:15:29 UTC
Action Description
You provided to IPaC the following name and description for the subject Action.
1. Name
Cooper Creek CAP
2. Description
The following description was provided for the project 'Cooper Creek CAP':
Flood risk reduction
The approximate location of the project can be viewed in Google Maps: https://
www.google.com/maps/033. ,-97. ,14z
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DKey Version Publish Date:04/18/2024 4 of 7
Project code: 2025-0022435 IPaC Record Locator: 333-153033255 11/20/2024 21:15:29 UTC
QUALIFICATION INTERVIEW
1. Does the proposed project involve research or other actions that include the collection,
capture, handling, or harassment of any individual federally listed threatened, endangered
or proposed species?
No
2. Does the proposed project involve the use of manned or unmanned aircraft (e.g., airplanes,
helicopters, drones, balloons)?
No
3. Is the action authorized, funded, or being carried out by a Federal agency?
Yes
4. Are you the Federal agency or designated non-federal representative?
Yes
5. Is the project a communications tower licensed or regulated by the Federal
Communications Commission?
No
6. Is the lead federal agency for the project Housing and Urban Development?
No
7. Is this a wind energy project ?
No
8. Is this a solar energy project ?
No
9. [Semantic] Does the project intersect the piping plover AOI?
Automatically answered
Yes
10. [Semantic] Does the project intersect the red knotAOI?
Automatically answered
Yes
11. [Semantic] Does the project intersect the peppered chub critical habitat?
Automatically answered
No
12. [Semantic] Does the project intersect the whooping crane AOI?
Automatically answered
Yes
DKey Version Publish Date:04/18/2024 5 of 7
Project code: 2025-0022435 IPaC Record Locator: 333-153033255 11/20/2024 21:15:29 UTC
13. Does the action area have habitat that may be used by whooping cranes during spring and
fall migrations (Mar 19-Apr 30, Oct 20—Nov 24)?
Note:Whooping crane habitat includes croplands and grasslands interspersed with wetlands such as lakes,ponds
and rivers.The portion of water bodies used by whooping cranes tend to be shallow(up to 20 inches in depth).
More information on stopover habitat can be found here:htWs://pubs.er.usgs.gov/publication/70202378.
No
14. [Semantic] Does the project intersect the sharpnose shiner critical habitat?
Automatically answered
No
15. [Semantic] Does the project intersect the smalleye shiner critical habitat?
Automatically answered
No
16. [Semantic] Does the project intersect the black-capped vireo range?
Automatically answered
No
17. [Semantic] Does the project intersect the Texas screwstem range?
Automatically answered
No
18. [Semantic] Does the project intersect the western chicken turtle range?
Automatically answered
Yes
19. [Semantic] Does the project intersect the Kisatchie painted crayfish range?
Automatically answered
No
20. Do you have additional supporting documents you would like to upload to support your
project review(e.g., Biological Evaluation, Habitat Assessment, Environmental Report,
photos, maps, etc.)?
No
DKey Version Publish Date:04/18/2024 6 of 7
Project code: 2025-0022435 IPaC Record Locator: 333-153033255 11/20/2024 21:15:29 UTC
IPAC USER CONTACT INFORMATION
Agency: Army Corps of Engineers
Name: Brandon Ford Ford
Address: 2000 Fort Point Road
City: Galveston
State: TX
Zip: 77550
Email christopher.b.ford@usace.army.mil
Phone: 4097663079
DKey Version Publish Date:04/18/2024 7 of 7
�t� NT Or r
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United States Department of the Interior /
FISH AND WILDLIFE SERVICE '
'RCM:i � Arlington Ecological Services Field Office �
17629 El Camino Real, Suite 211
Houston,TX 77058-3051
Phone: (817)277-1100 Fax: (817)277-1129
Email Address: arles(@fws.gov
In Reply Refer To: 11/20/2024 21:31:43 UTC
Project code: 2025-0022435
Project Name: Cooper Creek CAP
Federal Nexus: yes
Federal Action Agency (if applicable): Army Corps of Engineers
Subject: Technical assistance for 'Cooper Creek CAP'
Dear Brandon Ford Ford:
This letter records your determination using the Information for Planning and Consultation
(IPaC) system provided to the U.S. Fish and Wildlife Service (Service) on November 20, 2024,
for'Cooper Creek CAP' (here forward, Project). This project has been assigned Project Code
2025-0022435 and all future correspondence should clearly reference this number. Please
carefully review this letter.Your Endangered Species Act (Act) requirements are not
complete.
Ensuring Accurate Determinations When Using IPaC
The Service developed the IPaC system and associated species' determination keys in accordance
with the Endangered Species Act of 1973 (ESA; 87 Stat. 884, as amended; 16 U.S.C. 1531 et
seq.) and based on a standing analysis.All information submitted by the Project proponent into
IPaC must accurately represent the full scope and details of the Project. Failure to accurately
represent or implement the Project as detailed in IPaC or the Northern Long-eared Bat
and Tricolored Bat Range-wide Determination Key (Dkey), invalidates this letter.
Determination for the Northern Long-Eared Bat and Tricolored Bat
Based on your IPaC submission and a standing analysis completed by the Service, you
determined the proposed Project will have the following effect determinations:
Species Listing Status Determination
Tricolored Bat (Perimyotis sub flavus) Proposed May affect
Endangered
Other Species and Critical Habitat that May be Present in the Action Area
Project code: 2025-0022435 IPaC Record Locator: 333-153035270 11/20/2024 21:31:43 UTC
The IPaC-assisted determination key for the northern long-eared bat and tricolored bat does not
apply to the following ESA-protected species and/or critical habitat that also may occur in your
Action area:
■ Alligator Snapping Turtle Macrochelys temminckii Proposed Threatened
■ Monarch Butterfly Danaus plexippus Candidate
■ Piping Plover Charadrius melodus Threatened
• Rufa Red Knot Calidris canutus rufa Threatened
■ Whooping Crane Grus americana Endangered
You may coordinate with our Office to determine whether the Action may cause prohibited take
of the species listed above.
Conclusion
Consultation with the Service is not complete. Further consultation or coordination with the
Service is necessary for those species or designated critical habitats with a determination of
"May Affect."A"May Affect" determination in this key indicates that the project, as entered, is
not consistent with the questions in the key. Not all projects that reach a "May Affect"
determination are anticipated to result in adverse impacts to listed species. These projects may
result in a "No Effect", "May Affect, Not Likely to Adversely Affect", or "May Affect, Likely to
Adversely Affect" determination depending on the details of the project. Please contact our
Arlington Ecological Services Field Office to discuss methods to avoid or minimize potential
adverse effects to those species or designated critical habitats.
Federal agencies must consult with U.S. Fish and Wildlife Service under section 7(a)(2) of the
Endangered Species Act (ESA) when an action may affect a listed species. Tricolored bat is
proposed for listing as endangered under the ESA, but not yet listed. For actions that may affect a
proposed species, agencies cannot consult, but they can confer under the authority of section 7(a)
(4) of the ESA. Such conferences can follow the procedures for a consultation and be adopted as
such if and when the proposed species is listed. Should the tricolored bat be listed, agencies must
review projects that are not yet complete, or projects with ongoing effects within the tricolored
bat range that previously received a NE or NLAA determination from the key to confirm that the
determination is still accurate. Projects that receive a may affect determination for tricolored bat
through the key, should contact the appropriate Ecological Services Field Office if they want to
conference on this species.
DKey Version Publish Date: 11/07/2024 2 of 11
Project code: 2025-0022435 IPaC Record Locator: 333-153035270 11/20/2024 21:31:43 UTC
Action Description
You provided to IPaC the following name and description for the subject Action.
1. Name
Cooper Creek CAP
2. Description
The following description was provided for the project 'Cooper Creek CAP':
Flood risk reduction
The approximate location of the project can be viewed in Google Maps: https://
www.google.com/maps/033. ,-97. ,14z
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DETERMINATION KEY RESULT
Based on the answers provided, the proposed Action is consistent with a determination of "may
affect" for a least one species covered by this determination key.
QUALIFICATION INTERVIEW
1. Does the proposed project include, or is it reasonably certain to cause, intentional take of
listed bats or any other listed species?
Note: Intentional take is defined as take that is the intended result of a project.Intentional take could refer to
research,direct species management,surveys,and/or studies that include intentional handling/encountering,
harassment,collection,or capturing of any individual of a federally listed threatened,endangered or proposed
species?
No
2. Is the action area wholly within Zone 2 of the year-round active area for northern long-
eared bat and/or tricolored bat?
Automatically answered
No
3. Does the action area intersect Zone 1 of the year-round active area for northern long-eared
bat and/or tricolored bat?
Automatically answered
No
4. Does any component of the action involve leasing, construction or operation of wind
turbines?Answer'yes' if the activities considered are conducted with the intention of
gathering survey information to inform the leasing, construction, or operation of wind
turbines.
Note: For federal actions,answer`yes'if the construction or operation of wind power facilities is either(1)part
of the federal action or(2)would not occur but for a federal agency action(federal permit,funding,etc.).
No
5. Is the proposed action authorized, permitted, licensed, funded, or being carried out by a
Federal agency in whole or in part?
Yes
6. Is the Federal Highway Administration (FHWA), Federal Railroad Administration (FRA),
or Federal Transit Administration (FTA) funding or authorizing the proposed action, in
whole or in part?
No
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7. Are you an employee of the federal action agency or have you been officially designated in
writing by the agency as its designated non-federal representative for the purposes of
Endangered Species Act Section 7 informal consultation per 50 CFR § 402.08?
Note:This key may be used for federal actions and for non-federal actions to facilitate section 7 consultation and
to help determine whether an incidental take permit may be needed,respectively.This question is for information
purposes only.
Yes
8. Is the lead federal action agency the Environmental Protection Agency(EPA) or Federal
Communications Commission (FCC)? Is the Environmental Protection Agency (EPA) or
Federal Communications Commission (FCC) funding or authorizing the proposed action,
in whole or in part?
No
9. Is the lead federal action agency the Federal Energy Regulatory Commission (FERC)?
No
10. [Semantic] Is the action area located within 0.5 miles of a known bat hibernaculum?
Note:The map queried for this question contains proprietary information and cannot be displayed.If you need
additional information,please contact your State wildlife agency.
Automatically answered
No
11. Does the action area contain any winter roosts or caves (or associated sinkholes, fissures,
or other karst features), mines, rocky outcroppings, or tunnels that could provide habitat
for hibernating bats?
No
12. Will the action cause effects to a bridge?
Note: Covered bridges should be considered as bridges in this question.
No
13. Will the action result in effects to a culvert or tunnel at any time of year?
No
14. Are trees present within 1000 feet of the action area?
Note:If there are trees within the action area that are of a sufficient size to be potential roosts for bats answer
"Yes".If unsure,additional information defining suitable summer habitat for the northern long-eared bat and
tricolored bat can be found in Appendix A of the USFWS'Range-wide Indiana Bat and Northern long-eared bat
Survey Guidelines at:https://www.fws.gov/media/range-wide-indiana-bat-and-northern-long-eared-bat-survey_
guidelines.
Yes
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15. Does the action include the intentional exclusion of bats from a building or structure?
Note:Exclusion is conducted to deny bats'entry or reentry into a building.To be effective and to avoid harming
bats,it should be done according to established standards.If your action includes bat exclusion and you are
unsure whether northern long-eared bats or tricolored bats are present,answer"Yes."Answer"No"if there are no
signs of bat use in the building/structure.If unsure,contact your local Ecological Services Field Office to help
assess whether northern long-eared bats or tricolored bats may be present.Contact a Nuisance Wildlife Control
Operator(NWCO)for help in how to exclude bats from a structure safely without causing harm to the bats(to
find a NWCO certified in bat standards,search the Internet using the search term"National Wildlife Control
Operators Association bats").Also see the White-Nose Syndrome Response Team's guide for bat control in
structures.
No
16. Does the action involve removal, modification, or maintenance of a human-made structure
(barn, house, or other building) known or suspected to contain roosting bats?
No
17. Will the action cause construction of one or more new roads open to the public?
For federal actions, answer `yes'when the construction or operation of these facilities is
either (1) part of the federal action or(2)would not occur but for an action taken by a
federal agency (federal permit, funding, etc.).
No
18. Will the action include or cause any construction or other activity that is reasonably certain
to increase average daily traffic permanently or temporarily on one or more existing roads?
Note: For federal actions,answer`yes'when the construction or operation of these facilities is either(1)part of
the federal action or(2)would not occur but for an action taken by a federal agency(federal permit,funding,
etc.). .
No
19. Will the action include or cause any construction or other activity that is reasonably certain
to increase the number of travel lanes on an existing thoroughfare?
For federal actions, answer `yes'when the construction or operation of these facilities is
either (1) part of the federal action or (2) would not occur but for an action taken by a
federal agency (federal permit, funding, etc.).
No
20. Will the proposed Action involve the creation of a new water-borne contaminant source
(e.g., leachate pond, pits containing chemicals that are not NSF/ANSI 60 compliant)?
Note: For information regarding NSF/ANSI 60 please visit https://www.nsf.orWknowledge-library/nsf-ansi-
standard-60-drinking-water-treatment-chemicals-health-effects
No
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21. Will the proposed action involve the creation of a new point source discharge from a
facility other than a water treatment plant or storm water system?
No
22. Will the action include drilling or blasting?
No
23. Will the action involve military training (e.g., smoke operations, obscurant operations,
exploding munitions, artillery fire, range use, helicopter or fixed wing aircraft use)?
No
24. Will the proposed action involve the use of herbicides or other pesticides other than
herbicides (e.g., fungicides, insecticides, or rodenticides)?
No
25. Will the action include or cause activities that are reasonably certain to cause chronic or
intense nighttime noise (above current levels of ambient noise in the area) in suitable
summer habitat for the northern long-eared bat or tricolored bat during the active season?
Chronic noise is noise that is continuous or occurs repeatedly again and again for a long
time. Sources of chronic or intense noise that could cause adverse effects to bats may
include, but are not limited to: road traffic; trains; aircraft; industrial activities; gas
compressor stations; loud music; crowds; oil and gas extraction; construction; and mining.
Note:Additional information defining suitable summer habitat for the northern long-eared bat and tricolored bat
can be found in Appendix A of the USFWS'Range-wide Indiana Bat and Northern long-eared bat Survey
Guidelines at:htWs://www.fws.gov/media/range-wide-indiana-bat-and-northern-long-eared-bat-survey-
guidelines.
No
26. Does the action include, or is it reasonably certain to cause, the use of permanent or
temporary artificial lighting within 1000 feet of suitable northern long-eared bat or
tricolored bat roosting habitat?
Note:Additional information defining suitable summer habitat for the northern long-eared bat and tricolored bat
can be found in Appendix A of the USFWS'Range-wide Indiana Bat and Northern long-eared bat Survey
Guidelines at:https://www.fws.gov/media/range-wide-indiana-bat-and-northern-long-eared-bat-survey-
guidelines.
No
27. Will the action include tree cutting or other means of knocking down or bringing down
trees, tree topping, or tree trimming?
Yes
28. Will the proposed action occur exclusively in an already established and currently
maintained utility right-of-way?
Yes
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29. Will the proposed action result in the cutting of entire trees outside of the currently
maintained utility right-of-way?
Yes
30. Does the action include emergency cutting or trimming of hazard trees in order to remove
an imminent threat to human safety or property? See hazard tree note at the bottom of the
key for text that will be added to response letters
Note:A"hazard tree"is a tree that is an immediate threat to lives,public health and safety,or improved property.
No
31. Does the project intersect with the 0- 9.9% forest density category?
Automatically answered
Yes
32. Does the project intersect with the 10.0- 19.9% forest density category map?
Automatically answered
Yes
33. Does the project intersect with the 20.0- 29.9% forest density category map?
Automatically answered
No
34. Does the project intersect with the 30.0- 100% forest density category map?
Automatically answered
No
35. Will the action cause trees to be cut, knocked down, or otherwise brought down across an
area greater than 0.5 acre in total extent?
Yes
36. Does the action area intersect the tricolored bat species list area?
Automatically answered
Yes
37. [Semantic] Is the action area located within 0.25 miles of a culvert that is known to be
occupied by northern long-eared or tricolored bats?
Note:The map queried for this question contains proprietary information and cannot be displayed.If you need
additional information,please contact your State wildlife agency.
Automatically answered
No
38. Has a presence/probable absence bat survey targeting the tricolored bat and following the
Service's Range-wide Indiana Bat and Northern Long-Eared Bat Survey Guidelines been
conducted within the project area?
No
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39. Is suitable summer habitat for the tricolored bat present within 1000 feet of project
activities?
(If unsure, answer ""Yes."")
Note: If there are trees within the action area that may provide potential roosts for tricolored bats(e.g.,clusters of
leaves in live and dead deciduous trees, Spanish moss(Tillandsia usneoides),clusters of dead pine needles of
large live pines)answer""Yes.""For a complete definition of suitable summer habitat for the tricolored bat,
please see Appendix A in the Service's Range-wide Indiana Bat and Northern long-eared Bat Survey Guidelines.
Yes
40. Do you have any documents that you want to include with this submission?
No
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PROJECT QUESTIONNAIRE
Enter the extent of the action area (in acres) from which trees will be removed - round up
to the nearest tenth of an acre. For this question, include the entire area where tree removal
will take place, even if some live or dead trees will be left standing.
9.0
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IPAC USER CONTACT INFORMATION
Agency: Army Corps of Engineers
Name: Brandon Ford Ford
Address: 2000 Fort Point Road
City: Galveston
State: TX
Zip: 77550
Email christopher.b.ford@usace.army.mil
Phone: 4097663079
DKey Version Publish Date: 11/07/2024 11 of 11
�t� NT Or r
pP .i Fi �7�n•k'C
United States Department of the Interior /
FISH AND WILDLIFE SERVICE '
'RCM '" Arlington Ecological Services Field Office �
17629 El Camino Real, Suite 211
Houston,TX 77058-3051
Phone: (817)277-1100 Fax: (817)277-1129
Email Address: arles(@fws.gov
In Reply Refer To: 11/20/2024 21:12:14 UTC
Project Code: 2025-0022435
Project Name: Cooper Creek CAP
Subject: List of threatened and endangered species that may occur in your proposed project
location or may be affected by your proposed project
To Whom It May Concern:
Project code: 2025-0022435 11/20/2024 21:12:14 UTC
The enclosed species list identifies threatened, endangered, proposed, and candidate species, as
well as proposed and final designated critical habitat, which may occur within the boundary of
your proposed project. The species list fulfills the requirements of the U.S. Fish and Wildlife
Service (Service) under section 7(c) of the Endangered Species Act(Act) of 1973, as amended
(16 U.S.C. 1531 et seq.).
The purpose of the Act is to provide a means whereby threatened and endangered species and the
ecosystems upon which they depend may be conserved. Under section 7(a)(1) of the Act, Federal
agencies are directed to utilize their authorities to carry out programs for the conservation of
threatened and endangered species. Under and 7(a)(2) and its implementing regulations (50
CFR 402 et seq.), Federal agencies are required to determine whether their actions may affect
threatened and endangered species and/or designated critical habitat. A Federal action is an
activity or program authorized, funded, or carried out, in whole or in part, by a Federal agency
(50 CFR 402.02).
A Biological Assessment is required for construction projects (or other undertakings having
similar physical impacts) that are major Federal actions significantly affecting the quality of the
human environment as defined in the National Environmental Policy Act (42 U.S.C. 4332(2)
(c)). For Federal actions other than major construction activities, the Service suggests that a
biological evaluation (similar to a Biological Assessment)be prepared to determine whether the
project may affect listed or proposed species and/or designated or proposed critical habitat.
Recommended contents of a Biological Assessment are described at 50 CFR 402.12.
After evaluating the potential effects of a proposed action on federally listed species, one of the
following determinations should be made by the Federal agency:
1. No effect-the appropriate determination when a project, as proposed, is anticipated to
have no effects to listed species or critical habitat. A"no effect" determination does not
require section 7 consultation and no coordination or contact with the Service is necessary.
However, the action agency should maintain a complete record of their evaluation,
including the steps leading to the determination of affect, the qualified personnel
conducting the evaluation, habitat conditions, site photographs, and any other related
information.
2. May affect, but is not likely to adversely affect-the appropriate determination when a
proposed action's anticipated effects to listed species or critical habitat are insignificant,
discountable, or completely beneficial. Insignificant effects relate to the size of the impact
and should never reach the scale where "take" of a listed species occurs. Discountable
effects are those extremely unlikely to occur. Based on best judgment, a person would not
be able to meaningfully measure, detect, or evaluate insignificant effects, or expect
discountable effects to occur. This determination requires written concurrence from the
Service. A biological evaluation or other supporting information justifying this
determination should be submitted with a request for written concurrence.
3. May affect, is likely to adversely affect-the appropriate determination if any adverse effect
to listed species or critical habitat may occur as a consequence of the proposed action, and
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the effect is not discountable or insignificant. This determination requires formal section 7
consultation.
The Service has performed up-front analysis for certain project types and species in your project
area. These analyses have been compiled into determination keys, which allows an action agency,
or its designated non-federal representative, to initiate a streamlined process for determining a
proposed project's potential effects on federally listed species. The determination keys can be
accessed through IPaC.
The Service recommends that candidate species, proposed species, and proposed critical habitat
be addressed should consultation be necessary. More information on the regulations and
procedures for section 7 consultation, including the role of permit or license applicants, can be
found at: https://www.fws.gov/service/section-7-consultations
New information based on updated surveys, changes in the abundance and distribution of
species, changed habitat conditions, or other factors could change this list. Please feel free to
contact us if you need more current information or assistance regarding the potential impacts to
federally proposed, listed, and candidate species and federally designated and proposed critical
habitat. Please note that under 50 CFR 402.12(e) of the regulations implementing section 7 of the
Act, the accuracy of this species list should be verified after 90 days. This verification can be
completed formally or informally as desired. The Service recommends that verification be
completed by visiting the IPaC website at regular intervals during project planning and
implementation for updates to species lists and information.An updated list may be requested
through the IPaC system by completing the same process used to receive the enclosed list.
Please be aware that bald and golden eagles are protected under the Bald and Golden Eagle
Protection Act(16 U.S.C. 668 et seq.), and projects affecting these species may require
development of an eagle conservation plan (https://www.fws.gov/library/collections/bald-and-
golden-eagle-management). Additionally, wind energy projects should follow the wind energy
guidelines (https://www.fws.gov/media/land-based-wind-energy-guidelines) for minimizing
impacts to migratory birds and bats.
Guidance for minimizing impacts to migratory birds for projects including communications
towers (e.g., cellular, digital television, radio, and emergency broadcast) can be found at: https://
www.fws.gov/media/recommended-best-practices-communication-tower-design-siting-
construction-operation. The Federal Aviation Administration (FAA) released specifications for
and made mandatory flashing L-810 lights on new towers 150-350 feet AGL, and the elimination
of L-810 steady-burning side lights on towers above 350 feet AGL. While the FAA made these
changes to reduce the number of migratory bird collisions (by as much as 70%), extinguishing
steady-burning side lights also reduces maintenance costs to tower owners. For additional
information concerning migratory birds and eagle conservation plans, please contact the
Service's Migratory Bird Office at 505-248-7882.
We appreciate your concern for threatened and endangered species. The Service encourages
Federal agencies to include conservation of threatened and endangered species into their project
planning to further the purposes of the Act. Please include the Consultation Tracking Number in
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the header of this letter with any request for consultation or correspondence about your project
that you submit to our office.
Attachment(s):
■ Official Species List
■ USFWS National Wildlife Refuges and Fish Hatcheries
• Bald& Golden Eagles
■ Migratory Birds
• Wetlands
OFFICIAL SPECIES LIST
This list is provided pursuant to Section 7 of the Endangered Species Act, and fulfills the
requirement for Federal agencies to "request of the Secretary of the Interior information whether
any species which is listed or proposed to be listed may be present in the area of a proposed
action".
This species list is provided by:
Arlington Ecological Services Field Office
17629 El Camino Real, Suite 211
Houston, TX 77058-3051
(817) 277-1100
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PROJECT SUMMARY
Project Code: 2025-0022435
Project Name: Cooper Creek CAP
Project Type: Flooding
Project Description: Flood risk reduction
Project Location:
The approximate location of the project can be viewed in Google Maps: https://
www.google.com/maps/033. ,-97. ,14z
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Counties: Denton County, Texas
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ENDANGERED SPECIES ACT SPECIES
There is a total of 6 threatened, endangered, or candidate species on this species list.
Species on this list should be considered in an effects analysis for your project and could include
species that exist in another geographic area. For example, certain fish may appear on the species
list because a project could affect downstream species. Note that 2 of these species should be
considered only under certain conditions.
IPaC does not display listed species or critical habitats under the sole jurisdiction of NOAA
Fisheriesl, as USFWS does not have the authority to speak on behalf of NOAA and the
Department of Commerce.
See the "Critical habitats" section below for those critical habitats that lie wholly or partially
within your project area under this office's jurisdiction. Please contact the designated FWS office
if you have questions.
1. NOAA Fisheries, also known as the National Marine Fisheries Service (NMFS), is an
office of the National Oceanic and Atmospheric Administration within the Department of
Commerce.
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MAMMALS
NAME STATUS
Tricolored Bat Perimyotis sub flavus Proposed
No critical habitat has been designated for this species. Endangered
Species profile:https:Hecos.fws.gov/ecp/sl2ecies/10515
BIRDS
NAME STATUS
Piping Plover Charadrius melodus Threatened
Population: [Atlantic Coast and Northern Great Plains populations]-Wherever found,except
those areas where listed as endangered.
There is final critical habitat for this species.Your location does not overlap the critical habitat.
This species only needs to be considered under the following conditions:
• Wind Energy Projects
Species profile:https:Hecos.fws.gov/ecp/species/6039
Rufa Red Knot Calidris canutus ru fa Threatened
There is proposed critical habitat for this species.Your location does not overlap the critical
habitat.
This species only needs to be considered under the following conditions:
■ Wind Energy Projects
Species profile:https://ecos.fws.gov/ecp/species/1864
Whooping Crane Grus americana Endangered
Population:Wherever found,except where listed as an experimental population
There is final critical habitat for this species.Your location does not overlap the critical habitat.
