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Powder/Tongue River Basin Water Plan
Technical Memoranda
| SUBJECT: |
Appendix S
Future Water Use Opportunities |
|
| PREPARED BY: |
HKM Engineering Inc. |
|
| DATE: |
February 2002 |
INTRODUCTION
The purpose of this task is to identify future water use opportunities that can be implemented to satisfy
present and projected water demands in the Little Bighorn River, Tongue River, and Powder River Basins
in Wyoming. The list of opportunities compiled under this task is intended to be used by individuals and
organizations that need to develop a water supply to satisfy their specific needs.
To further assist the users of this list to identify potential opportunities to satisfy their demands, a
methodology is presented that can be employed to evaluate a specific opportunity on the list relative to
similar and related opportunities. The suggested methodology evaluates opportunities according to the
likelihood they are desirable, functional, and capable of receiving the support required for development.
By using the list of future water use opportunities and employing the evaluation methodology, individuals
and organizations will have "a place to start" in their investigation to develop a water supply to satisfy
their specific needs.
The procedure used to complete this task consists of the following four steps:
- Develop screening criteria to evaluate future water use opportunities;
- Develop a long-list of future water use opportunities;
- Develop a short-list of opportunities; and,
- Evaluate the opportunities on the short-list.
These steps and the results of this task are described in the remainder of this technical memorandum.
SCREENING CRITERIA
A significant task of the river basin planning process is the development of screening criteria and methods
for evaluating future water use opportunities identified and listed for the study basins. For the
Powder/Tongue River Basins, the screening criteria and evaluation method developed for the Green River
Basin Plan were presented to the Basin Advisory Group (BAG) for consideration, modification, and
adoption at a BAG meeting held October 10, 2001. The criteria adopted by the BAG, and a description of
each criterion, is presented below:
Criterion 1: Water Availability
This criterion reflects the general ability of a project to function, given likely bypasses for
environmental uses and prior rights. It is not a reflection of the relative size of the
project.
Criterion 2: Financial Feasibility
This criterion reflects the effects of the combination of technical feasibility (high or low
construction cost) and economic use to which the water would be put (e.g. irrigation of
native meadow vs. cultivation of alfalfa or row crops). The intent of this criterion is to
indicate the likely ability to afford the project or meet Wyoming Water Development
Commission (or other) funding source criteria. A low number represents a project with
suspect ability to be repaid, whereas a high number represents a project that should more
easily meet funding and repayment requirements.
Criterion 3: Public Acceptance
This criterion reflects the extent to which a project will encounter or create public
controversy (low number) versus a project that would likely engender broad public
support (high number). For example, on-stream storage in environmentally sensitive
areas would be very controversial, while off-channel storage in less sensitive areas would
more likely be supported.
Criterion 4: Number of sponsors/beneficiaries/participants
This criterion reflects the desirability, all other things being equal, that a project serving a
larger segment of the population should be evaluated higher (higher number) than one
serving only a few (lower number).
Criterion 5: Legal/Institutional concerns
This criterion reflects the perceived relative ease (high number) or difficulty (low
number) with which a project could be authorized and permitted under existing state and
federal law.
Criterion 6: Environmental/Recreation benefits
This criterion reflects the net effect of positive environmental and recreational aspects of
a project as offset, to the extent it can be determined, by potential negative impacts on
these attributes.
LONG-LIST OF FUTURE WATER USE OPPORTUNITIES
Compiling the long-list of future water use opportunities began with a review of published reports
available for the study basins. The level of information and data available for the projects identified
through the literature review varied from very sketchy to completed conceptual designs.
Specific groundwater development projects were not identified and included on the long-list. However,
groundwater development is included as a generic future water use opportunity for each of the sub-basins
and was considered along with the surface water opportunities. Similarly, groundwater produced in the
development of coalbed methane was not included on the long-list. Although this resource has the
potential to supply small, localized demands over the short-term, the feasibility of developing a
significant water supply from this activity is considered to be limited because of the wide geographic
dispersion of the wells and the projected short time of operation.
Water right permit applications have been submitted to the State Engineer for many of the projects
included on the long-list. Some of the applications have been approved and the State Engineer has
granted permits authorizing project development. The majority of the projects, however, have not been
elevated to permit status and the applications remain in the pending status.
Water right information was not compiled for the projects nor was water right status considered in the
subsequent evaluations of the projects. Each of the projects on the long-list were evaluated under the
assumption a water right for the project could be perfected and conflicts with competing water rights
could be resolved. Consideration was given to simply compiling the water right status for information
only and not for the purpose of evaluation. However, this task proved to be beyond the scope of this river
basin planning study and, more important, the information derived from this effort promised to be more
confusing than useful.
Another future water use opportunity in the Powder/Tongue River Basins is the establishment of instream
flow water rights. These water rights are developed through a specified procedure that begins when the
Wyoming Game and Fish Department proposes a stream segment for an instream flow water right. The
segment is then studied by the Water Development Commission, and the water right is granted or rejected
by the State Engineer. This opportunity is not, however, included on the long-list since the segments that
have been proposed are either under investigation, have been granted, or have been rejected. As new
segments are nominated they will be advanced through the process.
The initial long-list was presented to the BAG at a meeting held October 10, 2001, and distributed to
BAG members with a memorandum dated October 19, 2001. BAG members were asked to review the
list and identify potential opportunities not included on the initial draft of the long-list.
Comments and suggestions received from BAG members and additional research led to the development
of the final long-list. This list is presented in Appendix A, and the future water use opportunities included
on the long-list are shown on Figure 1.

Click To Enlarge
SHORT-LIST OF FUTURE WATER USE OPPORTUNITIES
Projects and opportunities on the long-list were reviewed to determine if they should be included on the
short-list or if they should be eliminated from consideration during the 30-year planning period. Reasons
considered to eliminate projects include: 1) the project has already been constructed; 2) the location of
project facilities, i.e. within a National Forest or wilderness area, presents major legal, institutional, and
permitting constraints; and, 3) the original demand for the project no longer exists and is not expected to
appear within the planning period.
The initial long-list presented to the BAG on October 10th and distributed to the BAG on October 19th
identified opportunities proposed to not be included on the short-list. Reasons for eliminating projects
from short-list consideration were provided. Again, BAG members were asked to review the proposed
eliminations and provide comments.
Comments and suggestions received from BAG members and additional research led to the development
of the final short-list.
SHORT-LIST EVALUATION METHODOLOGY
The methodology described in this section is intended to assist the user of the short-list of future water
use opportunities. The process described can be employed to establish "a place to start" in the quest to
match specific water demands to future water use opportunities.
The process begins after the short-list of future water use opportunities has been prepared. The result of
the process is an evaluation of opportunities according to their relative likelihood they are desirable,
functional, and capable of receiving enough public support to be implemented. In general, the results
present an overall picture of the favorability of a future water use opportunity or project.
The first step in the process is to categorize the future water use opportunities into one of the four types
described below:
Type 1: Rehabilitation projects that preserve existing uses.
Type 2: Projects that rectify existing shortages.
Type 3: Projects that meet projected future demands.
Type 4: Projects that enhance uses in other Wyoming basins.
By categorizing the short-list projects into one of these four types, projects are evaluated only relative to
similar type projects. Furthermore, the projects are grouped by sub-basin to allow planning evaluations
by geographic locale.
After the short-list projects have been assigned to a type category, the six evaluation criteria were used to
evaluate the projects under each of the types.
The evaluation process entails assigning a weight value to each of the criteria. These values range from a
weight of 10 for criteria judged to be very important, to a weight of 1 if the criterion is not considered
significant. Different criterion weight values are assigned for each of the four type categories. For
example, Criterion 1: Water Availability is not significant for Type 1 projects, since these projects already
have an established water supply, and will be assigned a low weight value. Conversely, this criterion is
very important for projects categorized under Types 2, 3, and 4, and will be assigned higher weight
values.