Species profile:https:Hecos.fws.gov/ecp/species/758
REPTILES
NAME STATUS
Alligator Snapping Turtle Macrochelys temminckii Proposed
No critical habitat has been designated for this species. Threatened
Species profile:https:Hecos.fws.gov/ecp/species/4658
INSECTS
NAME STATUS
Monarch Butterfly Danaus plexippus Candidate
No critical habitat has been designated for this species.
Species profile:https:Hecos.fws.gov/ecp/species/9743
CRITICAL HABITATS
THERE ARE NO CRITICAL HABITATS WITHIN YOUR PROJECT AREA UNDER THIS OFFICE'S
JURISDICTION.
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YOU ARE STILL REQUIRED TO DETERMINE IF YOUR PROJECT(S)MAY HAVE EFFECTS ON ALL
ABOVE LISTED SPECIES.
USFWS NATIONAL WILDLIFE REFUGE LANDS
AND FISH HATCHERIES
Any activity proposed on lands managed by the National Wildlife Refuge system must undergo a
'Compatibility Determination' conducted by the Refuge. Please contact the individual Refuges to
discuss any questions or concerns.
THERE ARE NO REFUGE LANDS OR FISH HATCHERIES WITHIN YOUR PROJECT AREA.
BALD & GOLDEN EAGLES
Bald and golden eagles are protected under the Bald and Golden Eagle Protection Act and the
Migratory Bird Treaty Act2.
Any person or organization who plans or conducts activities that may result in impacts to bald or
golden eagles, or their habitats3, should follow appropriate regulations and consider
implementing appropriate conservation measures, as described in the links below. Specifically,
please review the "Supplemental Information on Migratory Birds and Eagles".
1. The Bald and Golden Eagle Protection Act of 1940.
2. The Migratory Birds Treated of 1918.
3. 50 C.F.R. Sec. 10.12 and 16 U.S.C. Sec. 668(a)
There are likely bald eagles present in your project area. For additional information on bald
eagles, refer to Bald Eagle Nesting and Sensitivity to Human Activity
For guidance on when to schedule activities or implement avoidance and minimization measures
to reduce impacts to migratory birds on your list, see the PROBABILITY OF PRESENCE
SUMMARY below to see when these birds are most likely to be present and breeding in your
project area.
NAME BREEDING SEASON
Bald Eagle Haliaeetus leucocephalus Breeds Sep 1 to
This is not a Bird of Conservation Concern(BCC)in this area,but warrants attention Jul 31
because of the Eagle Act or for potential susceptibilities in offshore areas from certain
types of development or activities.
https://ecos.fws.gov/ecp/species/1626
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PROBABILITY OF PRESENCE SUMMARY
The graphs below provide our best understanding of when birds of concern are most likely to be
present in your project area. This information can be used to tailor and schedule your project
activities to avoid or minimize impacts to birds. Please make sure you read "Supplemental
Information on Migratory Birds and Eagles", specifically the FAQ section titled "Proper
Interpretation and Use of Your Migratory Bird Report" before using or attempting to interpret
this report.
Probability of Presence (■)
Green bars; the bird's relative probability of presence in the 10km grid cell(s) your project
overlaps during that week of the year.
Breeding Season ( )
Yellow bars; liberal estimate of the timeframe inside which the bird breeds across its entire
range.
Survey Effort (1)
Vertical black lines; the number of surveys performed for that species in the 10km grid cell(s)
your project area overlaps.
No Data (—)
A week is marked as having no data if there were no survey events for that week.
■probability of presence breeding season I survey effort —no data
SPECIES JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC
Eagl
Non-BCCe 11ij ++++ ++++ ++++ ++++ ++ii iiii ++++ + �� iiii gill iill
Vulnerable
Additional information can be found using the following links:
■ Eagle Management https://www.fws.gov/program/eagle-management
• Measures for avoiding and minimizing impacts to birds https://www.fws.gov/library
collections/avoiding-and-minimizing-incidental-take-migratory
■ Nationwide conservation measures for birds https://www.fws.gov/sites/default/files/
documents/nationwide-standard-conservation-measures.pdf
■ Supplemental Information for Migratory Birds and Eagles in IPaC https://www.fws.gov/
media/supplemental-information-migratory-birds-and-bald-and-golden-eagles-may-occur-
project-action
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MIGRATORY BIRDS
Certain birds are protected under the Migratory Bird Treaty Act1 and the Bald and Golden Eagle
Protection Act2.
Any person or organization who plans or conducts activities that may result in impacts to
migratory birds, eagles, and their habitats3 should follow appropriate regulations and consider
implementing appropriate conservation measures, as described in the links below. Specifically,
please review the "Supplemental Information on Migratory Birds and Eagles".
1. The Migratory Birds Treaty Act of 1918.
2. The Bald and Golden Eagle Protection Act of 1940.
3. 50 C.F.R. Sec. 10.12 and 16 U.S.C. Sec. 668(a)
For guidance on when to schedule activities or implement avoidance and minimization measures
to reduce impacts to migratory birds on your list, see the PROBABILITY OF PRESENCE
SUMMARY below to see when these birds are most likely to be present and breeding in your
project area.
BREEDING
NAME SEASON
American Golden-plover Pluvialis dominica Breeds
This is a Bird of Conservation Concern(BCC)throughout its range in the continental USA elsewhere
and Alaska.
https:Hecos.fws.gov/ecp/species/10561
Bald Eagle Haliaeetus leucocephalus Breeds Sep 1 to
This is not a Bird of Conservation Concern(BCC)in this area,but warrants attention Jul 31
because of the Eagle Act or for potential susceptibilities in offshore areas from certain types
of development or activities.
https:Hecos.fws.gov/ecp/species/1626
Chimney Swift Chaetura pelagica Breeds Mar 15
This is a Bird of Conservation Concern(BCC)throughout its range in the continental USA to Aug 25
and Alaska.
https://ecos.fws.gov/ecp/species/9406
Least Tern Sternula antillarum antillarum Breeds Apr 25
This is a Bird of Conservation Concern(BCC)throughout its range in the continental USA to Sep 5
and Alaska.
https://ecos.fws.gov/ecp/species/11919
Lesser Yellowlegs Tringa flavipes Breeds
This is a Bird of Conservation Concern(BCC)throughout its range in the continental USA elsewhere
and Alaska.
https:Hecos.fws.gov/ecp/species/9679
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Project code: 2025-0022435 11/20/2024 21:12:14 UTC
BREEDING
NAME SEASON
Little Blue Heron Egretta caerulea Breeds Mar 10
This is a Bird of Conservation Concern(BCC)only in particular Bird Conservation Regions to Oct 15
(BCRs)in the continental USA
https://ecos.fws.gov/ecp/species/9477
Pectoral Sandpiper Calidris melanotos Breeds
This is a Bird of Conservation Concern(BCC)throughout its range in the continental USA elsewhere
and Alaska.
hlWs://ecos.fws.gov/ecp/species/9561
Prairie Loggerhead Shrike Lanius ludovicianus excubitorides Breeds Feb 1 to
This is a Bird of Conservation Concern(BCC)only in particular Bird Conservation Regions Jul 31
(BCRs)in the continental USA
htWs:Hecos.fws.gov/ecp/species/8833
Prothonotary Warbler Protonotaria citrea Breeds Apr 1 to
This is a Bird of Conservation Concern(BCC)throughout its range in the continental USA Jul 31
and Alaska.
htWs:Hecos.fws.gov/ecp/species/9439
Red-headed Woodpecker Melanerpes erythrocephalus Breeds May 10
This is a Bird of Conservation Concern(BCC)throughout its range in the continental USA to Sep 10
and Alaska.
https://ecos.fws.gov/ecp/species/9398
Sprague's Pipit Anthus spragueh Breeds
This is a Bird of Conservation Concern(BCC)throughout its range in the continental USA elsewhere
and Alaska.
https://ecos.fws.gov/ecp/species/8964
PROBABILITY OF PRESENCE SUMMARY
The graphs below provide our best understanding of when birds of concern are most likely to be
present in your project area. This information can be used to tailor and schedule your project
activities to avoid or minimize impacts to birds. Please make sure you read "Supplemental
Information on Migratory Birds and Eagles", specifically the FAQ section titled "Proper
Interpretation and Use of Your Migratory Bird Report" before using or attempting to interpret
this report.
Probability of Presence (■)
Green bars; the bird's relative probability of presence in the 10km grid cell(s) your project
overlaps during that week of the year.
Breeding Season ( )
Yellow bars; liberal estimate of the timeframe inside which the bird breeds across its entire
range.
Survey Effort (1)
11 of 14
Project code: 2025-0022435 11/20/2024 21:12:14 UTC
Vertical black lines; the number of surveys performed for that species in the 10km grid cell(s)
your project area overlaps.
No Data (—)
A week is marked as having no data if there were no survey events for that week.
■probability of presence breeding season I survey effort —no data
SPECIES JAN FEB MAR +APR MAY JUN JUL AUG SEP OCT NOV DEC
American Golden-
plove
r T++++ ++++ ++++ + I ++++ ++++ ++++ +++ ++++ ++++ ++++ ++++
BCC Rangewide
(CON)
Non-BCCe ++++ 111111+ ++++ $W 111�11111 ++++ +T++ N111 W 1111
Vulnerable A MEN
Chimney t
BCC Rang wlide ++++ ++++ +111 +111 g+1 +100 ,++' 1'++ +"' ++++ ++++ ++++
(CON) mmmmON mmmm minim 1h
Least Tern
BCC Rangewide ++++ ++++ ++++ +++I IN ... .... .... ....
(CON)
Lesser Yellowlegs BCC Rangewide ++++ ++++ ++++ ++++ ++++ ++++ ++++ ++++ ++++ ++++ ++I+ ++++
(CON)
++++ ++++ +M ie$i zs 170 i+1l ++ ��ii +++ ++++ ++++
Little Blue Heron +
BCC-BCR �
Pectoral Sandpiper BCC Rangewide ++++ ++++ ++++ ++++ ++++ ++++ ++++ ++++ +A. ++++ ++++ ++++
(CON) yy +■ y
Prairie Loggerhead
Shrike ++++ 0TI 1p ' I �� T+IF+ +1*' ++„ ,+++ ++++ +,++ ++++ ++++
BCC-BCR
Warblerotary ++++ ++++ ++++Prothon +++I +++ ++++ ++++ ++++
BCC Rangewide
(CON)
Red-headed ++++ ++++ ++++ +++i � ++++ ++++ ++++
Woodpecker
BCC Rangewide
(CON) +
Spr Pipit
BCCC Rangewide TT T T++++ ++++ ++++ +++1 1+++ ++++ ++++ ++++ ++++Ran
(CON)
12 of 14
Project code: 2025-0022435 11/20/2024 21:12:14 UTC
Additional information can be found using the following links:
• Eagle Management https://www.fws.gov/program/eagle-management
• Measures for avoiding and minimizing impacts to birds https://www.fws.gov/library
collections/avoiding-and-minimizing-incidental-take-migratory-birds
■ Nationwide conservation measures for birds https://www.fws.gov/sites/default/files/
documents/nationwide-standard-conservation-measures.pdf
■ Supplemental Information for Migratory Birds and Eagles in IPaC https://www.fws.gov/
media/supplemental-information-migratory-birds-and-bald-and-golden-ea les-may-occur-
project-action
WETLANDS
Impacts to NWI wetlands and other aquatic habitats may be subject to regulation under Section
404 of the Clean Water Act, or other State/Federal statutes.
For more information please contact the Regulatory Program of the local U.S.Army Corps of
Engineers District.
Please note that the NWI data being shown may be out of date. We are currently working to
update our NWI data set. We recommend you verify these results with a site visit to determine
the actual extent of wetlands on site.
RIVERINE
■ R4SBCx
FRESHWATER FORESTED/SHRUB WETLAND
■ PF01A
13 of 14
Project code: 2025-0022435 11/20/2024 21:12:14 UTC
IPAC USER CONTACT INFORMATION
Agency: Army Corps of Engineers
Name: Brandon Ford Ford
Address: 2000 Fort Point Road
City: Galveston
State: TX
Zip: 77550
Email christopher.b.ford@usace.army.mil
Phone: 4097663079
14 of 14
Appendix C : Economics
Cooper Creek, Denton, TX
Section 205
Closeout Report
February 2025
1
Contents
1.0 Introduction .............................................................................................................................3
2.0 Structure Inventory..................................................................................................................3
3.0 Economic Evaluation Methodology.........................................................................................5
4.0 Summary of Baseline Estimated Damages ............................................................................6
5.0 National Economic Development Analysis .............................................................................8
2
1 .0 Introduction
This appendix presents economic analysis for the Cooper Creek Study. The economics
component of the study included identifying structures in the floodplain along with relevant
characteristics such as building type, structure replacement value, structure content value, and
estimating flood damages under different frequency of flood events. Expected annual damages
were used to determine if project alternatives were economically justified using standard
National Economic Development (NED) metrics. NED analysis is a fundamental component of
planning studies, and the purpose is to determine whether a proposed project is a sound
investment for federal taxpayers. The study area is in Denton County, Texas in areas along
Cooper Creek. Denton is part of the Dallas Fort Worth Metropolitan Statistical Area, and has
population of about one million people.
2.0 Structure Inventory
The team's hydrologists and engineers developed a reasonable impact area based on a review
of past studies and other data (Figure 1). With the impact area boundaries, PDT economists
compiled a structure inventory based on surface water profiles and depth grids developed by
the hydrologist using HEC-RAS (both 1-dimensional and 2-dimensional geometries) for existing
conditions. Given that the impact area is "built out", meaning future expansion of developable
land is not likely, the future without project conditions are assumed to mirror the existing
conditions for economic analyses. The marked structures in Figure 1 comprise the structure
inventory and were selected using the 0.002 Annual Chance Exceedance (500-year event)
inundation area with a 500-foot buffer within the impact area.
Based on data from the USACE National Structure Inventory 2022 (NS122), the area prone to
flooding is primarily residential with 684 structures total. There are 654 residential structures that
are mostly (96 percent) one-story single-family detached homes and, of these, about 90 percent
rest on concrete slab foundations with first-floor elevations range approximately 0.5-to-2.0 feet
above grade. Most (98 percent) of structures have wooden exterior walls and none have
basements.
Flood impact analysis discussed in subsequent sections mostly affects residential structures.
Based on data from the NS122, structure market values (net of land value) range from about
$42,000 to $860,000 with an average and median of$188,000 and $190,000 respectively and a
standard deviation of$60,000 (Table 1). A review of 2024 Denton County appraisal records
show that these values are more or less accurate.'
Per USACE policy and guidance, structure monetary values used in the analysis must be based
on depreciated replacement value (DRV) as opposed to market value, which can fluctuate
considerably based on several factors such as broader national and local economic trends. To
estimate DRV for the structure inventory, the PDT relied on construction cost data published by
' A search map with appraisal values is available at: https://www.dentoncad.com/maps
3
RS Means maintained by USACE cost engineers. Specifically, economists applied construction
per square foot to arrive at a baseline replacement value and then applied depreciation factors
also published by RS Means to estimate DRV. Since NS122 values are in year 2022, RS Means
construction cost indices for the Dallas Fort Worth MSA were applied to estimate DRVs at 2024
price levels. Table 2 summarizes DRV estimates used to calculate NED benefits.
Figure 1
Study Impact Area and Structures (Denton County,Texas)
IS
•Vr . l , a t • � .
c
.♦ f
Table 1
Structure Values Reported in the USACE National Structure Inventory(2022)for the Cooper Creek Impact
Area
Damage Nan NSI Structure Standard Mnunum 1Vlaximum
Category Count Value Deviation
Residential 655 $122,916,000 $187,658 $69,665 $42,498 $859,241
Commercial 18 $4,457,000 $247,611 $184,014 $112,833 $990,609
Public 10 $1,896,000 1 $189,600 $23,930 1 $156,821 1 $225,840
Industrial 1 $226,000 $226,000 $0 $226,000 $226,000
4
Damage N1van NSI Structure Standard Minunum NlLximum
Category Count Value Deviation
Total 684 $129,495,000.0 $189,320 $75,047 $42,498 $990,609
Table 2
Estimated Depreciated Replacement Value for Structures in the Cooper Creek Impact Area
De
DamageStandard
Category Count Replacement Nban Deviation NMnimum Nhximum
Value
Residential 655 $86,364,000 $131,853 $63,087 $42,498 $786,948
Coninercial 18 $3,215,000 $178,611 $63,178 $89,437 $866,001
Public 10 $1,282,000 $128,200 $56,622 $98,222 $186,420
Industrial 1 $138,000 $138,000 $0 $138,000 $138,000
Total 684 $90,999,000 $133,039 $75,047 $38,614 $866,001
3.0 Economic Evaluation Methodology
The Flood Damage Reduction Analysis (HEC-FDA) software developed by the USACE
Hydrologic Engineering Center provides the capability to perform an integrated hydrologic
engineering and economic analysis during the formulation and evaluation of flood risk
management plans. HEC-FDA is designed to assist USACE study members in using risk
assessment procedures for formulating and evaluating flood risk management measures
pursuant to pertinent policy and guidance (EM 1110-2-1619, ER 1105-2-101). HEC-FDA is
USACE's only tool certified to support inland flood risk assessment recommendations and has
supported 49 chief's reports in the last 10 years in which HEC-FDA was used by USACE project
delivery teams to identify more than $5 billion in annual benefits that justified nearly $44 billion
in flood risk management investment recommendations.
USACE makes investment decisions for flood risk management projects using marginal
expected annual damages. Flood events have return intervals that are based on the probability
that such an event will occur in any single year over the recurrence interval. Total damages
(single event damages) ignore the probability (annual exceedance probability) and assume that
the flood happens and damages manifest. In contrast, expected annual damages are weighted
by the probability. For example, for a 10-year flood event (0.10 probability), total or single event
damages are weighted by 0.10. Intervals or marginal changes between events ensure there is
no double counting. Standard event frequencies included in an FDA model are the
2,5,10,25,50,100,250 and 500-year recurrence intervals.
Key inputs in FDA consist of hydrologic, design engineering, economic and project construction,
or implementation cost data. Hydrologists develop hydraulic inputs, flow frequency functions
and stage discharge functions for both existing and the future without project conditions along
with inundation data including geospatial mapping products. Economists focus on developing
5
structure inventories and parameters for NED analysis such as discount rates and converting
cost and benefits to annualized values. Lastly, design engineers conceptualize structural study
alternatives, and cost engineers provide construction or implementation cost estimates.
Once relevant inputs are collected and entered, FDA estimates changes in hydraulics resulting
from structural alternatives, and how changes affect flood impacts to structures in the study
area. Reduced damages are NED benefits, and these are compared to the financial costs of
different alternative formulations. Structural alternatives directly affect hydraulics in the study,
while non-structural alternatives do not, but can reduce damages such as changes to structures.
For example, purchasing properties to remove them from a floodplain, or elevating structures
are considered non-structural alternatives even thought they involve construction.
For the economic analysis, key assumptions for the economic evaluation: 1) costs and benefits
are annualized to a common reference point using a 50-year period of analysis and a discount
rate of 3.00 percent (approved value for fiscal year 2025), and 2) the future without project
condition is the same as existing conditions given that the study is fully developed and zoned
accordingly; thus, future expansion in the area is not possible. For FDA, depth damage
functions and content value ratios are from Engineering Guidance Memorandum 01-03.
4.0 Summary of Baseline Estimated Damages
To illustrate the extent of flooding, Figures 2 and 3 show flooding for the without project
condition for the 0.10 AEP (10-year) event and the 0.002 AEP event (500-year), and Table 3
displays single event damages (unweighted by probability) for the suite of flood events included
in an FDA analysis. At higher frequency events, depths relative to first floor structure elevations
and estimated damages are limited, while at lower frequencies, they are higher and at the
extreme (0.002 AEP) structure and content damages total $7.8 million. Total Expected Annual
Damage (EAD) across the range of modeled flood events is roughly $907,000.
Table 3
Single Event Flood Depths and Damages for Structures with Nbdeled Damages
(monetary values in$millions)
Annual Exceedance 0.5 AEP 0.2 AEP 0.1 AEP 0.04 AEP 0.02 AEP 0.01 AEP 0.005 AEP 0.002 AEP
Probability
Depth Relative to First Floor Elevations
Ntan 0.80) 0.40) (0.20) 0.06 0.24 0.41 0.52 0.64
Standard Deviation 0.00 0.64 0.68 0.69 0.72 0.73 0.79 0.86
Maximum 0.16 1.06 1.48 1.98 2.54 3.07 3.57 4.23
NEnimum 1.82 1.93 1.92 1.82 1.89 1.51 1.46 1.95
Single Event Damages ($millions)
Structures $0.20 $0.85 $1.50 $2.31 $2.86 $3.46 $4.01 $4.90
Content and vehicles $0.15 $0.56 $0.95 $1.43 $1.73 $2.06 $2.36 $2.88
Total $0.34 $1.42 $2.45 $3.75 $4.59 $5.53 $6.37 $7.78
6
Figure 2
Flood Inundation at the 0.10 Annual Exceedance Probability Event
(10-year frequency interval)
,ot 51
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Figure 3
Flood Inundation at the 0.002 Annual Exceedance Probability Event
(500-year frequency interval)
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fnrrat 51
5.0 National Economic Development Analysis
National Economic Development (NED) analysis is a key part of evaluating projects to address
water resources problems with USACE involvement. Generally, this involves estimating
economic benefits of a project from a federal or national perspective, and comparing benefits to
the financial costs of project construction or implementation. From an economic perspective,
projects with the greatest net benefits (annualized benefits less costs) are considered the NED
plan, and such projects require a benefit to cost ratio (BCR) of greater than 1.0 to be considered
a sound investment on the part of the federal government.
Structural alternative include:
■ Alt 2A1
■ Alt 2C1
■ Alt 2D1
■ Alt 3A1
■ Alt 5A1
8
■ Alt 8A1
■ Alt 17A1
The main report and engineering appendix describes these in detail. Nonstructural alternatives
(NSA) consist of buyouts and structural elevation for properties showing damages for the 50, 25
and 10-year recurrence intervals. Buyouts would involve a complete purchase of properties at
market value and demolition costs of removing structures. Structure elevation consists of raising
homes off their foundations and placing support columns underneath to protect from flooding.
For both buyouts and elevation, it is assumed that all damages estimated for existing and future
without project conditions would be eliminated. Affected structures are those identified in each
inundation footprint for each recurrence interval. Thus, benefits are the entirety of avoided
existing without project impacts.
Selection of the properties in the 10, 25 and 50-year flood plains intervals is based on the notion
that the alternatives would focus on structures prone to repetitive damages (i.e., damages that
occur at higher frequency intervals). For structural elevation alternatives, cost estimates assume
that structures would be raised to eliminate damages across all flood frequencies for structures
in each alternative footprint with the underlying logic that the bulk of elevation costs involve
removing homes from their foundations, and the marginal costs of additional height are small
relative to total costs.
■ Elevation (50 YR)
■ Elevation (25YR)
■ Elevation (10 YR)
■ Buyout (50 YR)
■ Buyout (25 YR)
■ Buyout (10 YR)
Table 4 displays NED metrics including project costs, reduced flood damages (EAD) of each
alternative, net benefits and BCRs. EAD values and BCRs show stochastic ranges estimated by
FDA based on uncertainty in hydrologic and economic variables, all of which have an underlying
probability distribution. The mid-point or mean value is typically the benchmark used as a
decision metric in terms of NED analysis. Results indicate that no alternative plans meet NED
thresholds.
9
Table 4
Single Event Flood Depths and Damages for Structures with 1Vbdeled Damages
Implementation Costs Expected Annual Damages Reduced(Benefits) Benefit to Cost Ratios
Alternative Net Benefits
(Aan)
First Costs Annual Ntan Pt Quartile 2nd Quartile 3rd Quartile 1VEan 1st Quartile 2nd Quartile 3rd Quartile
Costs
Alt2A1 $35043,000 $134,474 $12,874 $6,670 $11,815 $20,385 $1215600 0.10 0.05 0.09 0.15
Alt2C1 $8,662,000 $390,113 $301,202 $49,486 $117,290 $340,197 $88,911 0.77 0.13 0.30 0.87
Ak2D1 $10,112,000 $455,417 $335,779 $49,898 $128,643 $370,760 $119,638 0.74 0.11 0.28 0.81
Alt3A1 $9,194,000 $416,833 $335,778 $61,178 $139,903 $380,235 $81,055 0.81 0.15 0.34 0.91
Ak 5Al $15,226,431 $1,587,349 $236,631 $44,910 $106,262 $270,594 $1,350,718 0.15 0.03 0.07 0.17
Ak8A1 $4,225,000 $186,708 $85,595 $21,443 $59,219 $114,615 $101,113 0.46 0.11 0.32 0.61
Ak 17A1 $10,608,000 $486,580 $337,429 $60,807 $141,618 $383,932 $149,151 0.69 0.12 0.29 0.79
Elevation 50 YR $34,606,000 $1,540,667 $752,000 $307,790 $523,334 $943,735 $788,667 0.49 0.20 0.34 0.61
Elevation 25YR $26,460,000 $1,176,031 $679,055 $242,017 $503,097 $859,646 $496,976 0.58 0.21 0.43 0.73
Elevation 10 YR $16,914,000 $751,753 $542,000 $286,271 $454,538 $697,080 $209,753 0.72 0.38 0.60 0.93
Buyout 50 YR $55,781,254 $2,200,325 $752,000 $307,790 $523,334 $943,735 $15448,325 0.34 0.14 0.24 0.43
Buyout 25 YR $39,307,987 $1,550,527 1 $679,055 1 $242,017 1 $503,097 1 $859,646 $8715472 0.44 1 0.16 1 0.32 1 0.55
Buyout 10 YR $22,880,759 $902,545 $542,000 $286,271 1 $454,538 $697,080 $3605545 0.60 0.32 0.50 0.77
10
Appendix D : Hydraulics and
Hydrology
Cooper Creek, Denton, TX
Section 205
Closeout Report
February 2025
Cooper Creek,Denton Texas
1.0 INTRODUCTION
Hydrologic and hydraulic analyses were conducted as part of the feasibility study to evaluate alternatives
developed by the PDT to address flood related damages along Cooper Creek. A without-project condition
model for the Cooper Creek was created to simulate the hydrologic and hydraulic response of the
watershed. The without-project condition model was then modified with different measures including
floodwater detention, channel improvement and bridge/culvert improvements to improve the
management of flood risk within the Cooper Creek watershed.