Each project is then assigned an evaluation score for each of the six criteria. These scores range from a
high of 10 if the project is very favorable for that criterion, to a low score of 0 if the project is very
unfavorable. Scoring a project under each criterion is accomplished relative to the other projects in the
same type category. For example, consider Project X and Project Y that are categorized as Type 2
projects and the evaluation of these two projects concludes Project X will result in more environmental
and recreational benefits (Criterion 6). Therefore, Project X will receive a higher score than Project Y
under Criterion 6 with the difference in scores reflecting the degree to which Project X provides more
environmental and recreational benefits than Project Y.
The total evaluation score for a project is then computed as the sum of the products of the weight value
and the evaluation score. Projects achieving a higher total score are considered to be more desirable,
more functional, and have a higher capability of receiving enough public support to be implemented,
relative to the other projects in the same type category.
As previously stated, the level of information and data available for the projects on the list of future water
use opportunities varies significantly from very sketchy to completed conceptual designs. Therefore, the
exercise of assigning weights to criterion and evaluation scores to projects is totally subjective and the
results of the evaluation process can only be interpreted to reflect the knowledge and judgement of the
individual assigning the weights and scores. In order to make the process more objective and less
subjective, detailed engineering, legal, and environmental investigations would need to be completed to
advance all projects to the same level of information and data.
The suggested evaluation process described above was applied to the short-lists of future water use
opportunities to provide an example of the thought process followed in its application. The results of the
application of the process are presented in Tables 1, 2, 3, 4, 5, and 6 for each of the six basins of the
planning area.
It must be emphasized the six evaluated short-list tables reflect the knowledge and judgement of the
individual that performed the exercise. When another individual having different opinions and a different
level of knowledge of the projects being evaluated completes the exercise, different total scores will likely
result. Variable results will be achieved because different weights will be assigned to the evaluation
criteria and different scores will be assigned to the projects.
Given this intrinsic characteristic of the evaluation methodology, it is difficult if not impossible to use the
resulting evaluated short-lists for anything other than to establish "a place to start" the required
investigations leading to the selection of a future water use opportunity compatible with the specific water
demands of the reviewer. The evaluated short-lists simply aren't appropriate to be used by the Wyoming
Water Development Commission or any other funding entity to prioritize funding awards.
Table 1
Evaluated Short-List: Little Bighorn River Basin
|
|
|
Project Evaluation Criteria |
|
Project Type (see below) Project Title |
Map Loc. No. |
Est. Yield(y), Cap(c) or Depl(d) (AF) |
Water Availability |
Financial Feasibility |
Public Acceptance |
No. of Sponsors/ Beneficiaries |
Legal/ Institutional Constraints |
Environmental/ Recreation Benefits |
Total Score |
| Type 1 (None) |
|
|
|
|
|
| Type 2 (None) |
|
|
|
|
|
| Type 3 |
|
|
6 |
5 |
6 |
5 |
8 |
6 |
|
| BEPC Sunrise Project |
2 |
82,110 c |
6 |
7 |
7 |
5 |
5 |
6 |
214 |
| Little Bighorn River Export System |
1,6 |
29,600 y |
8 |
7 |
6 |
7 |
3 |
5 |
208 |
| Groundwater Development |
|
unk |
5 |
6 |
8 |
4 |
7 |
4 |
208 |
| Half Ounce Reservoir |
5 |
10,000 y |
8 |
6 |
4 |
5 |
5 |
3 |
185 |
| Twin Creek Reservoir |
2 |
38,588 c |
8 |
6 |
4 |
4 |
4 |
4 |
178 |
| Fuller No. 1 Reservoir |
3 |
22,829 c |
4 |
3 |
5 |
4 |
5 |
5 |
159 |
| Fuller No. 2 Reservoir |
4 |
1,549 c |
4 |
3 |
5 |
4 |
5 |
4 |
153 |
| Type 4 (None) |
|
|
|
|
|
Notes:
1. Each criteria has a different weighting for each type of project; 10 is most important, 1 is least important
2. Under each project, the criteria are individually scored; 10 means largely favorable, 0 is unfavorable
3. Total scores are the additive result of multiplying each project criteria weighting by the associated project type criteria score
Type 1: Rehabilitation projects that preserve existing uses
Type 2: Projects that rectify existing shortages
Type 3: Projects that meet projected future demands
Type 4: Projects that enhance uses in other Wyoming basins |
Table 2
Evaluated Short-List: Tounge River Basin
|
|
|
Project Evaluation Criteria |
|
Project Type (see below) Project Title |
Map Loc. No. |
Est. Yield(y), Cap(c) or Depl(d) (AF) |
Water Availability |
Financial Feasibility |
Public Acceptance |
No. of Sponsors/ Beneficiaries |
Legal/ Institutional Constraints |
Environmental/ Recreation Benefits |
Total Score |
| Type 1 |
|
|
|
|
| Misc. Canal Rehab (Conservation) |
|
unk |
Not Ranked, only one project of this type |
|
| Type 2 (None) |
|
|
|
|
| Sheridan Canal System |
13 |
unk |
Not Ranked, only one project of this type |
|
| Type 3 |
|
|
6 |
8 |
6 |
7 |
6 |
6 |
|
| Upper State Line Reservoir |
10 |
75,000 y |
8 |
6 |
7 |
7 |
6 |
7 |
265 |
| Lower State Line Reservoir |
12 |
88,000 y |
8 |
6 |
7 |
7 |
6 |
7 |
265 |
| Jones Draw Reservoir |
16 |
2,500 y |
5 |
5 |
8 |
8 |
7 |
4 |
240 |
| West Fork Reservoir |
17 |
2,500 y |
5 |
5 |
8 |
8 |
7 |
4 |
240 |
| Prarie Dog Reservoir |
11 |
20,000 y |
6 |
4 |
7 |
4 |
6 |
6 |
210 |
| Rockwood Reservoir |
9 |
93,000 y |
7 |
7 |
4 |
5 |
3 |
5 |
205 |
| Groundwater Development |
|
unk |
4 |
4 |
9 |
4 |
6 |
4 |
198 |
| North Fork Reservoir |
7 |
21,600 y |
7 |
5 |
5 |
4 |
3 |
5 |
188 |
| South Fork Reservoir |
8 |
13,200 y |
7 |
5 |
5 |
4 |
3 |
5 |
188 |
| Shutts Flats Reservoir |
14 |
7,600 y |
7 |
4 |
5 |
4 |
3 |
5 |
180 |
| Type 4 (None) |
|
|
|
|
|
Notes:
1. Each criteria has a different weighting for each type of project; 10 is most important, 1 is least important
2. Under each project, the criteria are individually scored; 10 means largely favorable, 0 is unfavorable
3. Total scores are the additive result of multiplying each project criteria weighting by the associated project type criteria score
Type 1: Rehabilitation projects that preserve existing uses
Type 2: Projects that rectify existing shortages
Type 3: Projects that meet projected future demands
Type 4: Projects that enhance uses in other Wyoming basins |
Table 3
Ranked Short-List: Clear Creek Basin
|
|
|
Project Evaluation Criteria |
|
Project Type (see below) Project Title |
Map Loc. No. |
Est. Yield(y), Cap(c) or Depl(d) (AF) |
Water Availability |
Financial Feasibility |
Public Acceptance |
No. of Sponsors/ Beneficiaries |
Legal/ Institutional Constraints |
Environmental/ Recreation Benefits |
Total Score |
| Type 1 (None) |
|
|
|
|
|
| Type 2 (None) |
|
|
|
|
|
| Type 3 |
|
|
6 |
8 |