1.1 Study Area
The study area is the Cooper Creek watershed located within the City of Denton, Texas. Denton is the
county seat of Denton County and is in north central Texas approximately 36 miles north of Fort Worth
and 38 miles northwest of Dallas. Direct freeway access between Denton and Fort Worth/Dallas is
provided via IH-35W and IH-35E. According to US Census Bureau, Denton had a 2023 population of
158,349 and covers 87.95 square miles. The City of Denton lies within the Trinity River basin.
Cooper Creek is located in the northern part of the City of Denton, Texas. The creek flows in a
southeasterly direction though the city and terminates at Lewisville Lake. The watershed of Cooper Creek
is about 6.1 miles long and conveys a drainage area of approximately 9.35 square miles. Cooper Creek is
generally a trapezoidal, unlined earthen channel. The creek is generally small but well defined, mostly
unimproved channel with several tributaries. The main channel has an average depth of 6 feet,top width
of 50 feet and a slope of 25 feet per mile. The creek is normally dry with flow occurring during periods of
heavy rainfall.
There are several culvert crossings that have limited capacity and cause backwater conditions within the
stream channel. The 100-year floodplain generally extends beyond the stream banks and into the
residential yards. Existing detention ponds were constructed within Cooper Creek's watershed to reduce
flood damages along the creek.There is some channel erosion along Cooper Creek due to high velocities
in the channel.
At present, most of the development within Cooper Creek watershed is residential (mostly single-family),
with a few schools and parks scattered within the watershed. While the watershed is nearly fully
developed, there are some areas in the upstream reaches of Cooper Creek and its tributaries that are
presently undeveloped and future development of these areas may worsen the backwater problems,
causing additional flooding along Cooper Creek. Commercial development is widely scattered throughout
the lower end of the watershed and has only minimal flood damage potential. Much of the vegetative
cover is in its natural state except where residential development has encroached upon the creek in the
upper end of the watershed. A map of the Cooper Creek watershed is included in Figure 1.
Cooper Creek,Denton Texas
4
--
r
1.
Lend N
ge
i• � .
WE '�
FEMA 100-yr(1Vv10E)Flaodplain f �ailk
Cooper Creek%%-ashed +r. r 7
- Svrnms(Netirne Hydmgrephy Mksd) 0.25 O,S 1 1. 2MIle
Figure 1 Cooper Creek Watershed
Based on previous USACE studies and input from the Non-Federal Sponsor(NFS),the primary areas of
flooding concern were along Cooper Creek above Mingo Rd (Figure 2). During development of existing
conditions modeling, a significant number of structures, between 0.25— 1.0 mile upstream of the NFS
identified area (Between Stuart Rd. and Windsor Dr.), were experiencing economic damages in the 10-
year to 25-year floodplains as well (Figure 3).
Cooper Creek,Denton Texas
ze
a
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Figure 2 NFS Proposed Study Areas
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Figure 3 Structures located within 25-year Floodplain between Sherman Drive and Stream CC-2
Cooper Creek,Denton Texas
1.2 Prior Studies
Flood hazard information has been identified for the Cooper Creek watershed back to 1977. In 1977,
hydrologic and hydraulic analysis work was completed bythe U.S.Geological Survey(USGS)forthe Federal
Emergency Management Agency (FEMA). In December 1979, the U.S. Army Corps of Engineers (USACE)
prepared a reconnaissance report on the flooding problems in the City of Denton (FEMA, 2001). In 1982,
the USACE completed a Continuing Authorities Program (CAP) Section 205 study that identified several
plans with benefit-to-cost ratios above 1.0. The selected plan included a total of about 4,000 feet of
channel improvement passing between a 10-year to 25-year flood event. A map of the selected plan is
included in Figure 4 (USACE, 1982).
.-�' 1 tnT10N;p ♦f 9 f�'f_- •-—. - < J w rE AR Ass
LAWD CAL
Sherman Or. _• .e•
East Windsor Dr. " jy ��_e !sTaRT 3TaTgN xle.x+ 0rEM�
_y IYD 17"TiOM ileHO 1
OROM 9TwKR W FM • i iy N 1
t ( i Old North Rd.
� \wwcxr st/EeT
,- .�-- ,�' eMiOac ro,ft M(rnw�to �.L�_.. � ... - � .`•w
- wMnn1cTMtc,wt \�
, .'t et,Mt�rze
Fart .one ai*Mrc+
((( , 9TE P AJ/
,'. - l �. 1. _!. %� � = 1• .- :r, I1 COOPER CREEK
Figure 4 Plan view of Selected Plan from 1982 USACE Cooper Creek CAP Section 205 Study
In March 1985,The FEMA Flood Insurance Study(FIS) information was updated by the USACE Fort Worth
District (FEMA, 2001). In 2009, a flood mitigation study was performed for the City of Denton by Jacobs
Engineering Group. The 2009 study identified potential detention and bridge modification alternatives
but did not include any economic benefit information (Jacobs, 2009). In 2023, a stormwater master plan
needs assessment was performed for the City of Denton by Freese and Nichols, Inc. The 2023 study was
a high-level study that identified potential areas along Cooper Creek for further analysis. While potential
areas were identified, actual alternative analysis was not performed as part of this study(Freese, 2023).
Cooper Creek,Denton Texas
2.0 HYDROLOGIC ANALYSIS
A detailed hydrologic analysis of the Cooper Creek watershed was performed to develop discharge-
frequency relationships for the Cooper Creek watershed for existing without-project conditions.
Computed peak discharges were developed for the 50, 20, 10,4, 2, 1, 0.5 and 0.2%annual chance
storms or storms that have recurrence intervals of 2, 5, 10, 25, 50, 100, 200 and 500 years, respectively.
The 100-yr flood is defined as the flood which has a 1%chance of occurring in any given year.The
hydrologic analysis was performed using Hydrologic Engineering Center Hydrologic Modeling System
(HEC-HMS) version 4.12 and Hydrologic Engineering Center River Analysis System (HEC-RAS) version 6.5.
HEC-HMS was used to compute flow hydrographs for individual subbasins while HEC-RAS was used to
combine and route the subbasin hydrographs.
2.1 Streamflow Gauging
There are no U.S. Geological Survey (USGS) streamflow recording gauges within the Cooper Creek
watershed. Nearby gages (Hickory Creek at Denton, Texas; Clear Creek near Sanger, Texas; and Ray
Roberts Lake near Pilot Point,Texas) have drainage areas(129+square miles)and land use types(primarily
rural) significantly different than the Cooper Creek watershed and were not used in this analysis.
2.2 Drainage Basin Delineation
The Cooper Creek watershed includes approximately 9.35 square miles was sub-divided into 28 sub-
basins. The watershed was subdivided using 1m StratMap LiDAR (North & Central Texas) terrain data
flown in 2020. The Lidar was downloaded from the Texas Geographic Information Office (formerly TNRIS)
Cooper Creek,Denton Texas
in June 2024. Watershed characteristics such as drainage area, watercourse length, location of centroid,
basin slope, land use, and soil type were developed for each sub-basin (Figure 5).
r
rr ..
P
Legend Cooper Creek Subbasin Layout
Cooper creek "+�
Streamlines
1 2
Subbasins Miles
Figure 5 Cooper Creek Subbasin Layout
Based on previous USACE studies and input from the NFS, the primary areas of flooding concern were
along Cooper Creek above Mingo Rd. During development of existing conditions modeling, a significant
number of structures, between 0.25—1.0 mile upstream of the NFS identified area (Between Stuart Rd.
and Windsor Dr.),were experiencing economic damages in the 10-year to 25-year floodplains as well.
2.3 Precipitation Data
Precipitation for each frequency storm was developed using data from the National Oceanic and
Atmospheric Administration (NOAA)Atlas 14 report. NOAA Atlas 14 Volume 11 covers the state of Texas
and was published in 2018. The values(Table 1)were extracted from Cooper Creek at Sherman Drive but
the values do not vary across the small study area. Rainfall volumes were not reduced due to study area's
Cooper Creek,Denton Texas
small drainage area. HEC-HMS utilized the precipitation frequency estimates and generated balanced
hyetograph storms with the most intense portion of the event falling halfway through the storm.
Table 1 Precipitation Frequency Estimates
Return Period (years) 2yr 5yr 10yr 25yr 50yr 100yr 200yr 500yr
5-min 0.45 0.58 0.68 0.81 0.90 0.99 1.08 1.20
10-min 0.73 0.94 1.09 1.30 1.45 1.59 1.74 1.92
15-min 0.90 1.16 1.36 1.60 1.79 1.97 2.15 2.38
30-min 1.26 1.61 1.88 2.22 2.46 2.71 2.96 3.29
60-min 1.63 2.10 2.45 2.91 3.24 3.57 3.92 4.38
2-hr 2.00 2.62 3.08 3.69 4.16 4.63 5.13 5.82
3-hr 2.23 2.93 3.47 4.20 4.75 5.32 5.94 6.79
6-hr 2.64 3.51 4.18 5.10 5.80 6.55 7.36 8.48
12-hr 3.11 4.15 4.96 6.05 6.89 7.79 8.76 10.10
24-hr 3.64 4.86 5.80 7.08 8.06 9.10 10.20 11.90
2.3 Model Development
Using the USACE Hydrologic Engineering Center- Hydrologic Modeling System (HEC-HMS) version 4.12
software, a watershed runoff model was developed for without-project conditions. A 1-minute
computation interval was used in the model to provide detail (shaping) of the unit hydrograph applied at
the smaller subbasins in the analysis.
2.4 Land Use Data
Future land use data was acquired from the City of Denton that represented the City's best estimate on
how the watershed will develop over the next 50 years or more. The existing land use was created using
the future land use data and comparing with aerial imagery. Where the future land use did not match the
existing condition imagery,the future land use data was modified to create an existing conditions dataset.
Land use and percent urban and percent impervious relationships were developed by the USACE Fort
Worth District and have been in use on since the 1980s. These relationships are documented in the North
Central Texas Council of Governments (NCTCOG) integrated Stormwater Management (iSWM)Technical
Manual (Figure 6).
Cooper Creek,Denton Texas
Land Use Description Percent Percent
Imperviousness Urbanization
Low Density Single family: '/. —2 units per acre; 25 30
Residential average 1 unit per acre.
Medium Densitv Single family: 2 —3'/z units per acre: 41 80
Residential average 3 units per acre.
High Density Single family: greater than 31/ units 47 90
Residential per acre: average 4 units per acre.
Multifamily Row houses, apartments,
Residential townhouses. etc. 70 95
Mobile Home Parks Single family 5-8 units per acre. 20 40
Central Business Intensive, high-density commercial 95 95
District
Strip Commercial Low-density commercial; average 3 90 90
units per acre.
Shopping Centers Grocery stores. drug stores, malls, etc. 95 95
Institutional Schools, churches, hospitals, etc. 40 50
Industrial centers and parks: light and
Industrial heavy industry. JO 95
Transportation Major highways, railroads. 35 80
communication Microwave towers, etc. 35 50
Transformer stations, transmission line
Public Utilities right-of-way, sewage treatment 60 70
facilities. water towers, and water
treatment facilities.
Strip Settlement Densities less than Y —2 units per 10 21-1
acre; average 1 unit per 3— 5 acres.
Parks and Parks, cemeteries, etc.
Developed Open 6 1 15
Space
Developing Land currently being developed 15 20
Cropland 3 5
Grassland Pasture, short grasses. 0 0
Woodlands. Forest 0 0
Water Bodies Lakes, large ponds. 100 100
Barren Land Bare exposed rock, strip mines, gravel 0 0
its.
Sources- DetemiinAon of Percent Urbanizationilmperviousness in Watersheds, May 1,
1986, U.S.Army Corps of Engineers
SCS,TR-55,Second Edition, June 1986
Figure 6 Percent Urbanization and Imperviousness Summary with Associated Land Use Categories
Land use values were correlated with percent urban and percent impervious values and the final Cooper
Creek percent urban and impervious values are identified in Table 2 and Table 3. The percent urban values
used to develop transform parameters within the HEC-HMS model and the percent impervious values
were applied to the loss method within the HEC-HMS model. A spatial representation of the changes
from the existing to future percent urban values is included in Figure 7. The percent impervious maps
show similar change from Existing to Future conditions.
Cooper Creek,Denton Texas
Table 2 Final Percent Urban Values
Subbasin Areas . mi Existing Future Increase
S 010 0.35 60 78 18
S 020 0.35 75 78 3
S 030 0.10 3 90 87
S 040 0.06 5 91 86
S 050 0.05 20 96 76
S 060 0.24 45 96 51
S 070 0.12 91 91 0
S 080 0.02 34 34 0
S 090 0.16 62 71 9
S 100 0.41 86 86 0
S 110 0.17 76 76 0
S 120 0.17 87 87 0
S 130 0.58 89 89 0
S 140 0.61 72 85 13
S 150 0.17 92 92 0
S 160 0.29 84 86 2
S 170 0.12 92 92 0
S 180 0.31 5 91 86
S 190 0.25 26 91 65
S 200 0.33 83 94 11
S 210 0.08 83 93 10
S 220 0.14 96 96 0
S 230 0.30 51 94 43
S 240 0.44 37 91 54
S 250 0.98 85 90 5
S 260 0.28 76 84 8
S 270 0.70 50 88 38
S 280 1.59 26 81 55
Cooper Creek,Denton Texas
Table 3 Final Percent Impervious Values
Subbasin Areas . mi Existing Future Increase
S 010 0.35 44 58 14
S 020 0.35 54 55 1
S 030 0.10 3 49 46
S_040 0.06 5 50 45
S 050 0.05 19 75 56
S 060 0.24 39 86 47
S 070 0.12 57 57 0
S 080 0.02 19 19 0
S 090 0.16 45 52 7
S 100 0.41 57 57 0
S 110 0.17 47 47 0
S 120 0.17 54 54 0
S 130 0.58 55 55 0
S 140 0.61 57 69 12
S 150 0.17 58 58 0
S 160 0.29 52 54 2
S 170 0.12 55 55 0
S_180 0.31 5 52 47
S_190 0.25 18 55 37
S 200 0.33 57 68 11
S 210 0.08 56 65 9
S 220 0.14 92 92 0
S_230 0.30 34 74 40
S 240 0.44 33 70 37
S 250 0.98 60 64 4
S 260 0.28 71 75 4
S 270 0.70 43 74 31
S 280 1.59 19 48 29
Cooper Creek,Denton Texas
Existing
legend Percent Urban
0-10
so
90-100
- _ _ � '" � •try
Future
Legend Percent Urban
_ t 0-10
50
�E! - 90-100
..a+
w�
f
•.r, IL rW M•�Lnr _
Figure 7 Urbanization Changes from Existing to Future Conditions
Cooper Creek,Denton Texas
2.5 Loss Rates
The initial abstractions and infiltration rates presented below were developed by the USACE Fort Worth
District from flood hydrograph reproductions studies in which losses were determined for different soil
types (Table 4). The loss rates used to compute the flood frequency estimates for this study varied with
percent sand values ranging from 2-100%.
Table 4 Standard Fort Worth District Loss Rates
Annual Average Clayey Soils Sandy Soils
Exceedance Recurrence Initial Infiltration Initial Infiltration
Probability Interval Abstraction Rate Abstraction Rate
(percent) (years) (inches) (inches/hour) (inches) (inches/hour)
50 2 1.50 0.20 2.10 0.26
20 5 1.30 0.16 1.80 0.21
10 10 1.12 0.14 1.50 0.18
4 25 0.95 0.12 1.30 0.15
2 50 0.84 0.10 1.10 0.13
1 100 0.75 0.07 0.90 0.10
0.2 500 0.50 0.05 0.60 0.08
Runoff volumes(excess rainfall amounts)were computed by deducting applicable losses from incremental
rainfall amounts. "Block" (initial abstraction) and "uniform" (infiltration rate) losses were applied to all
pervious soil surfaces within each subbasin. These losses are based on an analysis originally done in 1957.
In this analysis,the initial abstractions and infiltration rates were determined for 10 storm reproductions
on the East Fork of the Trinity River near Rockwall,Texas. Losses from these storm reproductions ranged
from maximums of 1.30-inch initial abstraction and 0.16-inch per hour infiltration, to minimums of 0.50-
inch initial abstraction and 0.05-inch per hour infiltration. Based on these storm reproductions, the 2-
year frequency storm was assigned an initial abstraction and infiltration rate of 1.50 inches and 0.20 inch
per hour, respectively. The 1000-year frequency storm was assigned an initial abstraction and infiltration
rate of 0.50 inches and 0.05 inch per hour, respectively. Losses for the 5-year through 100-year frequency
storms were then interpolated. Later studies adopted the "1-year" losses to be the same as those for the
2-year event and the losses for the 500-year and SPF events to be the same as those for the 1000-year
event. An additional 30 storm reproductions were used in the development of the Blackland Prairie Clay
and Cross Timber Sandy Loam Urbanization in 1970(Nelson) and 1977 (Rodman). In the analysis of these
storm reproductions, it was determined that the losses calculated in 1957 more closely matched those
for the watersheds that were predominantly clayey in nature; therefore, they became the "clay" losses.
A companion set of "sand" losses were then developed by increasing the "clay" losses, using losses
determined from storm reproductions in the sandy watersheds as a guide. Subsequent studies, including
streamflow frequency analyses have been used to verify the reasonableness of these losses. These losses
were applied during the original Tarrant County and Dallas County FEMA Flood Insurance Studies (FIS)
based on the similarity of soils and runoff characteristics. They have also been applied successfully in
Cooper Creek,Denton Texas
studies throughout the state, since they relate to soil type, rather than to a specific geographic region.
The final subbasin losses are identified in Table 5 and Table 6.
Table 5 Final Initial and Constant Losses for the 2-year through 25-year Frequency Storms
Return Interval 2-yr 2-yr 5-yr 5-yr 10-yr 10-yr 25-yr 25-yr
Subbasin Percent Initial Constant Initial Constant Initial Constant Initial Constant
Name Sand (in) (in/hr) (in) (in/hr) (in) (in/hr) (in) (in/hr)
S 010 47 1.78 0.23 1.53 0.18 1.30 0.16 1.11 0.13
S 020 39 1.74 0.22 1.50 0.18 1.27 0.16 1.09 0.13
S 030 20 1.62 0.21 1.40 0.17 1.19 0.15 1.02 0.13
S 040 53 1.82 0.23 1.57 0.19 1.32 0.16 1.14 0.14
S_050 58 1.85 0.23 1.59 0.19 1.34 0.16 1.15 0.14
S 060 35 1.71 0.22 1.48 0.18 1.25 0.15 1.07 0.13
S 070 11 1.57 0.21 1.36 0.17 1.16 0.14 0.99 0.12
S 080 2 1.51 0.20 1.31 0.16 1.13 0.14 0.96 0.12
S 090 71 1.92 0.24 1.65 0.20 1.39 0.17 1.20 0.14
S_100 51 1.81 0.23 1.56 0.19 1.31 0.16 1.13 0.14
S 110 17 1.60 0.21 1.38 0.17 1.18 0.15 1.01 0.13
S_120 11 1.56 0.21 1.35 0.17 1.16 0.14 0.99 0.12
S 130 64 1.89 0.24 1.62 0.19 1.36 0.17 1.18 0.14
S 140 9 1.55 0.21 1.34 0.16 1.15 0.14 0.98 0.12
S 150 16 1.60 0.21 1.38 0.17 1.18 0.15 1.01 0.12
S 160 43 1.76 0.23 1.51 0.18 1.28 0.16 1.10 0.13
S_170 15 1.59 0.21 1.38 0.17 1.18 0.15 1.00 0.12
S 180 39 1.73 0.22 1.50 0.18 1.27 0.16 1.09 0.13
S 190 100 1 2.10 0.26 1.80 0.21 1.50 0.18 1.30 0.15
S 200 24 1.64 0.21 1.42 0.17 1.21 0.15 1.03 0.13
S 210 33 1.70 0.22 1.46 0.18 1.24 0.15 1.06 0.13
S_220 84 2.00 0.25 1.72 0.20 1.44 0.17 1.24 0.15
S 230 28 1.67 0.22 1.44 0.17 1.23 0.15 1.05 0.13
S_240 59 1.85 0.24 1.59 0.19 1.34 0.16 1.16 0.14
S 250 81 1.98 0.25 1.70 0.20 1.43 0.17 1.23 0.14
S 260 25 1.65 0.21 1.42 0.17 1.21 0.15 1.04 0.13
S 270 68 1.91 0.24 1.64 0.19 1.38 0.17 1.19 0.14
S 280 79 1.97 0.25 1.69 0.20 1.42 0.17 1.23 0.14
Cooper Creek,Denton Texas
Table 6 Final Initial and Constant Losses for the 50-year through 500-year Frequency Storms
Return Interval 50-yr 50-yr 100-yr 100-yr 200-yr 200-yr 500-yr 500-yr
Subbasin Percent Initial Constant Initial Constant Initial Constant Initial Constant
Name Sand (in) (in/hr) (in) (in/hr) (in) (in/hr) (in) (in/hr)
S 010 47 0.96 0.11 0.82 0.08 0.66 0.07 0.55 0.06
S_020 39 0.94 0.11 0.81 0.08 0.66 0.07 0.54 0.06
S 030 20 0.89 0.11 0.78 0.08 0.63 0.06 0.52 0.06
S 040 53 0.98 0.12 0.83 0.09 0.67 0.07 0.55 0.07
S 050 58 0.99 0.12 0.84 0.09 0.68 0.08 0.56 0.07
S 060 1 35 0.93 0.11 0.80 0.08 0.65 0.07 0.54 0.06
S_070 11 0.87 0.10 0.77 0.07 0.62 0.06 0.51 0.05
S 080 2 0.85 0.10 0.75 0.07 0.61 0.06 0.50 0.05
S_090 71 1.02 0.12 0.86 0.09 0.69 0.08 0.57 0.07
S 100 51 0.97 0.12 0.83 0.09 0.67 0.07 0.55 0.07
S 110 17 0.88 0.11 0.78 0.08 0.63 0.06 0.52 0.06
S 120 11 0.87 0.10 0.77 0.07 0.62 0.06 0.51 0.05
S 130 64 1.01 0.12 0.85 0.09 0.69 0.08 0.56 0.07
S_140 9 0.86 0.10 0.76 0.07 0.62 0.06 0.51 0.05
S 150 16 0.88 0.10 0.77 0.07 0.63 0.06 0.52 0.05
S 160 43 0.95 0.11 0.81 0.08 0.66 0.07 0.54 0.06
S 170 15 0.88 0.10 0.77 0.07 0.63 0.06 0.52 0.05
S 180 39 0.94 0.11 0.81 0.08 0.66 0.07 0.54 0.06
S_190 100 1.10 0.13 0.90 0.10 0.73 0.09 0.60 0.08
S 200 24 0.90 0.11 0.79 0.08 0.64 0.07 0.52 0.06
S_210 33 0.93 0.11 0.80 0.08 0.65 0.07 0.53 0.06
S 220 84 1.06 0.13 0.88 0.10 0.71 0.08 0.58 0.08
S 230 28 0.91 0.11 0.79 0.08 0.64 0.07 0.53 0.06
S 240 59 0.99 0.12 0.84 0.09 0.68 0.08 0.56 0.07
S 250 81 1.05 0.12 0.87 0.09 0.71 0.08 0.58 0.07
S_260 25 0.90 0.11 0.79 0.08 0.64 0.07 0.52 0.06
S 270 68 1.02 0.12 0.85 0.09 0.69 0.08 0.57 0.07
S 280 1 79 1.04 1 0.12 1 0.87 0.09 1 0.70 0.08 0.58 0.07
2.6 Point Precipitation Volume Reduction
NOAA Atlas 14 precipitation point values were not reduced for this study due to the relatively small
drainage area (2-3 square miles) of the primary damage area between Sherman Drive and East Windsor
Drive. The precipitation volume would be reduced less than 1% if area reduction was added.
Cooper Creek,Denton Texas
2.7 Unit Hydrograph Parameters
Synthetic unit hydrograph parameters were developed for each subbasin based on specific physical
measurements, as listed in Table 7. Flowpath/stream forcing was incorporated where aerial imagery,
National Hydrography Dataset (NHD) or City storm drain data supported a different flowpath than the
flowpath resulting from the raw LiDAR. Unit hydrograph lag times (Tp's) were derived for each subbasin
using methodology described in the following reports:
"Synthetic Hydrograph Relationships,Trinity River Tributaries,
Fort Worth-Dallas Urban Area",T.L. Nelson, dated 1970.
"Effects of Urbanization on Various Frequency Peak Discharges",
Paul K. Rodman, dated October 1977.
Each of these reports discuss the development of the previously mentioned Blackland Prairie Clay and
Cross Timber Sandy Loam urbanization curves for the general Dallas-Fort Worth vicinity of Texas. These
curves relate Tp to certain measurable subbasin parameters for a specific percent urbanization and soil
type (percent sand). Each set of curves was based on flood hydrograph reproductions of predominantly
clayey or sandy watersheds in the Dallas-Fort Worth area. These curves have been successfully applied
to a number of flood insurance and planning studies in Texas with satisfactory results. The urbanization
curves relate Tp to the quantity:
Tp= 10^(0.3833log (L*Lca/(Sst^ .5))+(Sand*(log1.81-log.92)+log.92)-(BW*Urban./100))
where: Tp = the lag time in hours from the midpoint of the unit
rainfall duration to the peak of the unit hydrograph
L = the stream mileage from the discharge point to the
upstream limits of the drainage subbasin
Lca = the stream mileage from the discharge point to the
geographical centroid of the drainage subbasin
Sst= the weighted stream slope over the stream length,
from 10 percent of L to 85 percent of L, above the
discharge point, in feet per mile.
Sand = percentage sand (0-Clay, 100-Sand), as determined from permeability rates.