6 |
7 |
6 |
6 |
|
| Lake DeSmet Enlargements |
21 |
239,243 c |
8 |
9 |
7 |
5 |
7 |
4 |
263 |
| Lower Clear Creek Reservoir |
26 |
30,300 y |
8 |
5 |
6 |
6 |
6 |
7 |
244 |
| B.C.L. Company Reservoir |
25 |
29,300 c |
7 |
5 |
6 |
6 |
6 |
7 |
238 |
| Tex Ellis Reservoir |
27 |
17,100 y |
7 |
4 |
7 |
6 |
7 |
6 |
236 |
| Tie Hack Reservoir Enlargement |
34 |
7,500 c |
4 |
5 |
7 |
8 |
4 |
7 |
228 |
| Groundwater Enlargement |
|
unk |
4 |
3 |
7 |
3 |
6 |
5 |
177 |
| Little Sour Dough Reservoir |
19 |
1,642 c |
4 |
3 |
4 |
3 |
3 |
4 |
135 |
| Camp Comfort Reservoir |
20 |
11,640 c |
4 |
3 |
4 |
3 |
3 |
4 |
135 |
| South Rock Creek Reservoir |
28 |
13,300 c |
4 |
3 |
4 |
3 |
3 |
4 |
135 |
| Trangle Park Reservoir |
29 |
3,000 c |
4 |
3 |
4 |
3 |
3 |
4 |
135 |
| Canyon Reservoir |
30 |
5,000 c |
4 |
3 |
4 |
3 |
3 |
4 |
135 |
| South Clear Creek Reservoir |
31 |
5,000 c |
4 |
3 |
4 |
3 |
3 |
4 |
135 |
| Lynx Park Reservoir |
32 |
10,700 c |
4 |
3 |
4 |
3 |
3 |
4 |
135 |
| Sour Dough Creek Reservoir |
33 |
4,500 c |
4 |
3 |
4 |
3 |
3 |
4 |
135 |
| Type 4 (None) |
|
|
|
|
|
Notes:
1. Each criteria has a different weighting for each type of project; 10 is most important, 1 is least important
2. Under each project, the criteria are individually scored; 10 means largely favorable, 0 is unfavorable
3. Total scores are the additive result of multiplying each project criteria weighting by the associated project type criteria score
Type 1: Rehabilitation projects that preserve existing uses
Type 2: Projects that rectify existing shortages
Type 3: Projects that meet projected future demands
Type 4: Projects that enhance uses in other Wyoming basins |
Table 4
Ranked Short-List: Crazy Woman Creek Basin
|
|
|
Project Evaluation Criteria |
|
Project Type (see below) Project Title |
Map Loc. No. |
Est. Yield(y), Cap(c) or Depl(d) (AF) |
Water Availability |
Financial Feasibility |
Public Acceptance |
No. of Sponsors/ Beneficiaries |
Legal/ Institutional Constraints |
Environmental/ Recreation Benefits |
Total Score |
| Type 1 (None) |
|
|
|
|
|
| Type 2 (None) |
|
|
6 |
7 |
5 |
6 |
4 |
3 |
|
| Hazeltonm Watershed Site "B" |
39 |
3,000 acres |
5 |
7 |
5 |
7 |
4 |
4 |
174 |
| Doyle Creek Reservoir |
42 |
3,000 acres |
5 |
7 |
5 |
7 |
4 |
4 |
174 |
| Hazelton Watershed Site "A" |
38 |
1,580 acres |
7 |
5 |
6 |
5 |
3 |
3 |
158 |
| Type 3 |
|
|
6 |
8 |
5 |
6 |
5 |
6 |
|
| Crazy Woman Reservoir |
36 |
10,500 y |
7 |
6 |
6 |
6 |
5 |
5 |
211 |
| Lower Crazy Woman Reservoir |
40 |
67,200 y |
7 |
4 |
6 |
7 |
4 |
6 |
202 |
| North Fork Crazy Woman Reservoir |
37 |
2,759 c |
6 |
5 |
5 |
4 |
6 |
4 |
179 |
| Enl. Negro Creek Reservoir |
35 |
13,900 y |
7 |
5 |
5 |
5 |
3 |
4 |
161 |
| Groundwater Development |
|
unk |
4 |
3 |
7 |
3 |
6 |
5 |
161 |
| Type 4 (None) |
|
|
|
|
|
Notes:
1. Each criteria has a different weighting for each type of project; 10 is most important, 1 is least important
2. Under each project, the criteria are individually scored; 10 means largely favorable, 0 is unfavorable
3. Total scores are the additive result of multiplying each project criteria weighting by the associated project type criteria score
Type 1: Rehabilitation projects that preserve existing uses
Type 2: Projects that rectify existing shortages
Type 3: Projects that meet projected future demands
Type 4: Projects that enhance uses in other Wyoming basins |
Table 5
Ranked Short-List: Powder River Basin
|
|
|
Project Evaluation Criteria |
|
Project Type (see below) Project Title |
Map Loc. No. |
Est. Yield(y), Cap(c) or Depl(d) (AF) |
Water Availability |
Financial Feasibility |
Public Acceptance |
No. of Sponsors/ Beneficiaries |
Legal/ Institutional Constraints |
Environmental/ Recreation Benefits |
Total Score |
| Type 1 (None) |
|
|
|
|
|
| Type 2 (None) |
|
|
6 |
7 |
5 |
6 |
4 |
3 |
|
| Morgareidge No. 7 Reservoir |
52 |
4,600 acres |
5 |
6 |
5 |
7 |
4 |
4 |
167 |
| Red Fork Powder River Reservoir |
53 |
unk |
4 |
4 |
5 |
6 |
4 |
4 |
141 |
| Type 3 |
|
|
6 |
8 |
5 |
6 |
5 |
6 |
|
| Moorhead Reservoir |
47 |
35,000 y |
8 |
7 |
7 |
6 |
5 |
6 |
236 |
| Buffalo Creek Reservoir |
54 |
unk |
8 |
3 |
7 |
6 |
7 |
6 |
214 |
| Pumpkin Reservoir |
45 |
60,000 y |
6 |
6 |
6 |
6 |
6 |
5 |
210 |
| Clarks Fork Reservoir |
|
99,700 c |
8 |
6 |
6 |
5 |
3 |
6 |
207 |
| Bass Industrial Reservoir |
46 |
123,380 c |
6 |
6 |
6 |
5 |
5 |
5 |
199 |
| Arvada Reservoir |
48 |
35,000 y |
6 |
6 |
6 |
5 |
5 |
5 |
199 |
| Middle Fork Powder River Reservoir |
43 |
27,000 y |
5 |
5 |
5 |
6 |
7 |
5 |
196 |
| Fence Creek Reservoir |
50 |
106,700 c |
7 |
4 |
7 |
5 |
6 |
4 |
193 |
| Fortification Creek Reservoir |
49 |
63,300 y |
5 |
4 |
7 |
6 |
6 |
4 |
187 |
| Gibbs Reservoir |
51 |
10,800 y |
6 |
5 |
6 |
4 |
5 |
5 |
185 |
| Groundwater Development |
|
unk |
3 |
3 |
7 |
3 |
6 |
5 |
155 |
| Type 4 (None) |
|
|
|
|
|
Notes:
1. Each criteria has a different weighting for each type of project; 10 is most important, 1 is least important
2. Under each project, the criteria are individually scored; 10 means largely favorable, 0 is unfavorable
3. Total scores are the additive result of multiplying each project criteria weighting by the associated project type criteria score
Type 1: Rehabilitation projects that preserve existing uses
Type 2: Projects that rectify existing shortages
Type 3: Projects that meet projected future demands
Type 4: Projects that enhance uses in other Wyoming basins |
Table 6
Ranked Short-List: Little Powder River Basin
|
|
|
Project Evaluation Criteria |
|
Project Type (see below) Project Title |
Map Loc. No. |
Est. Yield(y), Cap(c) or Depl(d) (AF) |
Water Availability |
Financial Feasibility |
Public Acceptance |
No. of Sponsors/ Beneficiaries |
Legal/ Institutional Constraints |
Environmental/ Recreation Benefits |
Total Score |
| Type 1 (None) |
|
|
|
|
|
| Type 2 (None) |
|
|
|
|
|
| Type 3 |
|
|
6 |
8 |
4 |
5 |
4 |
6 |
|
| Coal Mine Reclamation Reservoirs Reservoir |
|
unk |
5 |
7 |
8 |
6 |
6 |
8 |
220 |
| Groundwater Development |
|
unk |
6 |
5 |
7 |
4 |
7 |
5 |
182 |
| Type 4 (None) |
|
|
|
|
|
Notes:
1. Each criteria has a different weighting for each type of project; 10 is most important, 1 is least important
2. Under each project, the criteria are individually scored; 10 means largely favorable, 0 is unfavorable
3. Total scores are the additive result of multiplying each project criteria weighting by the associated project type criteria score
Type 1: Rehabilitation projects that preserve existing uses
Type 2: Projects that rectify existing shortages
Type 3: Projects that meet projected future demands
Type 4: Projects that enhance uses in other Wyoming basins |
REFERENCES
CH2M HILL, Prefeasibility Study Tongue & Little Bighorn River Project, March 1977, State of
Wyoming, Governor's Interdepartmental Water Conference
Wyoming Water Development Commission, Little Bighorn River Preliminary Feasibility Study of
Development Alternatives and Delivery Options, September 1981, Report to the Honorable Ed
Herschler, Governor of Wyoming
Wyoming State Engineer's Office, Wyoming Water Planning Program, Report 10, Water & Related Land
Resources of Northeast Wyoming, April 1972.