BW= log(tp) bandwidth between 0%and 100% urbanization
Cooper Creek,Denton Texas
Based on the percentages of clay and sand,the Tp value was computed for each subbasin by interpolating
between the Blackland Prairie Clay and Cross Timber Sandy Loam urbanization curves. A generalized
Snyder's unit hydrograph peaking coefficient of 0.72 was obtained from data developed during the
generation of the urbanization curves, was applied in this study area. The unit hydrograph data for each
subbasin are presented in Table 7.
Table 7 Watershed Characteristics and Existing and Future Lag Times
Length Weighted Existing Future
to Stream Lag Lag
Area Length Centroid Slope Time Time
Subbasin (sq. mi.) (mi) (mi.) (ft/mi) (hrs) (hrs)
S 010 0.35 1.10 0.25 42.56 0.26 0.23
S 020 0.35 0.99 0.29 53.96 0.22 0.21
S_030 0.10 0.80 0.40 53.22 0.31 0.18
S 040 0.06 0.46 0.15 53.96 0.21 0.12
S 050 0.05 0.42 0.19 71.17 0.20 0.13
S 060 0.24 1.11 0.41 47.41 0.31 0.23
S 070 0.12 0.74 0.29 29.73 0.16 0.16
S_080 0.02 0.37 0.17 52.11 0.12 0.12
S 090 0.16 0.89 0.38 51.64 0.32 0.30
S_100 0.41 1.29 0.45 59.03 0.29 0.29
S 110 0.17 1.18 0.45 47.78 0.24 0.24
S 120 0.17 0.96 0.52 40.81 0.22 0.22
S 130 0.58 1.22 0.28 66.42 0.24 0.24
S 140 0.61 1.94 0.69 23.71 0.38 0.35
S_150 0.17 0.69 0.17 45.46 0.12 0.12
S 160 0.29 1.17 0.38 56.97 0.25 0.24
S 170 0.12 0.86 0.43 41.40 0.19 0.19
S 180 0.31 0.98 0.37 67.64 0.35 0.21
S 190 0.25 0.84 0.22 66.05 0.36 0.24
S_200 0.33 1.65 0.58 41.98 0.31 0.29
S 210 0.08 0.93 0.29 53.64 0.20 0.18
S_220 0.14 0.95 0.46 48.31 0.31 0.31
S 230 0.30 1.19 0.15 63.31 0.19 0.15
S 240 0.44 1.55 0.92 30.94 0.65 0.47
S 250 0.98 2.34 1.18 37.33 0.70 0.68
S 260 0.28 1.92 1.02 23.02 0.48 0.46
S 270 0.70 1.55 0.54 26.51 0.54 0.43
S 280 1.59 3.53 1.51 18.06 1.46 1.04
Cooper Creek,Denton Texas
2.8 Hydrograph Routing
Once precipitation, losses, and transform parameters were developed for the HEC-HMS model, multiple
flood hydrographs were generated for each subbasin. Flood hydrographs were routed and combined
using 2 Dimensional (2D) HEC-RAS simulations.
2.9 Discharge-Frequency Relationships
As mentioned previously,the precipitation runoff process for the watershed was modeled using the HEC-
HMS model and 2D HEC-RAS model. Flow hydrographs for each subbasin were computed within HEC-HMS
and then applied in HEC-RAS as internal boundary conditions. These hydrographs were combined and
then routed downstream. Peak discharges (Existing (2024) Conditions) for various locations through the
study area are identified in Table 8. For this study the existing condition discharges were assumed to be
the same as the future without-project discharges since the majority of the upper half of the watershed
is already developed. A sensitivity test was performed for the 100-yr event and resulted in a 0.1 feet
elevation increase near Sherman Drive between the existing conditions and future without-project
conditions. The City of Denton identified that the primary areas of flooding concern were upstream of
Mingo Rd and as a result less detail was given to the analysis below Mingo Rd. For example, there were
no hydraulic structures added to HEC-RAS for improved hydrograph routing and flood elevations. As a
result, peak discharge reporting is only included above Mingo Rd. Peak discharges are also compared with
previous studies in Figure 8 and Figure 9. In general, the peak discharges from the current study are
higher than the currently effective FEMA FIS discharges but lower than the USACE peak discharges
developed during previous studies. The differences can be attributed to changes in
urbanization/imperviousness, reduction in precipitation depths, regional detention, and differences in
hydrologic and hydraulic methods and technology.
Table 8 Summary of Existing Condition Peak Discharges
Annual Chance (%)
50 20 10 4 2 1 0.5 0.2
Return Period (year)
Area 2 5 10 25 50 100 200 500
Location (sq. mi.)
Below Regional Pond 1 0.35 160 190 210
Above CC Trib 15 0.72 590 940 1,100 1,280 1,420 1,550 1,680 1,870
Below CC Trib 15 1.28 960 1,560 1,920 2,280 2,540 2,750 2,960 3,210
At Sherman Dr. 2.19 1,810 2,750 3,300 3,890 4,410 4,900 5,350 5,900
Below Stream CC 2 3.96 3,010 4,430 5,150 5,930 6,580 7,220 7,890 8,870
At Mingo Rd. 5.80 3,390 5,340 6,450 7,520 8,300 9,080 9,890 11,000
Cooper Creek,Denton Texas
Frequency Curves - Cooper Creek at Sherman Dr
Return Period(yrs)
10,000 2 F' 10 5 1 0 loo250 50i
y-2024 USAGE CAP Study
—FIS(2020 Effective)
u Previous Study(1985 USACE Study for FEMA)
u Previous Study(1982 USACE CAP 205 Study)
I
N
U
y
E _
U
U
N U
-ll_II_I
-�j 1 20 10 4 2 1 0 4 0
Annual Exceedance Probability(%)
Figure 8 Peak Discharge Frequency Curve for Cooper Creek at Sherman Drive
Cooper Creek,Denton Texas
Frequency Curves - Cooper Creek at Stream CC-2
Return Period(yrs)
10,000 5 10550 100 250 500
c
i
`v
m
e - -
t
N 2D24 USACE CAP Shay
G
—RS(2020 Eifeafve)
0 Previous Study(I M5 USACE 3"for FEMA)
o Preveous Snag(IGC2 USACE CAP 205 Sauy)
1,000
so =C 10 4 ? 0 d
Annual Exceedance Probability(%)
Figure 9 Peak Discharge Frequency Curve for Cooper Creek below Stream CC-2
Cooper Creek,Denton Texas
3.0 HYDRAULIC ANALYSIS
A detailed hydraulic analysis of the Cooper Creek watershed was performed to develop inundation areas
and flood depths for the Cooper Creek watershed for without-project conditions. Inundation areas and
flood depths were developed for the 50, 20, 10, 4, 2, 1, 0.5 and 0.2% annual chance storms or storms
that have recurrence intervals of 2, 5, 10, 25, 50, 100, 200 and 500 years, respectively. For this
study the existing condition discharges were assumed to be the same as the future without-project
discharges since the majority of the upper half of the watershed is already developed. A sensitivity test
was performed for the 100-yr event and resulted in a 0.1 feet elevation increase near Sherman Drive
between the existing conditions and future without-project conditions. The 100-yr flood is defined as
the flood which has a 1% chance of occurring in any year. The hydraulic analysis was performed using
HEC-HMS version 4.12 and HEC-RAS version 6.5. HEC-HMS was used to compute flow hydrographs
for individual subbasins while HEC-RAS was used to combine and route the subbasin
hydrographs. The HEC-RAS modeling was performed using 2D unsteady flow analysis.
3.1 Model Geometry Development
The study area was analyzed using HEC-RAS(version 6.5) 2D due to complex flowpaths(Figure 10),
hydrograph routing that is more physically based than simplified hydrologic routing methods, and for the
benefit of efficiently developing alternatives without the need to add cross sections.The elevation data
was developed using 1m StratMap LiDAR (North &Central Texas) terrain data. The terrain data was
reprojected into the NAD 1983 State Plane Texas North Central FIPS 4202(feet)coordinate system. All
elevations were measured from the NAVD 88(feet).
Cooper Creek,Denton Texas
fto
16
A • 11
Dr.
Jf
/1011
IL
lb
,
Figure 10 Complex Flow Paths
Generally, a 100-foot grid cell size was used to create the HEC-RAS 2D mesh. A smaller grid cell size of 50-
feet was tested and resulted in a significant (5 minute to 30 minute) increase in model simulation time
and small difference (1-2 inches) in water surface elevation. Breaklines were added to represent major
stream centerlines and were then burned or forced into the mesh. Breaklines were also utilized to
represent high points on the terrain such as embankments that either restrict flow or prevent flow. The
extents of the 2D area and associated grid cells can be seen in Figure 11.
Cooper Creek,Denton Texas
'VC-ks Park - ---
y
} Sherman Dr.
N
eaticn Celle
NOR—HAI Mingo Rd. 1 r,ri
i 3rt'3 n�3
I•
3�
! Fzr♦:
cCer�:a Din n • -
Q Ui a j�untSl:e Q
d o■
't,h S.:clg
Ashli Oak<.
Y of _ # -
xaF
r,
1 rrli I I
Figure 11 HEC-RAS Model Extents
The Multi-Resolution Land Characteristics Consortium (MRLC) 2021 National Land Cover Dataset (NLCD)
was utilized to create the base Manning's n values for the 2D cells. The NLCD dataset was used to estimate
Manning's n values primarily because,it was observed to have additional detail that was more appropriate
in some areas in determining manning's n values for the floodplain over the land use data provided by the
NFS. For example, the "Parks/Open" space land use type in the dataset provided by the NFS includes
grassland as well as forest, which have very different manning's n values (i.e. 0.04 vs 0.15). The NLCD
separates grassland and forest into separate land use categories so appropriate roughness values can be
represented. Figure 12 illustrates how the NLCD land use and associated manning's values vary spatially.
Figure 13 illustrates how the NFS land use type "Parks/Open" space can include different land use types
that have different manning's values.
Cooper Creek,Denton Texas
Grassland,n=0.038(NLCD)
Grassland Grassland
I ■ F-r r�-k
-:.,.per Creek
CC Trib 1� Forest
Legend Manning's n values
. 0.200
Park/Open Space,n=0.038(NFS) 0.168
0.137
Deciduous Forest,n=0.15(NLCD)
0.105
I 0.073
0.042
0.010
I
500 ft I
Figure 12 NLCD land use types and Manning's n assignment
Park/Open Space n=0.038
_ Grassland,n=0.038(NLCD)
f
N p,.
n
Cooper Creek
id r
a f�
j Cooper Creek
"1
CC Trib 10
,r
M s
Park/Open Space,n=0-038(NFS)
Deciduous Forest,n=0.15(NLCD)
�- Park en Space Entire Area
Figure 13 NFS Land Use Type and Manning's n assignments
Cooper Creek,Denton Texas
Manning's n values for the channel were also created that would be used in place of base values from the
NLCD data. Channel values of 0.04 and 0.015 were used for the earthen channel and concrete channel
portions respectively. The base Manning's n values were assigned based on average Manning's n values
assigned to each NLCD land used description from HEC-RAS 2D User's Manual. Table 9 indicates the base
values that were assigned for each land use type.
Table 9 Assigned Manning's n Values for NLCD Land Use
Assigned Minimum Maximum
Manning's n (21D User's (211) User's
NLCD Land Use Description Value Manual) Manual)
NoData 0.06
Grassland-Herbaceous 0.0375 0.025 0.05
Pasture-Hay 0.0375 0.025 0.05
Open Water 0.0375 0.025 0.05
Developed, Open Space 0.04 0.03 0.05
Developed, Medium Intensity 0.12 0.08 0.16
Developed, Low Intensity 0.09 0.06 0.12
Barren Land Rock-Sand-Clay 0.0265 0.023 0.03
Cultivated Crops 0.035 0.02 0.05
Deciduous Forest 0.15 0.1 0.2
Shrub-Scrub 0.115 0.07 0.16
Woody Wetlands 0.0975 0.045 0.15
Emergent Herbaceous Wetlands 0.0675 0.05 0.085
Developed, High Intensity 0.16 0.12 0.2
Mixed Forest 0.14 0.08 0.2
Evergreen Forest 0.12 0.08 0.16
3.2 Stream Crossings
Using the SA/21D Area Hydraulic Connection feature, the existing bridges and culverts were added to the
model using a combination of data from studies previously performed in the watershed as well as field
measurement. Elevations for the field measured crossings were established by combining crossing
measurements with the 1m Lidar data which accurately provided road elevations immediately adjacent
to the stream crossing as well as channel invert elevations. For study purposes, it was assumed that no
debris effects would alter bridge openings during flood stages.
Cooper Creek,Denton Texas
Culverts, bridges, and selected detention pond hydraulic structures were modeled as SA/2D Area
connections. SA/2D Area connections are model elements that hydraulically connect internal and
external model elements. These connections were used inside of the same 2D area to define key urban
features (e.g., embankments, culverts, and bridges). Every crossing in Cooper Creek was not modeled in
HEC-RAS but only those considered most important for flood hydrograph routing and water surface
elevation computation through the primary damage area. A list of the SA/2D Connections in the HEC-RAS
model is included in Table 10. A plan and profile view of the Windsor Drive crossing is shown in Figure 14
as an example.
Table 10 List of SA/2D Connections
Crossing Name Stream Name
Loop 288 CC Tributary 11 Tributary
Strickland Detention Pond CC Tributary 13
Loop 288 CC Tributary 15
Loop 288 CC Tributary 15 Tributary
Regional Detention Pond #1 Cooper Creek
Sherman Dr. Cooper Creek
Stuart Rd. Cooper Creek
Windsor Dr. Cooper Creek
Kings Row Stream CC-2
Cooper Creek,Denton Texas
coNua cc wrNo60R
822
Legend
� I �WaY
620
Exten&Tm+to Pace Ponta
KW Col Mn Ekv
618
1W Cel Mn Ebv
c Current Terran
616
I
W l
614
612
610
0 40 60 8C 100 120
Stator I M i
v
r
AL 0
Figure 14 Plan and Profile View of Windsor Dr. SA/2D Connection
Cooper Creek,Denton Texas
3.3 Boundary Conditions
The downstream boundary condition to determine the starting water surface elevations for Cooper Creek
approximately 5 miles downstream of Sherman Drive was established using a normal depth slope of 0.002.
The results in the study area are not sensitive to changes in the downstream boundary assumption with
an elevation change of around 100 feet from the downstream end to Sherman Drive.
Flow hydrographs for each subbasin were computed within HEC-HMS and were then added into the HEC-
RAS 2D flow area using internal boundary conditions. These hydrographs were then routed through the
HEC-RAS model using the 2D unsteady flow Diffusive Wave equations.
3.4 Description of HEC-RAS Plans
Table 11 contains a brief description of the alternatives within the HEC-RAS model and identifies the HEC-
RAS plan files associated with each alternative. Each alternative has 8 separate plan files representing the
2-yr, 5-yr,10-yr, 25-yr, 50-yr, 100-yr, 200-yr, and 500-yr events.
Table 11 HEC-RAS Plan Files for Alternatives
HEC-RAS
Plan Files
Alternative Description (.pXX)
W0131 Without-Project Condition 09- 16
2A1 Detention above Sherman 17- 24
2C1 Detention above Stuart ( elev 637) 74-81
2D1 Detention above Stuart ( elev 634) 82-89
03-08,
3A1 Detention (2C1) +channelization at Windsor Dr. 30,31
5A1 Detention (2C1) and bridge improvement at Sherman Dr. 40-47
25- 29, 71 -
8A1 Channelization and bridge improvement at Windsor Dr. 73
17A1 Detention (2C1) + bridge improvement (8A1) +channelization (8A1) 32-39
Cooper Creek,Denton Texas
4.0 PLAN FORMULATION
The goal of plan formulation was to determine if there was an economically and technically feasible
structural, non-structural, or combined plan for reducing flood risk on Cooper Creek in Denton, TX. The
non-structural plans did not require any additional H&H modeling.The structural plans were evaluated by
making modifications to the hydraulic model such as increases to floodplain storage or conveyance and/or
increases to hydraulic structure conveyance for the purpose of reducing water surface elevations and
associated flood risk.The first step was to identify an economic damage reach. Based on previous USACE
studies and input from the NFS, the primary areas of flooding concern were along Cooper Creek above
Mingo Rd. During development of existing conditions modeling, a significant number of structures,
between 0.25—1.0 mile upstream of the NFS identified area (Between Stuart Rd. and Windsor Dr.), were
experiencing economic damages in the 10-year to 25-year floodplains as well. After the primary areas of
flooding concern were identified, the watershed was investigated to determine economically feasible
opportunities to reduce flood risk. Much of the watershed has been developed and locations to
implement flood risk management measures was limited.
The Project Delivery Team (PDT) identified several alternatives and combinations of alternatives to
investigate for flood risk management feasibility. The alternatives were then represented in the hydraulic
model where hydrologic and hydraulic information was used to help determine economic benefits.
An economic analysis was developed for the structural alternatives. This required determining the costs
associated with constructing the structural changes such as: purchasing real estate,
excavation/hauling/disposal, and culvert improvements/enlargements. Preliminary costs were
calculated, and Flood Damage Analysis (HEC-FDA) was run to obtain the Expected Annual Damages
(EADs). A ratio of benefits over costs (B/C ratio) and net benefits were calculated for the
structural alternative. The analysis resulted in the determination that all of the structural alternatives
considered would produce a B/C ratio less than one. Cost and benefit details are located in the
economic appendix of the study report.
Unless flood risk management measures are implemented, flooding is expected to continue. Measures
investigated included detention, channel improvement, and bridge/culvert improvement, in different
combinations. The alternatives that were analyzed will be described in the following section.
Cooper Creek,Denton Texas
4.1 Structural Alternative Details
2A1 (Detention above Sherman Drive)
This alternative sought to utilize land already owned by the City of Denton and minimize impacts to the
environment. An area approximately 500 feet wide and 100 feet long was excavated (4,800 cubic yards)
from park area upstream of Sherman Drive. Figure 15 shows the location of alternative 2A1.
M
Figure 15 Location of alternative 2A1
This alternative added some floodwater storage capacity in the right overbank. 2A1 included up to 6
feet of excavation in the right overbank. To minimize impacts to the environment, this alternative will use
native grass plantings. A sample section of this alternative is included in Figure 16.
Cooper Creek,Denton Texas
ra Sample Section
Pbt I Table
Terrain Profile Plot
bib i Terrain.Cl
- —A2A
636
r 63d
o Without Project
q
1
O1 D
w
632
630 With Project
628
50 100 150 200 250
Station[ft]
Figure 16 Sample section from alternative 2A1
2A1 resulted in a maximum water surface elevation reduction of about 0.5 feet over a small stretch of
Cooper Creek upstream of Sherman Drive but did not reduce the water surface elevation between
Sherman Drive. and Windsor Dr.ive where several homes are located within the floodplain. Figure 17
and Figure 18 shows how much the 25-year and 100-years water surface elevation was reduced by
alternative 2A1. Figure 19 and Figure 20 compare the without-project floodplain and the alternative
2A1 floodplain for the 25-year and 100-year events.
Cooper Creek,Denton Texas
Water Surface Elevation Comparison(25-year)
650
649 —Without Project
646
6 —2A1(Detention above Sherman Dr)
642 Excavation Limits
640 x—mac
638
636 Stuart Dr.
u 634
tE 632
0 630 E.Sherman Dr.
628
W 626
624
622
620
618
616
614 E.Windsor Dr.
612
610
260DO 27000 2800C. 29000 30000 31000 32000 33000
Station(feet)
Figure 17 Water surface elevation reduction for alternative 2A1 (25-year event)
Water Surface Elevation Comparison(100-year)
650
648
646 —Without Project
644 _2A1(Detention above Sherman Dr)
642 Excavation Limits
640 x—�t
638
636 Stuart Dr.
u 634
632
o 630
628 E.Sherman Dr.
W 626
624
622
620
618 E.Windsor Dr.
616
614
612
610 — —
260D0 27000 280CC 29DDD 30000 310DO 32nrcii 330CC
Station(feet)
Figure 18 Water surface elevation reduction for alternative 2A1 (100-yr event)
i
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Cooper Creek,Denton Texas
2C1 (Detention above Stuart Road, elevation 637 feet)
This alternative sought to utilize a large area of undeveloped land upstream of Stuart Rd. This area is not
owned by the City of Denton and will result in more environmental impacts due to existing trees,
however this area has a significant amount of volume that could be used for floodwater storage. Figure
21 shows the location of alternative 2C1.
.r
�r1111 4 i
A
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1 � •y
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,
I �
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Figure 21 Location of alternative 2C1
About 9 acres of land was excavated to elevation 637 feet and resulted in an average excavation depth of
7 feet (Total excavation volume is 106,000 cubic yards). The alternative would include an earthen weir
approximately 850 feet in length cut to an elevation of 640.5 feet which would optimize the flood
storage of the peak of flood hydrograph. The elevation could be increased or decreased to focus flood
shaving for different events, but the 25-year event was the event that was selected as a compromise
between frequent flood events like the 10-year event and more infrequent flood events like the 100-
year. The alternative also includes a pipe at the downstream end to drain the detention area. This
Cooper Creek,Denton Texas
detention alternative meets study objectives but also provides environmental benefits through creation
of new fluvial floodplain area (Nature Based Solution) and native grass plantings. A sample section of
this alternative is included in Figure 22.
Sample Section
Without Pro]ec Terrai .Clone
614 rV
_
VA
o 5 feet
.2"'640 —
w
638
\ ith Project
630
0 100 .0 400 500 60-C 700
Station [`t]
Figure 22 Sample section from alternative 2C1
2C1 resulted in a reduction of discharges due to the flood storage capacity. The reduction in flow
resulted in a maximum water surface elevation reduction of about 1.4 feet (25-year event)with
structures along a large portion of Cooper Creek benefitting from the alternative due to the reduced
discharges. Figure 23 and Figure 24 shows how much the 25-year and 100-year water surface elevation
was reduced by alternative 2C1. Figure 25 and Figure 26 compare the without-project floodplain and
the alternative 2C1 floodplain for the 25-year and 100-year events.
Cooper Creek,Denton Texas
Water Surface Elevation Comparison (2S-year)
650
648 Without Project Detention Limas
646
644 20(Detention above Stuart(Elevation 637)
642
640
638
636 Stuart Dr.
u 634
632
0 630 E.Sherman Dr.
628
W 626
624
622
620
618
616
614 E-Windsor Dr.
612
610
26000 'iii 29DDO 30000 31000 32000 33W
Station(feet)
Figure 23 Water surface elevation reduction for alternative 2C1 (25-year event)
Water Surface Elevation Comparison(100-year)
650
648
Detention limas
646 -Without Project
644 -2C1(Detention above Stuart(Elevation 637)
642
640
638
636 Stuart Dr.
u 634
632
o 630
628 E.Sherman Dr.
W 626
624
622
620
618 E.Windsor Dr.
616
614
612
610
26OW 27000 28OCC 900C uuCC: 31000 32000 3300C
Figure 24 Water surface elevation reduction for alternative 2C1 (100-year)
i
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Cooper Creek,Denton Texas
2D1 (Detention above Stuart Road, elevation 634 feet)
This alternative is similar to 2C1 but has additional excavation depth, lower earthen weir elevation, and
longer drainage pipe.This alternative sought to utilize a large area of undeveloped land upstream of
Stuart Rd. This area is not owned by the City of Denton and will result in more environmental impacts
due to existing trees, however this area has a significant amount of volume that could be used for
floodwater storage. Figure 27 shows the location of alternative 2D1.
airy
%did - „rl
+A
vr
�. .s
IF 4
Figure 27 Location of alternative 2D1
About 9 acres of land was excavated to elevation 634 feet and resulted in an average excavation depth of
10 feet(Total excavation volume is 151,000 cubic yards). The alternative would include an earthen weir
approximately 850 feet in length cut to an elevation of 639.8 feet which would optimize the flood
storage of the peak of flood hydrograph. The elevation could be increased or decreased to focus flood
shaving for different events, but the 25-year event was the event that was selected as a compromise
between frequent flood events like the 10-year event and more infrequent flood events like the 100-
year. The alternative also includes a pipe at the downstream end to drain the detention area. This
detention alternative meets study objectives but also provides environmental benefits through creation
Cooper Creek,Denton Texas
of new fluvial floodplain area (Nature Based Solution) and native grass plantings. A sample section of
this alternative is included in Figure 28.
Sample Section
Without Project
—Terrain.Clore
f.1.1
h•1;
r 64C
0 Weir elevation, 639.8 feet
V
W
638
636 - - -
I
With Project
634
0 100 200 300 400 500 600 700
Station[ft]
Figure 28 Sample section from alternative 2D1
2D1 resulted in a reduction of discharges due to the flood storage capacity. The reduction in flow
resulted in a maximum water surface elevation reduction of about 1.7 feet(25-year event)with
structures along a large portion of Cooper Creek benefitting from the alternative due to the reduced
discharges. Figure 29 and Figure 30 shows how much the 25-year and 100-year water surface
elevation was reduced by alternative 2D1. Figure 31 and Figure 32 compare the without-project
floodplain and the alternative 21D1 floodplain for the 25-year and 100-year events.
Cooper Creek,Denton Texas
Water Surface Elevation Comparison (25-year)
650
648 Detention Limits
646 -Without Project X
644 -2D1(Detention above Stuart(Elevation 634)
642
640
638
636 Stuart Dr.
634
9632
C 630 E_Sherman Dr.
628
W 626
624
622
620
618 E-Windsor Dr.
616
614
612
610
26M 'ii ii 2800C 29000 30000 31ODD 32000 33M
Station(feet)
Figure 29 Water surface elevation reduction for alternative 2D1 (25-year event)
Water Surface Elevation Comparison(100-year)
650
648 Detertion Limits
646 -Without Project X
644 -2D1(Detention above Stuart(Elevation 634)
642
640
638
636 Stuart Dr.
u 634
632
o 630
628 E.Sherman Dr.
W 626
624
622
620
618 E.Windsor Dr.
616
614
612
610
26000 JCCC 28OCC 29000 30000 31000 32000 3300C
Station(feet)
Figure 30 Water surface elevation reduction for alternative 2D1 (100-year event)
i
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Cooper Creek,Denton Texas
3A1 (Detention (2C1) + channelization at Windsor Drive)
This alternative includes the detention from alternative 2C1 and channelization around Windsor Rd. The
channelization extent for this alternative was identified as the "NED Plan" in a previous USACE report
titled "Cooper Creek, Denton Texas, Stage 2 Planning Draft Detailed Project Report" which was from a
1981 USACE CAP Section 205 study on Cooper Creek. Figure 33 shows the location of alternative 3A1.
UP.