Banner Associates, Inc., Tongue River Level I, January 1985, Wyoming Water Development
Commission
Centennial Engineering & Research, Inc., Alliance Lateral Ditch Level II Rehabilitation Feasibility Study,
Final Report, October 1986, Wyoming Water Development Commission
Harza Engineering Company, Storage Development For Water Supply, Powder River Basin in Wyoming,
Level I Reconnaissance Study, September 1983, Wyoming Water Development Commission
Harza Engineering Company, Powder River Storage Development, August, 1974, Wyoming State
Engineer's Office, Wyoming Water Planning Program
HKM Associates, Crazy Woman Watershed Project Level II, Phase I Rehabilitation Plan and Phase II
Conceptual Design and Cost Estimates, November 1991, Wyoming Water Development
Commission
Harza Engineering Company, Middle Fork Powder River Dam and Reservoir Project Conceptual Report,
January, 1986, Wyoming Water Development Commission
Wright Water Engineers, Wyoming Yellowstone River Basin Exchange and Water Supply Project – A
Plan to Increase Wyoming's Use of Water From the Powder River by an Exchange to Montana of
Clarks Fork Water, May, 1981, Cadiz Corporation
Appendix A – Long-list and Short-list of Future Water Use Opportunities
The following is a long-list of future water use opportunities for the Powder, Tongue, and Little Bighorn River Basins of Wyoming. The long-list was compiled from a review of published reports and input from the Basin Advisory Group. A brief description of each project is provided. Numbers in parentheses following the project title, i.e. (MLN 6), are map location numbers indicating the location of the projects on Figure 1. Projects without map location numbers either have no specific location, i.e. groundwater development, or the project features are outside of the study area. Projects marked with an “ * ” were eliminated from the short-list. Reasons for elimination are provided.
Little Bighorn River Basin
- Little Bighorn River Export System (MLNs 1,6): Pipelines and reservoirs to collect and divert water to the Tongue River drainage. Proposals include Parkman Reservoir (42,580 acre-feet) and Dry Fork Reservoir (30,671 acre-feet); annual yield 29,600 acre-feet
- BEPC Sunrise Project (MLN 2): Industrial water supply developed in Sunrise No. 1 Reservoir (82,110 acre-feet) on Twin Creek with supply pipelines from East Pass, West Pass, and Gay Creeks
- Twin Creek Reservoir (MLN 2): Diverts Tongue River water to Twin Creek Reservoir (38,588 acre-feet)
- Fuller No. 1 Reservoir (MLN 3): Water pumped from Little Bighorn River and stored in Fuller No. 1 Reservoir on Red Gulch Creek (22,829 acre-feet)
- Fuller No. 2 Reservoir (MLN 4): Water pumped from Little Bighorn River and stored in Fuller No. 2 Reservoir on Muir Creek (1,549 acre-feet)
- Half Ounce Reservoir (MLN 5): Water stored in Half Ounce Reservoir (34,187 acre-feet) and diverted to Dry Fork; annual yield 10,000 acre-feet
- Groundwater Development
Tongue River Basin
- North Fork Reservoir (MLN 7): 40,200 acre-foot reservoir; annual yield between 13,800 and 21,600 acre-feet depending on minimum pool and fish flow requirements
- South Fork Reservoir (MLN 8): 26,500 acre-foot reservoir; annual yield between 9,900 and 13,200 acre-feet depending on minimum pool and fish flow requirement
- Rockwood Reservoir (MLN 9): 125,000 acre-foot reservoir; annual yield between 65,500 and 93,000 acre-feet depending on minimum pool and fish flow requirements, and Montana cooperation