• ' �It
• r
1
,Owft I
Figure 33 Location of alternative 3A1
In addition to the detention configuration describes under alternative 2C1, channelization was
performed around Windsor Dr. The channelization included approximately 850 feet of grass lined
channel improvement with a bottom width of 30 feet and side slopes of 3 horizontal to 1 vertical. The
total excavation amount for this alternative is 110,400 cubic yards. This detention alternative meets
study objectives but also provides environmental benefits through creation of new fluvial floodplain area
(Nature Based Solution) and native grass plantings. A sample section of the channelization is included in
Figure 34.
Cooper Creek,Denton Texas
Sample Section
—TNn,ir.Clore
- A8A
Without Project
C
O
R
6i
w �
E'C
ith Project
6'4
20 40 60 81 100
Station[ft]
Figure 34 Sample section from alternative 3A1
3A1 resulted in a reduction of discharges due to the added flood storage capacity as well as a maximum
reduction in water surface elevation of 1.3 feet(25-year event) with structures along a large portion of
Cooper Creek benefitting from the alternative due to the reduced water surface elevations. Figure 35
and Figure 36 shows how much the 25-year and 100-year water surface elevation was reduced by
alternative 3A1. Figure 37 and Figure 38 compare the without-project floodplain and the alternative
3A1 floodplain for the 25-year and 100-year events.
Cooper Creek,Denton Texas
Water Surface Elevation Comparison(25-year)
650
648 Detention Limits
646 Without Project R +
644 —3A1(Detention+Channel Improvement)
642
640
639
636 Stuart Dr.
u 634
tE 632
0 630
> E.Sherman Dr.
628 Channel Improvement limits
W 626
624
622
620
618 E.Windsor Dr.
616
614
612
610 —
26000 27Ciiri 28MC 29000 SFOOri 310DO 32000 33M
Station(feet)
Figure 35 Water surface elevation reduction for alternative 3A1 (25-year event)
Water Surface Elevation Comparison(100-year)
650
648
Detention Limits
646 —Without Project
644 —3A1(Detention+Channel lmprovemerrt)
642
640
638
636 Stuart Dr.
u 634
632
o 630
628 E.Sherman Dr.
Channel Improvement Limits
W 626 X i(
624
622
620
618 E.Windsor Dr.
616
614
612
610 -
26000 27000 2800C 29D00 30000 310M 32Cii_i 330p0
Station(feet)
Figure 36 Water surface elevation reduction for alternative 3A1 (100-year event)
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Cooper Creek,Denton Texas
5A1 (Detention (2C1) and bridge improvements at Sherman Drive)
The goal with this alternative was to reduce the water surface elevations through Cooper Creek by
adding flood storage with detention (Configuration from alternative 2C1) and increasing the capacity
through the Sherman Drive bridge. The capacity increase was based on a configuration analyzed and
costed during a 2009 study performed for the City of Denton by an engineering firm. Figure 39 shows
the location of alternative 5A1.
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Figure 39 Location of alternative 5A1
In addition to the detention configuration described under alternative 2C1,the Sherman Drive crossing
capacity was increased from a a single 30-foot clear span to 2—40 ft by 8 ft clear spans with a single 2 ft
wide pier and vertical abutments This provided a significant increase in flow area through the bridge
(From 210 square feet to 640 square feet). Figure 40 provides an illustration of how the existing
crossing compares to the proposed crossing from 5A1. The cost estimate for the improvements to
Sherman Drive from the 2009 study was$1M. Details associated with the cost estimate for this
alternative are included in Figure 41.
Cooper Creek,Denton Texas
t t 0 t Monterrey Drive
s
a�
' a
_ 3
v �
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Relocate
Relocate
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I "S.S
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eie F 1
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634
Install Box GatHon
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Regrade
Ci
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Cooper Creek Flood Mitigation Study
WITH DETENTION Sherman[hive
JACOBS
Figure 40 Layout of proposed bridge improvements for alternative 5A1
Cooper Creek,Denton Texas
City of Denton
Cooper Creek Flood Mitigation
Preliminary Opinion of Probable Construction Cost
Sherman Dr (2 Spans) Scenarios 2&4
Item Unit
No. Description Quantity Unit Cost Cost
1 Mobilization(5%i 1 LS $33,315.00 $33,315
2 15-Sanitary Sewer Pipe 550 LF $120.00 S66,000
3 4'X4'Sanitary Sewer Manhole 3 EA $3.000.00 $9,000
4 Remove Existing 8"&15" Sanitary Sewer 520 LF $10.00 $5.200
5 Remove Existing Sanitary Sewer Manhole 2 EA S1.000.00 $2.000
6 48"Class III RCP 110 LF $180.00 $19.800
7 Remove 48" Storm Drain Pipe 60 LF $15.00 $900
8 36-Class III RCP 150 LF S150.00 $22.500
9 Headwall&Win_ all Structure 1 EA $4.000.00 $4,000
10 12-Water Line 340 LF S80.00 $27.200
11 12"Gate Valve 3 EA S2.000 00 $6,000
12 1 Remove 8'&12'W ater Line 450 LF $5.00 $2,250
13 JAsphall Pavement Repair Utilities 140 LF S70.00 $9.800
14 Trench Safety 450 LF $3.00 $1.350
15 Property Acquisition & Demolition 1 LS $55,800.00 $55,800
16 Remove Existing Bride 1 LS S20.000.00 S20,000
17 2-40'Span Bride 5.280 SF $65.00 S343,200
18 Bridge Excavation 1.560 CY S15.00 $23,400
19 12-Asphalt Pavement Repair. Bridge 590 SY $70.00 $41,300
20 JChannel Excavation 200 CY $15.00 $3,000
21 Power Pole Relocation (By Others) 1 LS $0.00 So
22 Hydromulch(Channel Slope Stabilization 400 SY $9.00 $3,600
23 PVC Coated Box Gabion 13'x3') 150 CY $180.00 $27,000
24 Traffic Control 1 LS $20.000.00 $20.000
25 SWPPP 1 LS $10,000 00 $10,000
Subtotal - Construction $756.600
W0*Q Contingency S151,320
Construction Total S907,900
10%Engineering Survey $90,790
Total Protect Cost S998,700
Item 21 - Requires power pole relocation by others
Figure 41 Cost estimate for Sherman Drive bridge improvements from 2009 study for City of Denton
5A1 resulted in a reduction of discharges due to the added flood storage capacity as well as a maximum
reduction in water surface elevation of 2.8 feet (25-year event)with structures along a large portion of
Cooper Creek benefitting from the alternative due to the reduced water surface elevations. Figure 42
and Figure 43 shows how much the 25-year and 100-year water surface elevation was reduced by
alternative SAL Figure 44 and Figure 45 compare the without-project floodplain and the alternative
5A1 floodplain for the 25-year and 100-year events.
Cooper Creek,Denton Texas
Water Surface Elevation Comparison (25-year)
650
648
Detention Limits
646 -Without Project
644
642 -5A1(Detention+(Sherman Dr)Bridge Improvement)
640
638
636 Stuart Dr.
u 634
tE 632
o 630
628 E.Sherman Dr.
W626 Increase in
bridge
624
opening
622 capacity
620
618 E.Windsor Dr.
616
614
612
610
26000 27000 28000 29000 30uC0 310,: 32000 330CC
Station(feet)
Figure 42 Water surface elevation reduction for alternative 5A1 (25-year event)
Water Surface Elevation Comparison(100-year)
650
648
Detention limits
646 -With out Project
644
642 -5A1(Detention+(Sherman Dr)Bridge Improvement)
640
638
636 Stuart Dr.
u 634
632
o 630
go 628 E.Sherman Dr.
W 626 Increase
624 in
622 opening
opacity
620
618 E.Windsor Dr.
616
614
612
610
260DO 2?000 28OCC 30000 31''' 32000 330CC
Figure 43 Water surface elevation reduction for alternative 5A1 (100-year event)
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8A1 (Channelization and bridge improvement at Windsor Drive)
The goal of this alternative was to reduce the water surface elevations through Cooper Creek by
increasing the Cooper Creek channel capacity and crossing capacity at Windsor Dr. The channelization
extent for this alternative was identified as the "NED Plan" in a previous USACE report titled "Cooper
Creek, Denton Texas, Stage 2 Planning Draft Detailed Project Report" which was from a 1981 USACE CAP
Section 205 study on Cooper Creek. Figure 46 shows the location of alternative 8A1.
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Figure 46 Location of alternative 8A1
Channelization was performed around Windsor Dr. The channelization included approximately 850 feet
of grass lined channel improvement with a bottom width of 30 feet and side slopes of 3 horizontal to 1
vertical. The crossing capacity was increased from 4-8 ft x 8 ft culverts to 4—8 ft x 8 ft culverts and 2—
8 ft wide by 6 ft high culverts. It is assumed that that the 4 existing culverts will need to be demolished
and replaced with 6 new culverts.The total excavation amount for this alternative is 4,400 cubic yards.
To minimize impacts to the environment,this alternative will use native grass plantings. A sample
section of the channelization is included in Figure 47. A figure showing the without-project and with-
project culvert configuration is included in Figure 48.
Cooper Creek,Denton Texas
Sample Section
622
—Terrain.Clone
620 —
Without Project
, 618 —
0
R
w
w
616
ith Project
614 —
C ZO 40 60 81 100
Station[ft]
Figure 47 Sample section for alternative 5A1
Cooper Creek,Denton Texas
E2= without-project configuration
620 ---- -•-- ---- --
=C 60
�tffibn ifti
- with-project configuration
5tE
4
d 616
w
61a 1 I
612
610
0 20 60 30 1JC
Station tt
Figure 48 Culvert configuration (without-project vs with-project (8A1)
Alternative 8A1 resulted in a maximum water surface elevation reduction of 1.2 feet (25-year event)
between Windsor Drive and Sherman Drive but did not provide any benefits upstream of Sherman Drive
An important note about this alternative is that it did result in some increase in flood risk downstream of
the improvements. The water surface elevation increases as high as 0.4 feet(25-year event) were
identified and would need to be addressed. One possible solution is to combine this alternative with
upstream detention. Figure 49 and Figure 50 shows how much the 25-year water surface elevation was
reduced by alternative 8A1. Figure 51 and Figure 52 compare the without-project floodplain and the
alternative 8A1 floodplain for the 25-year and 100-year events.
Cooper Creek,Denton Texas
Water Surface Elevation Comparison (25-year)
650
648
646 —Without Project
644
642 - 8A1(Channel and Bridge Improvement through Windsor Dr)
640
638
636 Stuart Dr-
634 T ..
w 632
0 630
> 628 Channel Improvement Limits E.Sherman Dr.
w 626
624 Increase in
water surface
622 elevation.
620 Additional areas
E.Windsor Dr.
618 farther
616 downstream
614 _
612 -
610
26000 27000 25CG_ 29000
st f—tl
Figure 49 Water surface elevation reduction for alternative 8A1 (25-year event)
Water Surface Elevation Comparison (100-year)
650
648
646 —Without Project —
644
642 8A1(Channel and Bridge Improvement through Windsor Dr)
640
638
636 Stuart Dr.
u 634 T
632
0 630 ' ,
q 628 E-Sherman Dr.
Limits
-,° 626 Increase in "
624 water surface
622 elevation. -
620 Additional areas
61 farther ' E.Windsor Dr.
616 do tream wns
614 __-_ r
612
610 —
2600D 27000 28CC:, 29000 30000 31000 32000 33000
Station(feet)
Figure 50 Water surface elevation reduction for alternative 8A1 (100-year event)
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Cooper Creek,Denton Texas
17A1 (Detention (2Q+bridge improvements(8A1)+channelization(8A1))
The goal with this alternative was to reduce the water surface elevations through Cooper Creek by
adding flood storage with detention (Configuration from alternative 2C1) and increasing channel and
crossing capacity along Cooper Creek and through Windsor Dr(8A1). Figure 53 shows the location of
alternative 17A1.
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low ft
Figure 53 Location of alternative 17A1
In addition to the detention configuration described under alternative 2C1, channelization was also
performed around Windsor Dr. The channelization included approximately 850 feet of grass lined
channel improvement with a bottom width of 30 feet and side slopes of 3 horizontal to 1 vertical. The
crossing capacity was increased from 4-8 ft x 8 ft culverts to 4—8 ft x 8 ft culverts and 2—8 ft wide by 6
ft high culverts. The total excavation amount for this alternative is 110,400 cubic yards. A sample
section of the channelization is included in Figure 54.
Cooper Creek,Denton Texas
Terrain Profile Plot
622 —Terrain.done
_A.
I
620 -
I
i
' 618
c
4 �
w i
6-6
6'-1 -—
0 20 40 60 80 10C
Station[ft]
Figure 54 Sample section from alternative 17A1
Alternative 17A1 resulted in a maximum water surface elevation reduction of 2.4 feet (25-year event)
with structures along a large portion of Cooper Creek benefitting from the alternative due to the
reduced water surface elevations. Figure 55 and Figure 56 shows how much the water surface
elevations reduced by alternative 17A1. Figure 57 and Figure 58 compare the without-project
floodplain and the alternative 17A1 floodplain for the 25-year and 100-year events.
Cooper Creek,Denton Texas
Water Surface Elevation Comparison(25-year)
650
648 Detention Limits
646 >�-x
644 -Without Project
642
640 -17A1(Detention+(EEWindsor Dr)Bridge Improvement+Channel Improvement,)
638
636 Stuart Dr.
v 634
tt 632
o 630
> 628 Channel Improvement Limits E_Sherman Dr.
W 626
624
622
620
618 E_Windsor Dr.
616 Increase
614 in
culvert
612 opacity
610
26000 27000 28000 29000 30000 310DO 32000 33000
Station(feet)
Figure 55 Water surface elevation reductions for alternative 17A1 (25-year event)
Water Surface Elevation Comparison(100-year)
650
648
Detention Limits
646 -Without Project
644
642 -17A1(Detention+(E.Windsor Dr)Bridge Improvement+Channef Improvements)
640
638
636 Stuart Dr.
634
w� 632
o 630
m 628 E-Sherman Dr.
> Channel Improvement Limits
W 626 r�-x
624
622
620
618 E.Windsor Dr.
616 Increase
in
614 culvert
612 opacity
610
26000 2800C 29DDO 30000 31000 ii 3300C
Station(feet)
Figure 56 Water surface elevation reductions for alternative 17A1 (100-year event)
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5.0 CONCLUSIONS
Hydraulic analyses was performed to provide information that will help assess flood risk as well as inform
flood risk management decision making within the Cooper Creek watershed.
The resulting hydraulic data was then used to determine the expected (average) annual flood damages.
This existing conditions model was then used to analyze structural and non-structural flood damage
reduction alternatives along Cooper Creek throughout the City of Denton.
After existing conditions were developed,Cooper Creek was analyzed to determine what physical changes
could be made that would be most effective in reducing flood risk. Open space was considered for
detention while existing floodplain was considered for channel and crossing improvement. Costs were
then calculated and Hydrologic Engineering Center Flood Damage Analysis (HEC-FDA) was utilized to
obtain the EADs. A ratio of benefits over costs (B/C ratio) and net benefits were then calculated.
While flood risk could be reduced with the alternatives identified and analyzed, the economic analysis
resulted in the determination that all of the structural alternative would produce a B/C ratio less than
one. Cost and benefit details are in the economic appendix of the study report.
Model Limitations and Needs for Future Study
• Equation Set Testing — The Diffusion Wave equation set was selected for simulations in the
analysis. This equation was selected for efficient run times and model stability. There are 3
shallow water equations (SWE) available that account for more information than the Diffusion
Wave equations. The SWE will generally require a smaller computation interval than the Diffusion
Wave method to run in a stable manner. If there are significant differences between the two
runs,the user should assume the SWE answer is more accurate. The following is a list of examples
where the SWE should generally be used.
o Highly Dynamic Flood Waves
o Abrupt Contractions and Expansions
o Flat(less than 1 ft/mi) Sloping River Systems
o Tidally Influenced Conditions
o General Wave Propagation Modeling
o Super Elevation around Bends
o Detailed Velocities and Water Surface Elevations at Structures
o Mixed Flow Regime
• Model Detail Below Mingo Rd—While the results at and downstream of Mingo Rd. do not impact
the results of the study area, future studies at and downstream of Mingo Rd. may warrant
additional analysis to verify the results in the primary areas of interest. Hydraulic structures were
Cooper Creek,Denton Texas
not incorporated downstream of Mingo Rd. which could have an impact on flow hydrograph
routing and computations.
• Detention Refinement — The detention alternatives were developed to optimize flood risk
reduction to the 25-year flood water surface elevations. Weir elevation was the primary
parameter that was optimized. Sherman Drive was the location where reductions to water
surface elevation were being analyzed. Additional refinements storage volume, weir length and
weir height, as well as the primary location of interest for water surface elevation reduction may
have improved economic and flood risk reduction benefits.
REFERENCES
1. Federal Emergency Management Agency, Flood Insurance Study: Denton County,Texas;
48121CV001 (2001)
2. Freese and Nichols, Inc. Stormwater Master Plan Needs Assessment. Prepared for City of
Denton. September 2023.
3. Jacobs Engineering Group. Cooper Creek Flood Mitigation Preliminary Engineering Final
Report. Prepared for City of Denton (015322.010.001.0006). July 2009.
4. Nelson,Thomas L. "Synthetic Unit Hydrograph Relationships Trinity River Tributaries, Fort
Worth-Dallas Urban Area," 1970.
5. NOAA, NOAA Atlas 14 Precipitation Frequency Atlas of the United States: Volume 11 Version
2.0: Texas, 2018.
6. NOAA(US Department of Commerce Weather Bureau), Rainfall Frequency Atlas of the United
States. May, 1961.
7. Rodman, Paul K. "Effects of Urbanization on Various Frequency Peak Discharges," 1977.
8. Texas Geographic Information Office. North and Central Texas Lidar, 2020.
https://data.geographic.texas.gov/?category=Elevation,Lidar&pg=& gl=1*18vupsy* ga*OTM2
Ni13NiYyLiE3MiEzMTE2MTA.* ga CGH7RBEG6M*MTcyMTMxMTYxMC4xLiAuMTcyMTMxMTYx
MC4wLiAuMA. Accessed June 2024.
9. U.S. Army Corps of Engineers, Fort Worth District. Detailed Project Report, Cooper Creek,
Denton,Texas. February 1982.
10. U.S. Army Corps of Engineers, Fort Worth District. Final Interim Feasibility Report and
Integrated Environmental Assessment. Pecan Bayou Watershed. Brownwood,Texas.
February 2003.
11. U.S. Census Bureau, "QuickFacks, City of Denton Texas" <
https://www.census.gov/quickfacts/fact/table/dentoncitytexas/LND110210>, accessed on
January 3, 2025.
Appendix E : Civil Engineering
Cooper Creek, Denton, TX
Section 205
Closeout Report
February 2025
Engineering
1. General
A feasibility study took place to prepare a total of seven alternatives in Denton,Texas
within the Cooper Creek channel. Due to being a feasibility study, no engineering plan
sheets were prepared. All structural alternatives were found to have sub 1.0 benefit cost
ratios (BCR).
2. Civil Design
Alternative 2A1 (Detention Above Sherman Dr., Elev. 638 Feet)
This alternative is located upstream of Sherman Drive and consists of
approximately 4,800 cubic yards of earthwork to better channelize flow and
reduce water surface elevation through increased cross-sectional area.The cut
widens the channel by roughly 80 feet with a bottom elevation of 638 feet.This
alternative would include engineering with nature features that include native
plantings that can be found in Table 4.1.This alternative was found to have a
BCR under 1.0.
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Alternative 2C1 Detention above Stuart Rd, Elev. 637 Feet)
This alternative is located upstream of Stuart Drive and consists of a 9.3acre
detention pond. 6:1 Side slopes would be graded on all sides of the pond with
the bank along the creek terminating at an elevation of 640.5 feet that would
act as a weir for stormwater to fill the pond under heavy flow conditions and be
lined with 5mm nonwoven geotextile fabric on both sides of"weir".All other
sides would meet existing elevations. The bottom of the detention pond would
have a maximum elevation of 637 feet. Clearing and grubbing would require the
removal of large number of trees that would not require replanting and 106,000
cubic yards of earthwork that would be hauled to a local landfill.The detention
pond would be expected to fully drain within 24 hours through a 24" reinforced
concrete pipe that outflows back into Cooper Creek on the Northeast edge of
the detention pond. An existing 12" PVC sanitary sewer line parallels Cooper
Creek and would require either the relocation of the line or the invert elevations
to be lowered to keep a minimum of 2 feet of cover.A concrete sidewalk would
be removed and replaced with like dimensions and would be meet all ADA
requirements.This alternative would include engineering with nature features
that include native plantings within the detention pond and can be found in
Table 4.1.This alternative was found to have a BCR under 1.0.
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Alternative 2D1 (Detention above Stuart Rd, Elev. 634 Feet)
This alternative is located upstream of Stuart Drive in and consists of a 9.3acre
detention pond. 6:1 Side slopes would be graded on all sides of the pond with
the bank along the creek terminating at an elevation of 639.8 feet that would
act as a weir for stormwater to fill the pond under heavy flow conditions and be
lined with 5mm nonwoven geotextile fabric on both sides of"weir".All other
sides would meet existing elevations. The bottom of the detention pond would
have a maximum elevation of 634 feet. Clearing and grubbing would require the
removal of large number of trees that would not require replanting and 151,000
cubic yards of earthwork that would be hauled to a local landfill.The detention
pond would be expected to fully drain within 24 hours through a 24" reinforced
concrete pipe that outflows back into Cooper Creek on the Northeast edge of
the detention pond. An existing 12" PVC sanitary sewer line parallels Cooper
Creek and would require either the relocation of the line or the invert elevations
to be lowered to keep a minimum of 2 feet of cover.A concrete sidewalk would
be removed and replaced with like dimensions and would be meet all ADA
requirements.This alternative would include engineering with nature features
that include native plantings within the detention pond and can be found in
Table 4.1.This alternative was found to have a BCR under 1.0.
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Alternative 3A1 (Detention (M) +Channelization at Windsor Dr.)
This alternative includes the detention from alternative 2C1 and channelization
around Windsor Rd.The channelization included approximately 850 feet of grass
lined channel improvement with a bottom width of 30 feet and side slopes of 3
horizontal to 1 vertical. The total excavation amount for this alternative is
110,400 cubic yards.All required construction from Alternative 2C1 would take
place within this alternative. In addition to this,Windsor drive includes multiple
existing utilities and a bridge that would be required to be removed and
replaced. Currently,the bridge has 50-foot width and 4-8 foot by 8-foot box
culverts.This alternative would widen the channel at the crossing to house a
total of 6 box culverts under the bridge,4-8 foot by 8-foot box culverts and 2-8
foot by 6-foot box culverts.This alternative requires relocation of a 15" ductile
iron pipe water line, 15" PVC sanitary sewer line, and sanitary sewer manholes
and a 36" RCP storm drain would be reinstalled on the south bank.An existing
power pole would need to be relocated and the bridge would require
reconstruction with 12" asphalt pavement. Channel slope stabilization, such as
5mm nonwoven geotextile fabric, would be installed to reduce erosion after
bare earthwork along the channel sides in addition to native plantings such as
those found in table 4.1.This alternative was found to have a BCR under 1.0.
Existing 12"Water /
Line New 2-8'x6'
Box Culverts _
Existing Natural
Gas Line Remove&Replace
4-8'x8'Box Culverts
Relocate 15"SDR 26
Remove&Replace Sanitary Sewer Line
Asphalt Bridge -
i-
Remove&Replace
36"Storm Line
Remove and
Replace Power Pole H °
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Alternative 5A1 (Detention 2C1) and Bridge improvements at Sherman Dr.)
Alternative 5A1 involves an existing crossing located at Sherman Drive and the
previous alternative 2C1.The bridge opening would be widened to 2 40' spans
with wingwalls to increase flow under the bridge from a cross sectional area of
210 square feet to 640 square feet. This alternative requires relocation of a 12"
ductile iron pipe water line, 15" PVC sanitary sewer line, and sanitary sewer
manholes and a 48" RCP storm drain would be reinstalled on the north bank. An
existing power pole would need to be relocated and the bridge would require
repair with 12" asphalt pavement.The detention location is located upstream of
Stuart Drive and consists of a 9.3acre detention pond. 6:1 Side slopes would be
graded on all sides of the pond with the bank along the creek terminating at an
elevation of 640.5 feet that would act as a weir for stormwater to fill the pond
under heavy flow conditions and be lined with 5mm nonwoven geotextile fabric
on both sides of"weir".All other sides would meet existing elevations.The
bottom of the detention pond would have a maximum elevation of 637 feet.
Clearing and grubbing would require the removal of large number of trees that
would not require replanting and 106,000 cubic yards of earthwork that would
be hauled to a local landfill.The detention pond would be expected to fully drain
within 24 hours through a 24" reinforced concrete pipe that outflows back into
Cooper Creek on the Northeast edge of the detention pond. An existing 12" PVC
sanitary sewer line parallels Cooper Creek and would require either the
relocation of the line or the invert elevations to be lowered to keep a minimum
of 2 feet of cover. A concrete sidewalk would be removed and replaced with like
dimensions and would be meet all ADA requirements. Channel slope
stabilization of 5mm nonwoven geotextile fabric would be installed to reduce
erosion in addition to native plantings that can be found in Table 4.1.This
alternative was found to have a BCR under 1.0.
glow
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i
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h�
r
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Rebate
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Rebate
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Cooper Creek Flood Mitigation Study
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Alternative 8A1 (Channelization and Bridge Improvement at Windsor Dr.)
This alternative is located at the bridge crossing of Windsor Drive.Windsor drive
includes multiple existing utilities and a bridge that would required to be
removed and replaced. Currently, the bridge has a 50-foot width and 4-8 foot by
8-foot box culverts.This alternative would widen the channel at the crossing to
house a total of 6 box culvert under the bridge,4-8 foot by 8-foot box culverts
and 2-6 foot by 6-foot box culverts. In addition. The invert elevations of the box
culverts would reduce from the existing 612.4 feet to approximately 611.3. This
alternative requires relocation of a 15" ductile iron pipe water line, 15" PVC
sanitary sewer line, and sanitary sewer manholes.A 36" RCP storm drain would
be reinstalled on the south bank within a non-standard cast in place headwall
structure. An existing power pole would need to be relocated and the bridge
would require reconstruction with 12" asphalt pavement.Approximately,4,400
cubic yards of earthwork would be required and channel slope stabilization, such
as 5mm nonwoven geotextile fabric,would be installed to reduce erosion after
bare earthwork along the channel sides in addition to native plantings such as
those found in table 4.1.This alternative was found to have a BCR under 1.0.
Existing 12"Water
Line New 2-8'x6'
Box Culverts
Existing Natural
Gas Line Remove&Replace
/ 4-8'x8'Box Culverts 1.
Relocate 15"SDR 26''Y'
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Asphalt Bridge
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Replace Power Pole v
DIP Water Line '
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Alternative 17A1 (Detention (2C1)+Bridge Improvements(8A1)+Channelization (8A1))
This alternative is a combination of previous alternatives 2C1 and 8A1.
Alternative 2C1 is located upstream of Stuart Drive and consists of a 9.3acre
detention pond. 6:1 Side slopes would be graded on all sides of the pond with
the bank along the creek terminating at an elevation of 640.5 feet that would
act as a weir for stormwater to fill the pond under heavy flow conditions and be
lined with 5mm nonwoven geotextile fabric on both sides of"weir".All other
sides would meet existing elevations.The bottom of the detention pond would
have a maximum elevation of 637 feet. Clearing and grubbing would require the
removal of large number of trees that would not require replanting and 106,000
cubic yards of earthwork that would be hauled to a local landfill.The detention
pond would be expected to fully drain within 24 hours through a 24" reinforced
concrete pipe that outflows back into Cooper Creek on the Northeast edge of
the detention pond. An existing 12" PVC sanitary sewer line parallels Cooper
Creek and would require either the relocation of the line or the invert elevations
to be lowered to keep a minimum of 2 feet of cover.A concrete sidewalk would
be removed and replaced with like dimensions and would be meet all ADA
requirements.This alternative would include engineering with nature features
that include native plantings within the detention pond and can be found in
Table 4.1.This alternative is located at the bridge crossing of Windsor Drive.
Windsor drive includes multiple existing utilities and a bridge that would
required to be removed and replaced. Currently,the bridge has a 50-foot width
and 4-8 foot by 8-foot box culverts.This alternative would widen the channel at
the crossing to house a total of 6 box culvert under the bridge,4-8 foot by 8-foot
box culverts and 2-6 foot by 6-foot box culverts. In addition.The invert
elevations of the box culverts would reduce from the existing 612.4 feet to
approximately 611.3. This alternative requires relocation of a 15" ductile iron
pipe water line, 15" PVC sanitary sewer line, and sanitary sewer manholes.A 36"
RCP storm drain would be reinstalled on the south bank within a non-standard
cast in place headwall structure.An existing power pole would need to be
relocated and the bridge would require reconstruction with 12" asphalt
pavement.Approximately,4,400 cubic yards of earthwork would be required
and channel slope stabilization, such as 5mm nonwoven geotextile fabric, would
be installed to reduce erosion after bare earthwork along the channel sides in
addition to native plantings such as those found in table 4.1.This alternative was
found to have a BCR under 1.0.
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3. Construction Procedures
Construction Access
Haul routes,traffic control plans, and construction access would vary based on
the alternative(s) chosen and would be chosen to minimize disruption to local
traffic.
Pavement Repair
Due to construction traffic, it is anticipated that local roads would be damaged
and require repair.
Laydown Areas
Laydown areas for construction material and equipment would be required and
would be decided based on the alternative(s) chosen.
4. Native Plantings
In an effort to provide cost-effective, self-sustaining alternatives to traditionally
engineered flood management, the planting list in Table 4.1 would be used to replant all
disturbed areas due to them being native to the area of the North Texas, having deep
root systems that help resist erosion of soil, and their drought tolerance.
Table 4.1 Planting List
Common Name Botanical Name Classificaiton
Big Bluestem Andropogon gerardii Grass
Switchgrass Panicum virgatum var"Shenandoah' Grass
Turf's Cap Malvaviscus arboreus var. drummondii Forb
Little Bluestem Schizachyrium scoparium Grass
Blue Grama Bouteloua gracilis Grass
Eastern Gamagrass Tripsacum dactyloides Grass
Plains Coreopsis Coreopsis tinctoria Forb
Maximilian Sunflower Helianthus maximiliani Forb
Sideoats Grama Bouteloua curtipendula Grass
Appendix F :
Geotechnical
Cooper Creek, Denton, TX
Section 205
Closeout Report
February 2025
Cooper Creek CAP 205 1
1.0 Introduction
This report documents the results of a geotechnical evaluation performed for the Cooper Creek
Section 205 flood risk management project in Denton, Texas. The scope of the investigation was
to obtain a historical prospective of the site, identify surface and subsurface conditions, and
address geotechnical concerns relevant to the project. This report presents a summary of the
findings based on historical documents and site observations. This report also includes a
preliminary assessment of the geotechnical considerations for the future-with-project conditions
from five screened alternatives. The alternatives listed in the table below incorporate either one
or a combination of options intended to mitigate flooding impacting the surrounding residential
community including, detention basins at E Sherman Dr or Stuart Rd, channelization
improvements at E Windsor Dr, and bridge culvert modifications at E Sherman Dr.
(2A1)Detention above E Sherman Dr
Alternative 2—Detention Basin alone (2C1)Detention above Stuart Rd(elev 637)
(2D1)Detention above Stuart Rd(elev 634)
Alternative 3—Detention Basin and Channel Detention(20) with channelization at E
Improvements Windsor Dr.
Alternative 5—Detention Basin and Bridge Culvert Detention(2C1)with bridge improvement at E
Modifications Sherman Dr.
Alternative 8—Channel Improvements and Bridge Channelization and bridge improvements at E
Culvert Modifications Windsor Dr.
Alternative 17-Detention Basin,Bridge Culvert Detention(20)with channelization and bridge
Modifications,Channel Improvements improvements at E Windsor Dr.
Geotechnical Feasibility Report February 2025
Cooper Creek CAP 205 2
2.0 Existing Conditions
2.1. Location and Description
Cooper Creek stretches across the northeastern portion of the City of Denton, Texas. The creek
flows to the southeast through a primarily residential portion of the city and feeds into Lewisville
Lake. The watershed of Cooper Creek is about 6.1 miles long and conveys a drainage area of
approximately 9.64 square miles. The creek is generally small but well defined, mostly
unimproved channel with several tributaries. The main channel has an average depth of 6 feet,
top width of 50 feet and a slope of 25 feet per mile. The creek is normally dry with flow
occurring during periods of heavy rainfall. Cooper Creek is generally a trapezoidal, unlined
earthen channel. There are several culvert crossings that have limited capacity and cause
backwater conditions within the stream channel. The 100-year floodplain generally extends
beyond the stream banks and into the residential yards. Existing detention ponds were
constructed within Cooper Creek watershed to reduce flood damages along the creek. There is
some channel erosion along Cooper Creek due to high velocities in the channel.
2.2. Geology
The project area is in a region known as the Eastern Cross Timbers Ecoregion. This region
extends southward from the Red River through eastern Denton County and along the boundary
between Dallas and Tarrant counties. It then stretches through Johnson County to the Brazos
River and into Hill County (Butler, 2022). The region includes rolling hills, cuestas, and ridges.
Soils within the Cross Timbers are mostly sandy, loamy, and are underlain by sand, shale, clay,
sandstone, calcareous shale, and limestone. Today, livestock farming is the main land use, but
some cropland also occurs (TPWD-A 2024). The City of Denton sits on top of the Grayson Marl
rock formation. Grayson Marl, mostly marl, is light-greenish-gray to medium-gray, weathers to
grayish yellow. Thickness of Grayson Marl in Texas is between 15 and 60 feet(USGS, 2024).
Geotechnical Feasibility Report February 2025
Cooper Creek CAP 205 3
3.0 Previous Investigations
3.1. Site Visit
A site visit to Cooper Creek was conducted by the Fort Worth District project team on June 18,
2024. During the site trip, representatives from the City of Denton accompanied the project team
and identified several problematic locations where existing infrastructure was being adversely
impacted during flooding events. The following excerpt from draft feasibility report briefly
describes the pressing inundations issues affecting the existing infrastructure. Beginning
downstream, Cooper Creek crosses Mingo Road. Mingo Road currently is overtopped during
flooding events, affecting emergency response and evacuation times, but does not create
backwater affects nor damage to any structures directly upstream from the crossing. The
Nottingham Drive crossing is just downstream of Avondale Park; flooding seems to cause
minimal structural damages at this point, however, there is evidence of bank erosion downstream
of this location. At East Sherman Drive, a bend occurs directly at the crossing with the low-lying
area occurring just upstream and to the north of the crossing. Overloading and surcharging of the
local storm drain system is likely during flooding events, with this location having the most
properties experiencing flooding. The upstream limit of the project area does not appear to
include any structures that experience flooding will likely not fall within the scope of this
project.
3.2. Historical Geotech Report
In lieu of performing a geotechnical investigation, a historic geotechnical document provided by
the City of Denton, titled Report 187-08-06 Geotechnical Engineering Services, Cooper Creek
Detention Pond, was utilized to inform and characterize the potential subsurface. In 2008, four
(4) borings were drilled by CMJ Engineering, Inc. down to 12 and 17 feet below ground surface.
The borings were obtained at three different locations that coincidentally surround the primary
site for the proposed work at E Sherman Dr and E Windsor Dr. The closest borings were drilled
at Sites 2 and 3, which are located approximately 4000-feet northwest and 3800-feet southwest
from the proposed work at E Sherman Dr, respectively. Site 1 is located approximately 6000-feet
east of the proposed work site. No groundwater was observed in the borings during drilling or at
the time of completion.
Boring logs indicate that overburden material consisting of sandy, silty, and shaly clays were
encountered from the surface down to depths of about 4 feet (in the two 17-feet-deep borings) at
Site 2, while overburden material was encountered down to boring termination (in the two 12-
feet-deep borings) at Sites 1 and 3. These clay soils were characterized as having very stiff to
hard consistencies, moisture contents ranging from 6% to 21%, with colors ranging from dark
brown, brown, reddish brown, to light brown.
Geotechnical Feasibility Report February 2025
Cooper Creek CAP 205 4
The primary formation was only encountered at Site 2, which typically consisted of tan limestone
down to depths of 10 to 15 feet, underlain by gray shale extending down to 15 and 17 feet below
ground surface. Clay seams were observed throughout the limestone. Both the limestone and
shale primary were classified as moderately hard to hard.
Geotechnical Feasibility Report February 2025
Cooper Creek CAP 205 5
4.0 Future With Project Conditions
Flood protection is primarily provided by an unlined earthen channel. The channel bottom and
slopes soils were observed to be primarily sandy, silty, and shaly clays with the occasional
limestone outcrop. The existing channel is inadequate to provide flood protection with the 100-
year plain generally extending beyond the stream banks and into residential yards.
A total of five project alternatives are being selected for the future with project conditions. Of
these alternatives, one alternative considers three different detention basin designs with one
detention basin design at E Sherman Dr and two different detention designs at Stuart Rd. The
final four alternatives incorporate a combination of the elev. 637 Stuart Rd detention basin
design, with the channelization improvements or the bridge/culvert modifications to mitigate
flooding. The alternatives are listed below.
4.1. Alternative 1: No Action (Future Without Project Conditions).
Alternative 1 is No Action. If no action is taken the current situation with flooding would continue
to occur or become more frequent as the unlined channel deteriorates.
4.2. Alternative 2: Detention Basin alone.
Alternative 2 would consist of designing and constructing a detention basin in the vicinity of
Cooper Creek. The detention basins would provide additional storage capacity to the creek
during flooding and rainfall events, mitigating the inundation issues in the surrounding residents.
• Alternative 2A1 considers the excavation and construction of a detention basin to the east of E
Sherman Dr. The proposed design would widen the existing channel bottom (approximately at
elevation 628 feet) by about 100-feet. An estimated 4,800 cubic yards of native soil/rock is
expected to be excavated.
• Alternative 2C 1 considers the construction of a detention basin to the east of Stuart Rd. The
proposed design incorporates a basin bottom at elevation 637 feet and weir at elevation 640.5
feet. An estimated 106,000 cubic yards of native soil/rock is expected to be excavated.
• Alternative 2D 1 considers the construction of a detention basin at the same location as 2C 1,
listed above. Except, this proposed design incorporates a basin bottom at elevation 634 feet
and weir at elevation 639.8 feet. An estimated 151,000 cubic yards of native soil/rock is
expected to be excavated.
4.3. Alternative 3: Detention Basin and Channel Improvements.
Alternative 3 includes detention basin design from Alternative 2C 1 and the channel improvement
Geotechnical Feasibility Report February 2025
Cooper Creek CAP 205 6
proposed in Alternative 8. The proposed channel improvement would incorporate straightening
an 842-foot-long section of Cooper Creek at E Windsor Dr as well as deepening or widening the
channel. An estimated 106,000 cubic yards of native soil/rock is expected to be excavated for the
detention basin, and approximately 4,400 cubic yards is expected to be excavated from the
channel improvement. In total, approximately 110,400 cubic yards of soil/rock will need to be
excavated.
4.4. Alternative 5: Detention Basin and Bridge Culvert Modifications.
Alternative 5 includes detention basin design from Alternative 2C 1 as well as adding or
modifying the box culvert/bridge at Sherman Drive, Mingo Road, and/or Blagg Road to increase
hydraulic capacity. An estimated 106,000 cubic yards of native soil/rock is expected to be
excavated for the detention basin.
4.5. Alternative 8: Channel Improvements and Bridge culvert modifications.
Alternative 8 includes channel improvements such as straightening and deepening or widening
an 842-feet-long section of Cooper Creek near E. Windsor Dr as well as adding or modifying the
box culvert/ bridge at Sherman Drive, Mingo Road, and/or Blagg Road to increase hydraulic
capacity. A typical section for of the completed channel improvement will incorporate 3 to 1
(horizontal to vertical) slopes, resulting in approximately 4,400 cubic yards of expected soil/rock
excavation.
4.6. Alternative 17: Detention Basin, Bridge culvert modifications, Channel
improvements.
Alternative 17 includes detention basin design from Alternative 2C1, the channel improvements
from Alternative 8, as well as adding or modifying the box culvert/ bridge at Sherman Drive,
Mingo Road, and/or Blagg Road to increase hydraulic capacity. An estimated 106,000 cubic
yards of native soil/rock is expected to be excavated for the detention basin, and approximately
4,400 cubic yards is expected to be excavated from the channel improvement. In total,
approximately 110,400 cubic yards of soil/rock will need to be excavated.
Geotechnical Feasibility Report February 2025
Cooper Creek CAP 205 7
5.0 Considerations
5.1. Excavation Concerns
Based upon information gathered during a site visit and borings from CMJ Engineering's
geotechnical report, both the sandy, silty, and shaly clay overburden material and the
limestone/shale primary material are expected to be encountered at the surface and during
excavation of the detention basin and channel improvements. It is expected that the excavation of
denser and harder limestone or shale primary will likely incur a considerable increase to cost,
and effort compared to the conventional earthwork equipment used for overburden soils.
Additionally, should sands be encountered during excavation, precautions to prevent caving
should be considered.
Additional costs and design changes could also be later incurred in the event shale is encountered
during excavation at the channel improvement and detention basin sites. When primary shales
are unloaded and exposed to the surface and to weathering, significant swell/shrinkage can occur.
The presence of exposed shale along the surface of the slopes or bottom at either the channel or
detention basin could present significant potential erosion and heave concerns. A subsurface
investigation could mitigate some uncertainties.
5.2. Earthwork Concerns
Slope stability is major concern for nearly all earthen embankments, especially when subjected
to various loading and drawdown conditions from inundation. Permanent slopes at the site
should be as flat as practical to reduce the potential for shallow slides and erosion. Currently, the
channel improvement design incorporates a 3H:1 V slope for the final channel profile with a
channel depth at approximately 9 feet. The following table for maximum slope angles was
recommended by CMJ Engineering for similar detention pond designs at Cooper Creek.
Height(ft) Slope
Horizontal : Vertical
0-3 1:1
3-6 2:1
6-9 3:1
>9 4:1
5.3. Conclusion
The Project Delivery Team concluded that the BCR(benefit-to-cost ratio) for the selected project
alternatives would not be sufficient to meet the threshold (BCR>1) required to justify the
proposed work. Should any of the selected project alternatives be proposed or reconsidered, a
Geotechnical Feasibility Report February 2025
Cooper Creek CAP 205 8
subsurface exploration program and a more detailed engineering analysis is required before final
geotechnical recommendations for the design and construction of the proposed detention basin
and channel improvements can be made. Without sufficient subsurface sampling and testing
within the immediate vicinity of the proposed detention basin and channel improvement
locations, costs may vary significantly. Additionally, on-site permeability testing should be
conducted at all proposed detention basin construction sites.
Geotechnical Feasibility Report February 2025
Cooper Creek CAP 205 9
6.0 References
• Butler D.R., Ecoregions of Texas 2022.
https://texasalmanac.com/topics/environment/physical-regions-texas Accessed
July 3, 2024.
• Texas Parks and Wildlife Department - A. 2024. Texas Ecoregions.
https://tpwd.texas.gov/education/hunter-education/online-course/wildlife-
conservation/texas-ecoregions
• United States Geological Survey, Geologic Atlas of Texas 2024.
https://webapps.usgs.gov/txgeology/Accessed July 3, 2024.
• CMJ Engineering, Inc (2008). Report 187-08-06 Geotechnical Engineering Services,
Cooper Creek Detention Pond, Three Sites, Denton, Texas.
Geotechnical Feasibility Report February 2025
I I
US Army Corps
of Engineers
REAL ESTATE APPENDIX
Cooper Creek
Continuing Authorities Program: Section 205
Flood Risk Management
Denton, Texas
Updated: 10 January 2025
Prepared By: Justin Weeks
Realty Specialist
US Army Corps of Engineers
Fort Worth District
819 Taylor Street
Fort Worth,TX 76102
r
Real Estate Considerations/Problems in Area
Cooper Creek, and much of the surrounding City of Denton, Texas, is widely
developed with residential housing resulting in little available land within the study area.
Over the course of the CAP 205 study, the Real Estate Division advised the team of
their available resources and constraints to use on potential project lands. City
representatives were informed of what actions were necessary as a Non-Federal
Sponsor (NFS) and their requirement of providing Lands, Easements, Rights of Way,
Relocations, and Disposal Areas (LERRD). District real estate appraisal staff performed
an appraisal cost analysis to support plan formulation.
Engineering Regulation ER 405-1-12 Chapter 12 requires the Real Estate
Division to determine the minimum interest in real property necessary to construct,
operate and maintain a USACE cost-shared civil works project. Once the minimum
interest has been determined, the corresponding USACE standard estate must be used
for the acquisition of said interest. Any deviation from the approved estates is
considered non-standard and must be approved by the USACE Directorate of Real
Estate. A discussion on the standard estates identified as required to support each
alternative is included below.
Evaluation of Lands for Alternatives
Three primary areas were identified to support construction of the structural
measures for the project. Of those, two support digging detention basins to store water
in flood events, a second alternative is to arm the creek channel against further erosion
and support greater flood conveyance, and the third involves culvert modifications under
2 separate bridges within the areas of the previous alternatives. There are several
modifications that involve combinations of the above. District economists also evaluated
non-structural alternatives of buyouts, and raising of structures within 10-, 25-, and 50-
year flood events. These alternatives will be discussed further in the economics
appendix. All alternatives considered by the Real Estate Division are shown in table 1,
below.
ALTERNATIVE PLAN DESCRIPTION
1—No Action
2A1 Detention above Sherman
2—Detention basin alone 2C1 Detention above Stuart(elev 637)
2D1 Detention above Stuart(elev 634)
3—Detention basin and channel improvements 3A1 I Detention(2c1)+channelization at Windsor Dr.
5—Detention basin and bridge culvert modifications 5A1 IDetention (2C1)and bridge improvement at Sherman Dr.
8—Channel improvements and bridge culvert modifications 8A1 lChannelization and bridge improvement at Windsor Dr.
17—Detention basin,bridge culvert modifications,channel improvements 17A1 Detention(2C1)+bridge improvement(SA1)+channelization(sA1)
Table 1. Alternatives considered during feasibility stage of Cooper Creek CAP Section
205 Study.
2 1 P a g e
Alternative 2A1
Alternative 2A1 involves creation of a detention pond along the existing channel
within Denton County Appraisal District (DCAD) parcel number 84607. This parcel is
owned in fee by the City Parks Department, no additional acquisition would be
necessary. During the site visit the project delivery team identified two existing sewer
lines that would require relocation through some form of combination of a 12" and 15"
into one 18" line off property. The city valuated said relocation at approximately
$525,000. Utility and facility relocations are responsibility of the sponsor and
submittable for credit as LERRD.
Figure 1. Area of impact for alternative
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Alternatives 2C1/2D1
Alternatives 2C1 and 2D1 both utilize DCAD parcel number 39529 owned by
Trans-Atlas Financial, LLC. Both require the same surface acreage but differ in the
maximum volume of disposal material to be removed. Due to much of the parcel being
necessary for the work to be done it was evaluated as a fee ownership take. The area
for these two alternatives is shown below in figure 2.
3 1 P a g e
Figure 2. Area to be acquired for alternatives 2C1 and 2D1.
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Alternative 8A1
Alternative 8A1 involves channelization measures to be performed upstream and
downstream of E. Windsor Drive. This work would impact 21 private residences where
the creek has eroded into the backyards of the homes and the city would be required to
acquire a channel improvement easement over the lands. According to City plat
records, the landowners on either side of the creek hold fee title to the lands to the
centerline of Cooper Creek, and the city holds a drainage easement over the creek. The
city provided said drainage easement and associated figures to the Real Estate Division
for review. The provided easements do not meet the minimum requirements of the
USACE Channel Improvement Easement and therefore the city was informed that
further acquisition would be necessary. These deeds, plats and associated figures are
included as Addendum 1 to this report.
Alternative 8A1 also involves culvert modification under the E. Windsor Drive
bridge over Cooper Creek. The bridge would be removed, the culverts would be
upgraded to allow greater flow under the bridge, and the bridge would then be replaced.
Bridge and other road modifications are included as public facility relocations and a duty
of the sponsor as a portion of the LERRD required for the project as described in ER
1165-2-131. As such this modification was included as a relocation within the project
cost estimate.
4 1 P a g e
Figure 3. Area to be ac uired for alternative 8A1.
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Alternative 5A1
Alternative 5A1 involves a similar bridge culvert modification within 8A1 under E.
Sherman Drive, downstream from the proposed area of 2A1. This modification was also
treated as a public facility relocation to be performed by the sponsor and costed in the
project cost estimate. The area is shown on figure 4, below.
Figure 4. Area of brid e culvert modifications required for alternative 5A1.
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5 Page
Schedule and Real Estate Capability Assessment
The Real Estate Division met with the PDT and representatives from the City of
Denton (including engineering staff, Real Estate, and the Parks Department staff) to
perform an acquisition capability assessment as required for a typical Real Estate
Planning Report. Overall, the sponsor was deemed to be capable of performing the
acquisition and any necessary relocations in accordance with P.L. 91-646 (The Uniform
Relocation Act). However, the city representatives expressed unwillingness to acquire
any private residences through condemnation authority which could pose a risk to
project timeline and viability. Additionally, the city expressed the desire to hire an
outside consultant to handle any relocations. USACE has allowed other non-federal
sponsors to do so on other projects and therefore this was determined acceptable for
this stage of planning. During the same meeting, the overall project acquisition schedule
was discussed with emphasis on timelines and periods of performance that can be
expected for typical deliverables related to the acquisition. Typical contracts for surveys,
appraisals, and title work have 30 to 60-day periods; the city can close on a property in
approximately 4 months from initial offer (if accepted), and the usual condemnation
action takes between 1.5-2 years to complete. These estimates fall within normal for
project timelines. The full capability assessment is attached as addendum 2.
Real Estate Cost Study
In agreement with Project Management, the Gross Appraisal typically
required as part of the Real Estate Planning Report generated during a feasibility study
would be unnecessarily costly and more detailed than necessary for this study.
Therefore, SWF-RE appraisal staff preformed a cost study report. The study considered
the required estates identified for each alternative and adjusted the valuation based on
said estate. A Fee ownership was determined at 100% of the County Appraisal District
(CAD) valuation (plus contingency) and an easement was reduced slightly to 90% of
CAD (again, plus some contingency). The full cost study is attached as addendum 3.
The results of the cost study are shown in the table 2, below.
Alternative Acres needed Cost per acre Total Cost
2A1 0.82 $33,319 $24,590
2C1/2D1 15.14 $32,016 $484,715
8A1 1.84 $6.10/ft2 $439,200
Table 2, cost analysis chart for the 3 primary alternatives considered.
6 1 P a g e
Prepared by:
Di signed by
WEEKS.JUSTIN.R WEIEKS.JUSTIN.REID.15895646
EID.1589564690 90
Date:2025.02.1107:50:29-06'00'
Justin Weeks
Realty Specialist
Fort Worth District
Reviewed by:
Digitally signed y
MINDIETA.DAVID. MINDIETA.DAVID.WADE.128363
WADE.
Date:2025.02.13 07:44:12-06'00'
David W. Mindieta
Chief, Planning and Appraisal
Fort Worth District
7 Page
APPENDIX 1: DRAINAGE EASEMENT AND PLAT
V " J
THE STATE OF TEXAS 13SS
KNOW ALL MEN BY THESE FRESENTSs
COUNTY OF DENTON j
THAT WE, Nette Shultz, Susie Beyette and Callie R. Ratliff, each
being a feme sole, of Denton County, 'Texas, for and in consideration of
the sum of One Dollar ($1.00) cash to us in hand paid and-the benefits
that will accrue to our property, the receipt of which is hereby acknow-
ledged, do hereby GIVE AND GRANT unto the said-.City of:Denton, Texas,
a Municipal Corporation, the right to' dig -a drainage ditch and perpet
ually maintain an open drainage ditch :in, upon and across the follow-
in described tract of land being more `g , g particularly described as fol-
lows, ,
lows, to-wit:
All that certain lot, tract or parcel of land lying and
being situated in the County of Denton,,-State of Texas,
being out of the Hardin Carter Survey, Abst. No. 281,
and being more particularly described,wi'-followss.,,.. �wd�
BEGINNING at a point in the west boundary,litie of the
Hardin Carter Survey, Abst. No. 281, and being the west y� b�
property line of the Nette Shultz property, same being w�
659 feet north, 0 deg. 27 min. east of the northeast
corner of Block F of the Brentwood Addition to the City
of Denton, Texas;
THENCE east from the beginning point along a 10 deg.
00 min. curve4 to the right, 56.50 feet to-a point of
tangency. _
THENCE south 51 deg., 10 min. east, 85.5T'•feet for a
point of curvature of a 12 deg. .00. min. curve to the
left;
THENCE along said 12. deg. 00 min. curve to the left,
198.06 feet to a point of tangency;
THENCE south 73 deg. 56 min. east, 1,017,77 feet for a
point; �• .
THENCE north 15 deg. 04 min. east, 80:feet for a point; '- }
THENCE north 7.3 deg. 5.6'min. west along the south boundary .
line of a sewer easement 20 feet wide granted to the City
of Denton, Texas, by Nette Shultz by instrument dated the
6th day of December, 1955, 1002.53 feet to a point of
curvature.of a 12 deg. 00 min. curve to the right;:'
THENCE along said 12 deg. 00 min. curve to the right,
198.06 feet to a point of tangency;
THENCE north 51 deg. 10 min. west, 72.87 feet fora point
of curvature of a 10 deg. 00 min. curve' t'o the left;
TIIENCE along said 10 deg. 00 min. curve to the left,
107.51 feet for a point in the west property line of the'
Shultz property and being in` the west survey line of the,-"
Hardin Carter Survey; ;h wYL
TIiENCE South 00, deg. 27 min. ;.Kest,. 92,89 feet to the
t place of beginning.
TO HAVE AND TO HOLD the same perpetually to the City of Denton,
Texas, its successors and assigns, and to its agents, officers and
employees, together with the right and privilege at any and all times
to enter said premises for the purpose of digging and maintaining -`
1 said drainage ditch.
WITNESS OUR HANDS at Denton, Texas, this _` day of
A. D., 1956.
f� e to Shultz .
Susiee Beyette
Callie 14. Ratliff !i ! ##
! THE STATE OF TEXAS 1
jCOUNTY OF DENTON
BEFORE NE, the undersigned authority, a Notary Public in and ':-
t
for said County and State, on this day personally appeared Nette Shultz,
I '
Susie Beyette and Callie E. Ratliff, each being a feme sole, all well i :..
known to me to be the persons whose names are subscribed to the forea
going instrument and acknowledged to me that they each executed the
same for the purposes and consideration Uerein expressed.,
GIVEN UNDER NY HAND AND SEAL OF OFFICE, this ..O*Y of
D., 1956. f
o ary Public in and for
j Denton County, Texas
T1iie Sute..•of Teat!
••,:nty .f!).'•(teen •1> �•A.J.BARNIS'iT,t7krk of the Ceninry i:n+rrt fa atwi fnr 4illd•Cmu1ry
• - .'rtr•�.:....'e lify thut:tfu• f iw(iiiw it rnWcr-"et-"o�ff writh"-,with it,crilifivate_of uWhMlieJirin wa.
i •veWJ the ..� _:.,:f,a tlf.. /LC/v..5. 1).. I ds7o, al-L4e .L.•k _ .Q �!
4-u"Je.1 she 4. «ic!d.IJZ+ 14-10 . U. lJ ��0.,at f J��_ e.'e!.• k f!. .�f.,
. W _...!� ...:-___..._ 1lrergrLs u) L:.•nh.0 f:nauty lrCet , pc
IVtieiw.+.my kA.%I end .eal`ai nllira-Nt (lenhae- •I;rva3,the 4LIV anuf year ianl al+vver tMIit1AA•• •-<.;..a++t. i •
i;. tlLe? e• ruf _Caval, IG%l:wueh f.n.r:.,f1 et.n l_ u.,T� ec_m i
C. F. BALLARD & ASSOCIATES, INC.
REGISTERED CIVIL ENGINEERS & SURVEYORS
218 NORTH AUSTIN PHONE (617) 387-0506
DENTON, TEXAS 76201
March 21 , 1974
REVISED FIELD NOTES :
DESCRIPTION OF 11.131 ACRE SECTION FOUR AVONDALE ADDITION TO DENTON:
All that certain tract or parcel of land situated in the City and County of Denton
Texas, owned by Builders Developers Company constituting SECTION FOUR OF AVONDALE
ADDITION to said City, and being more particularly described as follows:
BEGINNING at the Northernmost corner of Lot 19, Block J, of Section Two of said
Addition;
THENCE following the North line of Lots 20 through 28 of said Block J, the following
5 courses and distances : (1) N. 47° 08' 30" E. 109.5 feet 11
� (2) N. 64 20 41 E.
299.29 feet,
(3) N. 720 24' 34" E. 197.56 feet, (4) N. 780 11 ' 02" E. 176.64 feet,
and (5) N. 870 35' 12m E. 130.21 feet to a corner on the West line of Pickwick Lane:
THENCEN. 820 36' 24" E. 50.29 feet across Pickwick Lane to the Northwest corner
of Lot 1, Block R, SECTION FOUR:
THENCE N. 78° 51 ' 20" E. with the North line of Lots i and 2, a distance of 149.5
feet to a corner;
THENCE S. 650 51 ' 40" E. 53.63 feet to the Northwest corner of Lot-) 3, Block R;
THENCE N. 880 45' 40" E. 108.82 feet to the Northeast corner of Lot 3 on the West
line of Nottingham Drive;
THENCE S. 780 51 ' 03" E. across Nottingham Drive 72.12 feet to the Northwest
corner of Lot 1, Block Q;
THENCE N. 800 29" 21" E. 175.31 feet to the Northeast corner of Lot 1, Block Q;
THENCE S. 30 02' 30" W. with the East line of Section Four and crossing Windsor
Drive 401 .35 feet to the Southeast corner of Lot 6, Block P of this Section;
THENCE N. 85° 32' 50" W. 125.04 feet to the Southwest corner of Lot 6 on the East
line of Nottingham Drive;
THENCE S. 860 42' 24" W. across Nottingham Drive 60.37 feet to the Southeast
corner of Lot 20, Block H of this Section;
Avondale
A-126-0
1974
pg. 2. of F.N. to SECTION FOUR Avondale Addition
THENCE Westerly with the South lines of Lots 8 through 18, and 20 the following
6 courses and distances: (1) N. 850 40' 27" W. 347.45 feet, (2) S. 85° 04' W.
171 .86 feet (3) S. 79° 32' 10" W. 102.0 feet (4) S. 73° 38' 50" W. 102.02 feet
(5) S. 67° 50' 20" W. 102.02 feet and (6) S. 60° 44' W. 232.9 feet to the
Southernmost corner of Lot 8, herein, same being the Easternmost corner of Lot
7, Block 8, Section Two;
THENCE N. 420 53' 06" W. 122.5 feet to the Westernmost corner of Lot 8 on the
Southerly line of Windsor Drive;
THENCE N. 370 48' 31" W. across Windsor Drive 80.02 feet to the Southernmost
corner of Lot 20;
THENCE N. 420 59' 11" W. 127.79 feet to the place of beginning, containing in
all 11.131 acres of land.
TILL STATE OF TEXAS X
I KNOW ALL MEN BY THESE PRESENTS:
COUNTY OF DENTON X 1�.`�5 0
WHEREAS, on the 15th day of Januarv, 1964, Foxworth-Galbraith Lumber
( y executed, acknowledged and delivered to Builders Development Company,
-poration, a certain Deed, conveying a 153.86 acre tract of land, out of
;to John Carter, Hardin Carter, W. Pogue and S. McCracken Surveys, said Deed
being recorded in Volume 503, Page 64D of the Deed Records of Denton County,
Texas; and
WHEREAS, Builders Development Company, being the sole owner of said
,+:rty, desires to plat a portion of said property into an Addition to be
vtl as Avondale Addition, Section Four, to the City of Denton, Texas.
NOW, T'FIERErORE, KNOW ALL MEN BY THESE PRESENTS that Builders Development
Company, a corporation, acting herein, by and through its undersigned officers,
does hereby make and adopt the plat this day filed of the Hereinafter described
property, to be known as Avondale Addition, Section Four, to the City of Denton,
Texas, said property platted being more particularly described as follows:
BR(:TNWTNr Ft rY+�• Norther:-,.,1-at- corner of Lot 19, Block J,
of Avondale Addition, Section Two,
THENCE following the North line of Lots 20 through 28 of
said Block J, the following 5 courses and distances:
(1) N. 47° 05' 30" E. 109.5 feet, (2) N. 640 20' 41" E.
299.29 feet, (3) N. 720 24' 34" E. 197.56, feet, (4) N.
78" .11.' 02" E. 176.64 feet, and (5) N. 87" 35' 12" E.
130.21 feet, to a corner on the West line of Pickwick
Lane;
THENCE N. 820 36' 24" E. 50.29 feet across Pickwick Lane
to the Northwest. corner of Lot 1, Block R, of this Section;
THENCE N. 78° 51' 20" E. with the North line of Lots 1 and
2, a distance of 149.5 feet- to a corner;
THENCE S. 650 51' 40" E. 53,63 feet to the Northwest corner
of Lot 3, Block R of this Section;
THENCE, N. 880 45' 40" E. 108.82 feet to the Northeast corner
of Lot 3, on the West line of Nottingham Drive;
THENCE S. 78° 51' 03" E. across Nottingham Drive 72.12 feet
to the Northwest corner of Lot 1, Block Q of this Section;
THENCE N. 800 29' 21" E. 175.31 feet-, to the Northeast corner
of Lot 1, Block Q of this Section;
T11J'.NCEI S. 30 02' 30" W. with thc east l t.n.e of Sc,cLi on YOM: and
crossing Windr-oi. Drive 397.53 feet to the Soutih(,iAsL corner of
Lot (1, Block 1' of this Seet..ion;
Avondale
A-126-00
1A64
THENCE N. 86° 57' 30" W. 125.0 feet to the SOULhweSt corner of
Lot 6, on the; East line of Nottingham Drive,
ME NCE S. 86" 00' 52" W. across Nottingham Drivc 60.45 feet
to the Southeast corner of Lot 20, Block 11, of this Section;
Tl1ENCE Westerly with the South lines of Lots 8 through 18,
and 20, the following 6 courses and distances: (1) N. 850 IV
27" W. 347.45 feet, (2) S. 85° 04' W. 171.86 feet, (3) S. 79°
32' 10" W. 102.0 feet, (4) S. 730 38' 50" W. 102.02 feet,
(5) S. 670 50' 20" W. 102.02 feet and (6) S. 60' 44' W.
232.9 feet to the Southernmost corner of Lot 8, Block H,
herein, same being the Eata:ernmost corner of Lot 7, Block H.
Avondale Addition, Section Two;
THENCE N. 42" 53' 06" W. 122.5 feet to the Westernmost corner
! of Lot 8, Block li, on the Southerly line of Windsor Drive;
THENCE N. 370 48' 31" W. across Windsor Drive 80.02 feet to
the Southernmost corner of Lot 20, Block J, of this Section;
'ME NCE N. 42° 59' 11f1 W. 127.79 feet to the, place of beginning,
containing in all 11.125 acre of land, including all easements
as shown on the official plat of Section Four of Avondale Addition,
together with adjacent easements shown on said plat which may be
necessary for the installation of utilities in this Section.
The undersigned does hereby further dedicate the streets, as shown on said
plat, to the public use forever.
The undersigned owner hereby acknowledges the requirement of the completion
of all water distribution and sewage collection systems, and all street, curb
and gutter, and drainage improvements, at its expense and guarantees the per-
formance of same.
The undersigned owner further acknowledges that this plat is approved
subject to all platting ordinances, rules, regulations, and resolutions of the
City of Denton, Denton County, Texas.
The undersigned does further hereby reserve for utility and drainage pur-
poses, the easements, as shown on said plat of said Addition, together with
the right of ingress and egress on said easements for the purpose of the
erection, construction, repairs and maintenance of such drainage and utility-
facilities.
IN WITNESS WHEREOF, Builders Development Company has caused its name to
be set hereto and its seal to be affixeds the 13th day of September, 1973.
BUILDERS DEV1•JAMI.NT COMPANY
By
Prod dent. I
w GCS t'S�
TILE STATE OF TEXAS
COUNTY OF DALIAS
X BEFORE ;;� , the undersigned authority, a Notary
Public it; and for said Coui.�t_-y and State, on this
day personally appeared J. C. Galbraith, Jr.. , President of Builders Develop-
ment Company, known to me to be the person andl officer whose name is sub-
scribed to the fore:goI.ng i.nstrumoni., and acknowledged to me that the. same
was the act of said Builders Development. Company, a corporation, and that ..„
he executed the saute as thc-' act of such corporation for the purposes and
consideration therein expressed, .and in'the capacity therein stated.
1973.GIVEN UNDER MY BAND AND SEAL Or OFFICE, this 13th day of September,
1c !fir > f i.'f t Ar' rLLL wa irrt;
Notary Public n and for Dallas County,
gyp,.• %
s Texas.
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6153
THE STATE OF TEXAS
MOW ALL MEN BY THESE PRESENTS; ��7
COUNTY OF DENTON
THAT WE, Nette Shultz, Susie Beyette and Callie R. Ratliff,
each being a feme sole, of Denton County, Texas, for and in con-
sideration of the sum of One Dollar ($1.00) cash to us in hand _
paid and the benefits that will accrue to our property, the receipt It
of which is hereby acknowledged, do hereby GIVE AND GRANT unto the f
t �
said City of Denton, Texas, a Municipal Corporation, the 'right to
dig a drainage ditch and perpetually maintain an open drainage
ditch in, upon and across the following described tract of land,
being more particularly described as follows, to-wit:
All that certain lot, tract or parcel of land lying and
being situated in the County of Denton, State of Texas,
being out of the Hardin Carter Survey, Abstract No. 281,
and being more particularly described- as follows:
BEGINNING at a point in the most Southerly North line of ;
a certain 279.33 acre tract of land conveyed by Laura E.
Poe to Nette Shultz, that is South 86050.' West of an
inner Ell corner of said 279.83 acre tract, said point I
also being the Southwest corner of Lot No. 1, in Block
No. 7 of Norchester Subdivision;
THENCE South 8 deg. 40 min. East from said beginning E•
point, 195.9 feet for a point for a corner;
THENCE South 81 deg. 20 min. West 25 feet for a point for
a corner;
THENCE North 3 deg. 40 min. West 199.5 feet for a point for
a corner;
THENCE North 86 deg. 50 min. East 25.50 feet to the place k
of beginning. i
- t
The easement herein granted being a strip of land 25 feet
wide. .
4
TO HAVE AND TO HOLD the same perpetually to the City of Denton,
- t
Texas, its successors and assigns, and to its agents, officers and ; -
employees, together with the right and privilege at any and all
,
times to enter said premises for the purpose of digging and main-
taining said drainage ditch. j.
WITNESS OUR HANDS at Dentoa, 'Texas, this day of
A.D., 1957.
Nette Silultz Ily
sus le Eeye e
M171
APPENDIX 2
ASSESSMENT OF NON-FEDERAL SPONSOR'S
REAL ESTATE ACQUISITION CAPABILITY
COOPER CREEK SECTION 205 PROJECT
NON-FEDERAL SPONSOR: CITY OF DENTON, TEXAS
I. Legal Authority:
a. Does the sponsor have legal authority to acquire and hold title to real property for
project purposes?
Yes
b. Does the sponsor have the power of eminent domain for this project?
yes
c. Does the sponsor have "quick-take" authority for this project?
There is no "quick-take" authority under Texas law, however, possession of property
can be obtained without undue delay.
d. Are any of the lands/interests in land required for the project located outside the
sponsor's political boundary?
No. everything in city limits 4V N
e. Are any of the lands/interests in land required for the project owned by an entity
whose property the sponsor cannot condemn?
Two roads identified as potentially within the project area (Sherman Dr. And Locust Dr.)
are both owned by TxDOT.
II. Human Resource Requirements:
a. Will the sponsor's in-house staff require training to become familiar with the real
estate requirements of Federal projects including the Uniform Act?
No.
b. If the answer to Il.a. is "yes," has a reasonable plan been developed to provide such
training?
-will hire consultant
c. Does the sponsor's in-house staff have sufficient real estate acquisition experience to
meet its responsibilities for the project?
yes
d. Is the sponsor's projected in-house staffing level sufficient considering its other work
load, if any, and the project schedule?
e. Can the sponsor obtain contractor support, if required in a timely fashion?
-Planning to utilize contractor support for relocations
f. Will the sponsor likely request USACE assistance in acquiring real estate?
-No, not likely.
III. Other Project Variables:
a. Will the sponsor's staff be located within reasonable proximity to the project site?
-yes, all lands are within the City limits of Denton.
b. Has the sponsor approved the project/real estate schedule/milestones?
-Full schedule was not prepared. City officials provided typical periods of
performance for RE acquisition tasks. 30-60 days for survey/appraisal/title, 3-4 months
to acquire from offer to closing, condemnation typically requires 1 .5-2 years.
IV. Overall Assessment:
a. Has the sponsor performed satisfactorily on other USACE projects?
The City was the NFS on a previous section 205 planning report from the 80's as well
as ongoing coordination with USACE at Lewisville Lake.
b. With regard to this project, the sponsor is anticipated to be:
Capable
V. Coordination:
a. Has this assessment been coordinated with the sponsor?
- yes, assessment was performed via teleconference on Thursday, 26 September 2024.
b. Does the sponsor concur with this assessment?
Concur.
1. TITLE PAGE
REAL ESTATE COST STUDY
COOPER CREEK SECTION 20S
FLOOD DAMAGE REDUCTION PROJECT
DENTON (DENTON COUNTY) TEXAS
CONTINUING AUTHORITIES PROGRAM
NON-FEDERAL SPONSOR - CITY OF DENTON
Prepared for:
U.S. Army Corps of Engineers
Fort Worth District
Programs and Project Planning Division
Prepared By:
Clay Miller, Review Appraiser
U.S. Army Corps of Engineers
Fort Worth District
Real Estate Division
Effective Date: November 6, 2024
Date of Report: November 6, 2024
PROJECT: Real Estate Cost Estimate—Cooper Creek Section 205 Flood Damage Reduction Project, City of
Denton (Denton County)Texas
2. TABLE OF CONTENTS
1. TITLE PAGE................................................................................................................................................1
2. TABLE OF CONTENTS.................................................................................................................................2
3. SUMMARY.................................................................................................................................................2
4. PURPOSE OF COST ESTIMATE...................................................................................................................4
5. INTENDED USE OF COST ESTMATE/INTENDED USER................................................................................4
6. PROJECT SUMMARY..................................................................................................................................4
7. ESTATES OR PROPERTY RIGHTS ................................................................................................................4
8. SCOPE OF THE COST ESTIMATE.................................................................................................................5
9. DEFINITIONS..............................................................................................................................................5
10. LIMITING CONDITIONS AND ASSUMPTIONS...........................................................................................6
11. EXISTING EASEMENTS OR INTERESTS.....................................................................................................7
12. AREA, CITY, AND NEIGHBORHOOD DATA...............................................................................................8
13. PROPERTY DATA......................................................................................................................................8
14. HIGHEST AND BEST USE:.........................................................................................................................9
15. CONSIDERATION OF FEDERAL AND STATE RULES ..................................................................................9
16. VALUATION PROCESS..............................................................................................................................9
17. CORRELATION/RECONCILIATION..........................................................................................................11
18. DAMAGES/SEVERANCES.......................................................................................................................12
20. CONCLUSION.........................................................................................................................................13
22. AERIAL MAPS.........................................................................................................................................14
3. SUMMARY
As requested by the client, the estimated project real estate cost was developed for each
of the following three (3) alternatives.
1. Alternative 2A1 — Channel Improvement Easement on City Owned Tract PID 34607
• 0.82 acres $24,590
2. Alternative 2C1/2D1 — Fee Simple acquisition of Privately Owned Tract PID 39529
• 15.14 acres $484,715
3. Alternative 8A1 — Channel Improvement Easement on 21 Privately Owned Tracts
in Avondale Subdivision
• 1.837 acres $439,200
2
PROJECT: Real Estate Cost Estimate—Cooper Creek Section 205 Flood Damage Reduction Project, City of
Denton (Denton County)Texas
Damages/Severance
Scenario 1 $0
Scenario 2 $0
Scenario 3 $0
Minerals
Scenario 1 $0
Scenario 2 $0
Scenario 3 $0
Relocation (PL 91-646)
Scenario 1 $0
Scenario 2 $0
Scenario 3 $0
Other Costs
Scenario 1 $24,590 X 20% _ $4,918
Scenario 2 $484,715 X 20% = $96,943
Scenario 3 $439,200 X 20% = $87,840
Total Estimate by Scenario:
Scenario 1 $29,508
Land value $24,590
Damages/Severances $0
Minerals $0
Relocation $0
Other Costs $4,918
Scenario 2 $581,658
Land value $484,715
Damages/Severances $0
Minerals $0
Relocation $0
Other Costs $96,943
Scenario 3 $527,040
Land value $439,200
Damages/Severances $0
Minerals $0
Relocation $0
Other Costs $87,840
3
PROJECT: Real Estate Cost Estimate—Cooper Creek Section 205 Flood Damage Reduction Project, City of
Denton (Denton County)Texas
4. PURPOSE OF COST ESTIMATE
The purpose of this cost estimate is to develop for internal pre-planning purposes and
project feasibility purposes, an estimate of market value for each of the following three
(3) scenarios:
1. Alternative 2A1 — Channel Improvement Easement on City Owned Tract Out of
PID 34607 — 0.82 acres.
2. Alternative 2C1/2D1 — Fee Simple acquisition of Privately Owned Tract PID 39529
— 15.14 acres.
3. Alternative 8A1 — Channel Improvement Easement on 21 Privately Owned Tracts
in Avondale Subdivision — 80,000 square feet or 1.84 acres.
Project aerial maps are attached.
The Continuing Authorities Program (CAP) and Section 205 of the Flood Control Act of
1948, as amended, authorizes the U.S. Army Corps of Engineers to participate in the
development and implementation of structural and non-structural flood damage reduction
projects.
5. INTENDED USE OF COST ESTMATE/INTENDED USER
The values generated for each of the three (3) scenarios will be used by the intended
user (authorized personnel of the U.S. Corps of Engineers) for planning, development of
a project budget, and internal decision making.
6. PROJECT SUMMARY
A Project Management Plan (PMP) was not provided to the individual providing this cost
estimate. The principal objective of the project is flood damage reduction in the urbanized
Cooper Creek basin.
Alternative 2A1 is a 0.82-acre detention basin on city owned land. Alternative 2C1/2D1 is
a detention basin on a 15.14-acre tract that are currently privately owned. Alternative
8A1 is a 1.84-acre (1,000' x 80') channelization improvement easement that would travel
across a pre-existing drainage easement situated at the rear of 21 privately owned single
family lots that are situated along the current course of Cooper Creek.
7. ESTATES OR PROPERTY RIGHTS
The property rights analyzed are fee simple and channel improvement easement.
4
PROJECT: Real Estate Cost Estimate—Cooper Creek Section 205 Flood Damage Reduction Project, City of
Denton (Denton County)Texas
8. SCOPE OF THE COST ESTIMATE
This cost estimate is a pre-planning level estimate of the market value (fee simple or
easement) of properties identified as being necessary for the successful completion of
the project, taken "in gross", for the purposes for planning, development of a project
budget, and internal decision making. This real estate cost study was requested by the
Programs and Project Management Division of the Fort Worth District, U.S. Army Corps
of Engineers.
This cost study is not considered to be a USPAP compliant appraisal report. The person
preparing this cost estimate is familiar with the area but did not visit the subject project
for the purpose of preparing this estimate. A detailed highest and best use analysis was
not completed. Zoning was confirmed to provide a basis for highest and best use and
Denton Central Appraisal District (DCAD) records were researched to provide a basis for
real estate cost data. Individual market sales transactions were not researched or relied
upon for this estimate. The format and contents of this report are styled in conformity
with guidance received from USACE. A gross appraisal compliant with ER 405-1-04 and
reviewed and accepted for use by a Government Review Appraiser will be required to
proceed with the project.
9. DEFINITIONS
Fee Simple: ER 405-1-11 defines fee simple as:
"The fee simple title to the land described, subject, however, to existing easements
for public roads and highways, public utilities, railroads and pipelines."
Easement: The Dictionary of Real Estate Appraisal, Seventh Edition, Appraisal Institute,
Chicago, Illinois, 2022 defines an easement as:
"The right to use anthers land for a stated purpose."
Channel Improvement Easement: ER 405-1-11 defines a channel improvement easement
as:
A perpetual and assignable right and easement to construct, operate, and maintain
channel improvement works on, over and across (the land described in Schedule
A) (Tracts Nos and ) for the purposes as authorized by the
Act of Congress approved , including the right to clear, cut, fell,
remove and dispose of any and all timber, trees, underbrush, buildings,
improvements and/or other obstructions therefrom; to excavate, dredge, cut
away, and remove any or all of said land and to place thereon dredge or spoil
material; and for such other purposes as may be required in connection with said
work of improvement; reserving, however, to the owners, their heirs and assigns,
all such rights and privileges as may be used without interfering with or abridging
the rights and easement hereby acquired;subject, however, to existing easements
far public roads and highways, public utilities, railroads and pipelines.
5
PROJECT: Real Estate Cost Estimate—Cooper Creek Section 205 Flood Damage Reduction Project, City of
Denton (Denton County)Texas
Market Value: The Uniform Appraisal Standards for Federal Land Acquisition, The
Appraisal Foundation, 2016 Edition, Section 1, Paragraph 1.2.4, Page 10, defines market
value as:
"Market value is the amount in cash, or on terms reasonably equivalent to cash,
for which in all probability the property would have sold on the effective date of
value, after a reasonable exposure time on the open competitive market, from a
willing and reasonably knowledgeable seller to a willing and reasonably
knowledgeable buyer, with neither acting under any compulsion to buy or sell,
giving due consideration to all available economic uses of the property."
Neighborhood: The Dictionary of Real Estate Appraisal, Seventh Edition, Appraisal
Institute, Chicago, Illinois, 2022 defines a neighborhood as:
1. A group of complementary land uses; a congruous grouping of inhabitants,
buildings, and business enterprises.
2. A developed residential superpad within a master planned community usually
having a distinguishing name and entrance.
3. A geographic area around a property that influences that property, I.e. its
environment.
Highest and Best Use: The Uniform Appraisal Standards for Federal Land Acquisition, The
Appraisal Foundation, 2016 Edition, Section 4, Paragraph 4.3.1, Page 102, defines highest
and best use as:
"The highest and most profitable use for which the property is adaptable and
needed or likely to be needed in the reasonably near future."
10. LIMITING CONDITIONS AND ASSUMPTIONS
This real estate cost estimate is subject to the following assumptions and limiting
conditions.
• The estimator assumes no responsibility for matters legal in character nor do I
render any opinion as to the title, which is assumed to be good. All existing liens
and encumbrances have been disregarded, and the property is appraised as
though free and clear under responsible and competent management.
• The estimator made no survey of the property and assumes no responsibility in
connection with such matters.
• The estimator believes to be reliable the information identified in this report as
furnished by others but assumes no responsibility for its accuracy.
• Possession of the report, or copy thereof, does not carry with it the right of
publication, nor may it be reproduced in whole or in part, in any manner, by any
person, without the prior written consent of the author. Neither all nor any part of
the contents of the report shall be conveyed to the public through advertising,
public relations, news, sales, or other media without the prior written consent of
the author, particularly as to value conclusions, the identity of the appraiser, or
the Governmental body with which the estimator is connected.
6
PROJECT: Real Estate Cost Estimate—Cooper Creek Section 205 Flood Damage Reduction Project, City of
Denton (Denton County)Texas
• The estimator is not required to give testimony or attendance in court by reason
of this cost estimate, with reference to the property in question, unless
arrangements have been previously made, therefore.
• The distribution of the total valuation in this report between land and
improvements applies only under the existing program of utilization. The separate
valuations for land and building must not be used in conjunction with any other
estimate and are invalid if so used.
• Unless otherwise stated in this report, the existence of hazardous material used in
the construction, such as the presence of urea-formaldehyde foam insulation,
asbestos, the existence of radon gas, which may or may not be present on the
property, and/or underground petroleum storage tanks, was not observed by the
estimator. The estimator has no knowledge of the existence of such materials on
or in the property and is not qualified to detect such substances. The existence of
any such hazardous construction materials or potentially hazardous waste material
may have an effect on the value of the property. If such is present, the value of
the property may be adversely affected.
• The Americans with Disabilities Act (ADA) became effective January 26, 1992. The
estimator has not made a specific compliance survey and analysis of this property
to determine whether or not it is in conformity with the various detailed
requirements of the ADA. It is possible that a compliance survey of the property is
not in compliance with one or more of the requirements of the act. If so, this fact
could have a negative effect upon the value of the property. Since the estimator
has no direct evidence relating to this issue, I did not consider possible
noncompliance with the requirements of ADA in estimating the value of the
property.
• This report is prepared solely for the internal use of authorized personnel of
USACE, by the estimator in consideration of payment of a sum of money in the
form of salary paid by USACE and would not be prepared in the absence of such
consideration. This report is prepared solely for USACE and may not be relied upon
by any other person, entity, or organization for any other purpose whatsoever.
• In accordance with ER 405-1-04 (dated 29-3an-2016), 4-2, c. Exemptions from
USPAP and UASFLA, several USACE valuation assignments require quick and
sometime superficial estates of value, primarily for internal planning purposes and
are not under the purview of 49 C.F.R. Part 24 for acquisition appraisals. USACE
valuation assignments that fall within this exemption category include preliminary
estimates of value, cost estimates, feasibility reports, gross appraisals, and
informal value estimates.
11. EXISTING EASEMENTS OR INTERESTS
The properties currently identified on the project aerial maps and publicly and privately
owned. Although not identified at the current level of design, it is anticipated that
easements for power lines, roads, utilities, pipelines, and/or drainage may exist. An
Attorney's Opinion of Compensability would be necessary from the USACE Office of
Counsel to address any utilities that are impacted.
PROJECT: Real Estate Cost Estimate—Cooper Creek Section 205 Flood Damage Reduction Project, City of
Denton (Denton County)Texas
12. AREA, CITY, AND NEIGHBORHOOD DATA
The City of Denton is the county seat of Denton County and located in north Texas,
approximately 30 miles north of both Dallas and Fort Worth. It is included in the Dallas-
Fort Worth-Arlington Metropolitan Statistical Area (MSA). The city is located on IH-35
which traverses the United States from Mexico to Canada. The 2020 U.S. Census indicates
that Denton had a population of 139,869. This is a 23.4% increase over the 2010 Census
population of 113,383.
Denton is a home-rule city with a council-manager form of government. Residents elect
a mayor, four single-member district council members, and two at-large members. The
Denton City Council appoints the city manager. Council terms are for two years, with a
maximum of three consecutive terms, and elections are held each year in May. The city
is served by police, fire, Denton Municipal Electric (owned by the city), water, wastewater
and sanitary treatment facilities, natural gas (Oncor), and telephone. K-12 education is
provided by Denton ISD. The University of North Texas and Texas Women's University
are also located in Denton.
13. PROPERTY DATA
The subject property is located in the City of Denton, Texas and in general, follows the
course of Cooper Creek. The larger neighborhood impacted by the project is generally
described as being bounded by Loop 288 to the north and the east, U.S. Highway 380
(University Drive) to the south, and U.S. Highway 77 (N Elm Street) to the west.
Site:
Alternative 2A1 is a proposed 0.82 are detention pond located on Tax Parcel 34607, which
is owned by the City of Denton and currently used as a public park. Parcel 34607 currently
has PF (Public Facilities) zoning per City of Denton Development Services.
• Parcel 34607 is described as A0274A 1. CARTER, TR 22, 6.07 ACRES, OLD DCAD
TR 1A
Alternative 2C1/2D1 is a detention pond on a 15.14-acre tract, Tax Parcel 39529, which
is privately owned. This tract is currently vacant and is zoned PD with an R-7 residential
overlay per City of Denton Development Services.
• Parcel 39529 is described as A0186A BBB & CRR, TR 23,261 15.1395 ACRES
Alternative 8A1 is a 1.84-acre (1,000' x 80') channelization improvement easement that
would travel across a pre-existing drainage easement situated at the rear of 21 privately-
owned single-family lots that are situated along the current course of Cooper Creek.
These lots are part of the Avondale subdivision and most of the lots are currently
improved with single family dwellings.
8
PROJECT: Real Estate Cost Estimate—Cooper Creek Section 205 Flood Damage Reduction Project, City of
Denton (Denton County)Texas
The area sought for the project is not improved as it is assumed to encompass the areas
of the lots located in the pre-existing drainage easement. Lots impacted are as follows:
• Lots 7 thru 10 and Lot 23, Block A, Avondale 1, City of Denton, Denton County,
Texas
• Lots 8 thru 11, Block C, Avondale 1, City of Denton, Denton County, Texas
• Lots 5 thru 12, Block F, Avondale 2, City of Denton, Denton County, Texas
• Lots 1 thru 3, Block G, Avondale 2, City of Denton, Denton County, Texas
• Lots 4 and 5, Block G, Avondale 3, City of Denton, Denton County, Texas
Improvements: Based on a review of aerial photographs, the different land areas required
for the project are currently vacant.
Ownership Data:
Alternative 2A1, Parcel 34607 is owned by the City of Denton.
Alternative 2C1/2D1 Parcel 39529 is owned by Trans-Atlas Financial Inc.
Alternative 8A1 is owned by multiple private owners.
Environmental/Historical Issues: An ESA has not been provided to the individual preparing
this cost estimate.
14. HIGHEST AND BEST USE:
For Alternative 2A1, the highest and best use is continued use as a public park.
For Alternative 2C1/2D1, the highest and best use is residential development.
For Alternative 8A1, the highest and best use is single family residential use.
15. CONSIDERATION OF FEDERAL AND STATE RULES
The NFS (City of Denton) will acquire the property under State rules. Texas rules of
valuation differ from Federal rules primarily in that state rules do not allow enhancements
to offset the value of the part taken. In the state rule, such benefits may offset damages
only. This real estate cost estimate has been prepared under this assumption.
16. VALUATION PROCESS
Normally, a discussion of the 3 approaches to value (cost, income, and sales) are included
and reconciliation results is 1 or all approaches being identified as applicable. Given that
the properties are vacant, cost and income approaches are not applicable.
9
PROJECT: Real Estate Cost Estimate—Cooper Creek Section 205 Flood Damage Reduction Project, City of
Denton (Denton County)Texas
For this cost estimate, the client requested the development of market value estimate for
each of the following three (3) scenarios:
• Alternative 1 — what is the estimated value of a channelization improvement
easement to be located on 0.82 acres of public owned land in Tax Parcel 34607
• Alternative 2 — what is the estimated value of a fee simple acquisition of 15.14
acres of privately owned land (Tax Parcel 39529)
• Alternative 3 — what is the estimated value of a 1,000' x 80' (80,000 sf or 1.84
acres) channelization improvement easement to be located out of 21 tax parcels
with a pre-existing drainage easement in the Avondale subdivision.
Consistency is needed in order to address this request. As such, 2024 assessed land
values from the Denton Central Appraisal District records will be used.
The use of tax records in the development of a cost estimate is allowed in ER 405-1-04,
Paragraph 4-21 Gross Appraisal (a)(1) which states:
"Gross appraisals shall be as complete and descriptive as possible, but there is no
requirement for owner contact, and the appraiser may rely on tax records, cursory
inspections, or other suitable information for descriptions of improvements, as
detailed inspections may not be practical. "
Alternative 2A1:
This scenario requires a 0.82-acre channelization improvement easement of a 6.07-acre
tract owed by the City of Denton. The 2024 DCAD assessed land value is $202,248 for
6.07 acres, or $33,319 per acre. In this estimator's opinion the limitations placed on the
use of the property by a perpetual channelization improvement easement will restrict
90% of the usability. Therefore, for Alternative 2A1, the channelization easement has
been valued at 90% of the assessed unit value of the property.
0.82 Acres X $33,319/Acre X 90% _ $24,589.42
Say $24,590®
Alternative 2C1/2D1:
This scenario requires the fee simple acquisition of a 15.14-acre property that is privately
owned. The subject property is identified as DCAD Tax Parcel 39529. The 2024 DCAD
assessed land value is $484,715 for 15.14 acres, or $32,016 per acre. Therefore, for
Alternative 2C1/2D1, the total fee acquisition has been valued at 1000% of the assessed
value of the property.
$484,715
10
PROJECT: Real Estate Cost Estimate-Cooper Creek Section 205 Flood Damage Reduction Project, City of
Denton (Denton County)Texas
Alternative 8A1:
This scenario requires an 80,000 square foot of 1.84-acre channelization improvement
easement of 21 privately-owned single-family parcels in the Avondale subdivision. The
2024 DCAD assessed land values for the 21 parcels have bene summarized in the chart
below.
Parcel Legal Lot Size(SF) Land Imps Total Land$/SF
23403 AVONDALE 1 BLK A LOT 7 12,516 $93,446 $256,554 $350,000 $7.47
23414 AVONDALE 1 BLK A LOT 8 12,000 $92,434 $315,670 $408,104 $7.70
23417 AVONDALE 1 BLK A LOT 9 13,385 $95,152 $171,514 $266,666 $7.11
23431 AVONDALE 1 BLK A LOT 10 16,195 $100,666 $227,334 $328,000 $6.22
23454 AVONDALE 1 BLK A LOT 23 18,782 $105,743 $147,315 $253,058 $5.63
23485 AVONDALE 1 BLK C LOT 11 14,700 $97,733 $225,261 $322,994 $6.65
23488 AVONDALE 1 BLK C LOT 10 13,600 $95,574 $235,811 $331,385 $7.03
23070 AVONDALE 1 BLK C LOT 9 20,790 $109,684 $205,396 1 $315,080 $5.28
R
083 AVONDALE 1 BLK C LOT 8 18,500 $105,190 $281,769 $386,959 $5.69
673 AVONDALE 2 BLK F LOT 5 16,615 $101,491 $244,333 $345,824 $6.11
676 AVONDALE 2 BLK F LOT 6 13,650 $66,014 $245,876 $311,890 $4.84
679 AVONDALE 2 BLK F LOT 7(W 1/2) 6,343 $34,357 $1,776 $36,133 $5.42
682 AVONDALE 2 BLK F LOT 7(E 1/2),8 19,994 $108,122 $278,496 $386,618 $5.41
23691 AVONDALE 2 BLK F LOT 9(ALL),10(W 1/2) 13,650 $95,672 $185,946 $281,618 $7.01
23696 AVONDALE 2 BLK F LOT 10(E1/2),11 13,650 $95,672 $133,876 $229,548 1 $7.01
23703 AVONDALE 2 BLK F LOT 12 16,109 $100,498 $263,502 $364,000 $6.24
23148 AVONDALE 2 BLK G LOT 1 17,829 $103,873 $218,811 $322,684 $5.83
22638 AVONDALE 2 BLK G LOT 2 13,832 $96,029 $236,854 $332,883 $6.94
22644 AVONDALE 2 BLK G LOT 3 9,375 $50,044 $267,132 $317,176 $5.34
22648 AVONDALE 3 BLK G LOT 4 16,380 $10,103 $0 $10,103 $0.62
23004 AVONDALE 3 BLK G LOT 5 1 16,40 1 $68,820 1 $251,207 1 $320,027 1 $4.18
The assessed land values range from $0.62/SF to $7.70/SF, with a mean value of
$5.89/SF and a median value of $6.11/SF. If the highest and lowest indicator are
removed, then the mean is $6.07/SF and the mean is $6.11/SF. A single unit land value
of $6.10/SF has been selected as representative of the assessed unit value of the 21
individual tax parcels.
In this estimator's opinion the limitations placed on the use of the property by a perpetual
channelization improvement easement will restrict 90% of the usability. Therefore, for
Alternative 8A1, the channelization easement has been valued at 90% of the assessed
unit value of the property.
80,000 SF X $6.10/SF X 90% = $439,200
17. CORRELATION/RECONCILIATION
• Alternative 2A1 90% of $33,319 per acre
• Alternative 2C1/2D1 $32,016 per acre
• Alternative 8A1 90% of $6.10 per square foot
11
PROJECT: Real Estate Cost Estimate—Cooper Creek Section 205 Flood Damage Reduction Project, City of
Denton (Denton County)Texas
18. DAMAGES/SEVERANCES
Generally partial acquisition can result in a diminished market value for the remainder of
the area and result in severance and/or non-economic damages being paid for the
remnants and/or a tract that may become landlocked. For Alternative 2A1, given that the
tract identified for the project is already public owned, no damages or severance are
attributed to this scenario of the project. For Alternative 2C1/2D1, given that the proposed
acquisition would be a total acquisition of the fee simple estate, no damages or
severances are required. For Alternative 8A1, given that the land required for the project
is unimproved and already encumbered by a drainage easement, no damages or
severance are required.
19. INCREMENTAL REAL ESTATE COSTS
Relocation (PL 91-646h Government programs designed to benefit the public often result
in the acquisition of private property and occasionally the displacement of people from
their residences, businesses, non-profit organizations, or farms/ranches. To provide
uniform and equitable treatment for persons displaced, Congress passed the Uniform
Relocation Assistance and Real Property Acquisition Policies Act of 1970 and amended it
in 1987. This law is simply called the Uniform Act (PL 91-646). Given the tracts are vacant,
there are no relocations for this project.
Other Costs: In project cost estimates, there are various elements that are fluid and must
be based on assumptions and generalized data. Property lines have not been surveyed,
and detailed title research has not been performed. Complete inspections and
comparisons of individual properties are not practical at this time. The project, if
approved, will be implemented at an undetermined time in the future; and market
conditions cannot be exactly projected. For these reasons, I believe a contingency of 20%
is appropriate.
12
PROJECT: Real Estate Cost Estimate—Cooper Creek Section 205 Flood Damage Reduction Project, City of
Denton (Denton County)Texas
20. CONCLUSION
As requested by the client, the estimated project real estate cost was developed for each
of the following three (3) alternatives.
1. Alternative 2A1 — Channel Improvement Easement on City Owned Tract PID 34607
• 0.82 acres $24,590
2. Alternative 2C1/2D1 — Fee Simple acquisition of Privately Owned Tract PID 39529
• 15.14 acres $484,715
3. Alternative 8A1 — Channel Improvement Easement on 21 Privately Owned Tracts
in Avondale Subdivision
• 1.837 acres $439,200
Damages/Severance
Scenario 1 $0
Scenario 2 $0
Scenario 3 $0
Minerals
Scenario 1 $0
Scenario 2 $0
Scenario 3 $0
Relocation (PL 91-646)
Scenario 1 $0
Scenario 2 $0
Scenario 3 $0
Other Costs
Scenario 1 $24,590 X 20% _ $4,918
Scenario 2 $484,715 X 20% = $96,943
Scenario 3 $439,200 X 20% = $87,840
13
PROJECT: Real Estate Cost Estimate—Cooper Creek Section 205 Flood Damage Reduction Project, City of
Denton (Denton County)Texas
Total Estimate by Scenario:
Scenario 1 $29,508
Land value $24,590
Damages/Severances $0
Minerals $0
Relocation $0
Other Costs $4,918
Scenario 2 $581,658
Land value $484,715
Damages/Severances $0
Minerals $0
Relocation $0
Other Costs $96,943
Scenario 3 $527,040
Land value $439,200
Damages/Severances $0
Minerals $0
Relocation $0
Other Costs $87,840
I certify that I have no personal interest, present or prospective, in the property, or
with the owners thereof. The value reported represents my best unbiased judgement.
Pursuant to ER 405-1-04, Paragraph 4-17, this estimate is exempt from the provisions
of USPAP by virtue of a Jurisdictional Exception.
MILLER.WILLIAM Digitally signed by
MILLERMILLIAM.CLAYTON.
.0 LAYTO N.
Date:2024.11.06 15:56:34
442074 -06,00,
November 6, 2024 Clay Miller
Review Appraiser
USACE, Fort Worth District
22. AERIAL MAPS
14
PROJECT: Real Estate Cost Estimate—Cooper Creek Section 205 Flood Damage Reduction Project, City of
Denton (Denton County)Texas
Alternative 2A1
w
J•1or
70
i
15
PROJECT: Real Estate Cost Estimate—Cooper Creek Section 205 Flood Damage Reduction Project, City of
D- •n (Denton County)
Alternative 1
Ail
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16
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PROJECT: Real Estate Cost Estimate—Cooper Creek Section 205 Flood Damage Reduction Project, City of
D- •n (Denton County)
Alternative 8A1
17
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Appendix H : Hazardous, Toxic,
Radioactive Waste
Cooper Creek, Denton, TX
Section 205
Closeout Report
February 2025
1.0 Introduction
In order to complete a feasibility level Hazardous, Toxic and Radioactive Waste(HTRW)evaluation
for the Cooper Creek CAP 205 project, a report was completed following the rules and guidance of ER
1165-2-132:HTRW Guidance for Civil Works Projects and ASTM E1527-13 Standard Practice for
Environmental Site Assessments:Phase I Environmental Site Assessment Process. The purpose of this
search was to identify any sites with recognized environmental conditions (RECs)where hazardous
substances or petroleum products have been released or are likely to have been released to soil,
groundwater, or surface water in the proposed project area.
2.0 Search Parameters
A desktop records review was conducted using various sources to determine the presence of HTRW
sites on or near the project footprint. This search was focused on active cleanup sites and sites with a
reasonable risk of HTRW release. Several databases were searched manually to narrow down the
search area. These databases included the Environmental Protection Agency(EPA) Cleanups in my
Community database,the EPA Envirofacts database,the Texas Commission on Environmental
Quality's(TCEQ)Central Registry, and the Texas Railroad Commission's (RRC) oil and gas well
Public GIS Viewer. The information collected from this desktop records review was analyzed for
recognized environmental conditions(RECs)that would affect the proposed project or need further
investigation,given the proposed project measures.
3.0 Search Results
Federal National Priorities List(NPL)—The National Priorities List(NPL)is the list of sites of
national priority among the known releases or threatened releases of hazardous substances,pollutants,
or contaminants throughout the United States and its territories. The NPL is intended primarily to guide
the EPA in determining which sites warrant further investigation. The records search did not reveal any
NPL sites in the project footprint or adjacent areas. This is based on a search of the EPA Superfund
National Priorities List(NPL) map viewer.
Federal Comprehensive Environmental Response, Compensation, and Liability Information System
(CERCLIS)List—The CERCLIS database,now called the Superfund Enterprise Management System
(SEMS),tracks hazardous waste sites where remedial action has occurred under EPA's
Comprehensive Environmental Response,Compensation, and Liability Act(CERCLA)program. This
list also includes sites that are in the screening and assessment phase for possible inclusion on the
NPL. The records search of EPA's listed SEMS sites did not reveal any sites in the project footprint or
adjacent areas. This is based on a search of the EPA SEMS database.
Federal No Further Remedial Action Planned(NFRAP)List—The Federal NFRAP list(now known as
the SEMS archive list)tracks sites where no further remedial action is planned,based on available
assessments and information. The list also represents sites that were not chosen for the NPL. Further
EPA assessment could possibly be ongoing, and hazardous environmental conditions may still exist;
however, in the absence of remedial action and assessment data,no determination about environmental
hazards can be made. The records search did not reveal any NFRAP sites in the project footprint or
adjacent areas. This is based on a search of the EPA SEMS database.
Federal Resource Conservation and Recovery Act (RCRA) Corrective Action List — The records
search identified 1 site with corrective actions under RCRA within the project footprint or adjacent areas.
Safety-Kleen Systems is half a mile from the Creek but this case is inactive currently and not anticipated
to impact the project. This is based on a search of the EPA Cleanups in My Community map viewer.
State Superfund Sites- This search is to check for any state CERCLA sites in the project vicinity. The
records search of state CERCLA cleanup sites did not show any sites of concern in the project or
adjacent areas. This search is based on a search of the Texas Commission on Environmental Quality
Superf ind Sites database.
State and Tribal Solid Waste Facilities/Landfill Sites—This search is designed to check any state or
tribal databases for solid waste handling facilities or landfills in the project vicinity. The records search
did not find any solid waste facilities or landfill sites in area of this project or adjacent areas. This is
based on a search of the TCEQ Municipal Solid Waste Viewer.
State and Tribal Registered Storage Tanks—This list is a combination of the State of Texas registered
Underground Storage Tank(UST)and Above-ground Storage Tank(AST) databases,representing
sites with storage tanks registered with the State of Texas. The search revealed 6 open/active USTs
within one mile of the project area(Figure 1). Records indicate 3 reported releases; all 3 show a status
of"No Further Action",indicating the regulatory agency was satisfied with the response measures.
The nearest open/active USTs are approximately 0.5 miles from the creek and recommended to be
avoided in construction footprint, otherwise additional investigation and response will be required.
Due to the distances from the proposed project and the closed NFA status for the releases,none of these
tanks are expected to pose an impact to the project. Therefore,no registered storage tanks will be
carried forward as RECs. These results are based on searches of the TCEQ Petroleum Storage Tank
Viewer and EPA UST Finder databases.
Toxic Release Inventory Sites- The Toxics Release Inventory(TRI)Database provides reports on
releases,transfers, and waste managed for chemical releases reported. There are four sites that are
within 1 mile of the project area but all were either closed or inactive and will not be considered as a
REC. This was based on a search of the EPA TRI Explorer database.
State and Tribal Voluntary Cleanup Sites—The TCEQ Voluntary Cleanup Program(VCP) database
identifies sites where the responsible party chooses to clean up the site themselves with TCEQ
oversight.No sites from this database were identified within one mile of the work area,based on a
search of the TCEQ Voluntary Cleanup Program using the Central Registry(CR) Query.
Brownfields List—A Brownfield is a property, the expansion,redevelopment, or reuse of which may
be complicated by the presence or potential presence of a hazardous substance,pollutant, or
contaminant.No sites from this database were identified within one mile of the work area,this was
based on a search for Brownfields sites using the EPA Cleanups in My Community database.
Oil and Gas Wells—A search for oil and gas wells in the project area using the RRC website identified
multiple oil and gas sites including wells and pipelines within the surrounding area(Figure 3).
Although not classified as HTRW under USACE regulations,pipelines and oil wells play an important
role in the HTRW existing conditions near the potential project area. This is because the well and/or
pipeline contents could potentially leak or spill into the surrounding environment or be struck by a
contractor's equipment during construction of the proposed project features. Precise locations for oil
and gas infrastructure should be obtained during the Pre-construction Engineering and Design phase
and additional environmental testing of soils may be necessary depending on the location of oil and gas
wells and if they are within the project footprint. The Railroad Commission(RRC)Public GIS Viewer
was used to map these findings.
4.0 Conclusion
No Recognized Environmental Conditions were identified within one mile of the project area that could
be reasonably expected to affect the Cooper Creek CAP 205 project.Although not classified as HTRW
under USACE regulations, several oil and gas infrastructure sites were identified within the
surrounding area. As a result of these findings,pipelines and wells within the project vicinity and along
potential site access routes should be precisely located during PED to ensure no unintended interaction
occurs with the existing oil and gas facilities.
Despite the lack of identified sites that could be reasonably expected to affect the project,there is
always a possibility that previously unidentified HTRW could be uncovered, even when a proposed
project is entirely within a pre-existing project footprint.An updated HTRW survey will be required
should the project be reconsidered and funded at a future time.Additionally, care should be taken to
identify and address HTRW concerns that may arise in a timely manner, so as not to affect proposed
project timelines.
Figure 2: HTRW Sites
Cooper Creek HTRW Sites
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Figure 3: Oil & Gas Wells and Pipelines
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