- Upper State Line Reservoir (MLN 10): 250,000 acre-foot reservoir; annual yield between 68,000 and 75,000 acre-feet depending on minimum pool and fish flow requirements
- Prairie Dog Reservoir (MLN 11): 128,000 acre-foot reservoir; 150 cfs pumped diversion from Tongue River; annual yield between 18,000 and 20,000 acre-feet depending on minimum pool requirement
- Lower State Line Reservoir (MLN 12): 870,000 acre-foot reservoir; annual yield 88,000 acre-feet for Wyoming
- Sheridan Canal System (MLN 13): diversion from the Tongue River into the Goose Creek drainage for irrigation; storage in Rockwood Reservoir (125,000 acre-feet); annual yield 68,500 acre-feet
- Shutts Flats Reservoir (MLN 14): 11,250 acre-foot reservoir; annual yield between 5,800 and 7,600 acre-feet depending on fish-flow and minimum pool requirement
- Alliance Lateral Ditch Rehabilitation* (MLN 15): rehabilitation of ditch to reduce O&M costs; serves 1,395 acres
Reasons for elimination: rehabilitation is currently being addressed by WWDC
- Jones Draw Reservoir (MLN 16): Rural water supply developed in a 4,000 to 5,000 acre-foot reservoir on Jones Draw that is filled through the enlarged and reconstructed Peralta Ditch diverting from Little Goose Creek; annual yield 1,000 to 2,500 acre-feet
- West Fork Reservoir (MLN 17): Rural water supply developed in a 4,000 to 5,000 acre-foot reservoir; annual yield 1,000 to 2,500 acre-feet
WTM Reservoir* (MLN 18): 140,345 acre-foot reservoir on Tongue River; annual yield 50,000 acre-feet
Reasons for elimination: similar to Upper State Line Reservoir which is larger
- Groundwater Development
Clear Creek Basin
- Little Sour Dough Reservoir (MLN 19): 1,642 acre-foot irrigation reservoir
- Camp Comfort Reservoir (MLN 20): 11,640 acre-foot irrigation reservoir
- Lake DeSmet and Enlargements (MLN 21): Enlargements include Healy Reservoir Enlargement (13,725 acre-feet) on Clear Creek, Reynolds High Dam (44,442 acre-feet) on Piney Creek, and 4th Enlargement Lake DeSmet (23,513 acre-feet); bring total capacity to 239,243 acre-feet
- Reynolds Shell Creek Reservoir* (MLN 22): 1,369 acre-foot reservoir
Reasons for elimination: proximity to and conflict with Lake DeSmet
- Reynolds Piney Creek Reservoir* (MLN 23): 12,660 acre-foot reservoir
Reasons for elimination: proximity to and conflict with Lake DeSmet
- Boxelder Reservoir* (MLN 24): 20,000 acre-foot reservoir
Reasons for elimination: proximity to and conflict with Lake DeSmet
- B.C.L. Company Reservoir (MLN 25): 29,300 acre-foot reservoir; annual yield 9,600 acre-feet
- Lower Clear Creek Reservoir (MLN 26): 302,400 acre-foot reservoir, annual yield 30,300 acre-feet
- Tex Ellis Reservoir (MLN 27): 61,500 acre-foot reservoir on Buffalo Creek with pumped supply diversion from Clear Creek; annual yield 17,100 acre-feet
- South Rock Creek Reservoir (MLN 28): 13,300 acre-foot reservoir
- Triangle Park Reservoir (MLN 29): 3,000 acre-for reservoir
- Canyon Reservoir (MLN 30): 5,000 acre-foot reservoir
- South Clear Creek Reservoir (MLN 31): 5,000 acre-foot reservoir
- Lynx Park Reservoir (MLN 32): 10,700 acre-foot reservoir
- Sour Dough Creek Reservoir (MLN 33): 4,500 acre-foot reservoir
- Tie Hack Reservoir Enlargement (MLN 34): 7,500 acre-foot enlargement of the capacity of the City of Buffalo’s Tie Hack Reservoir
- Groundwater Development
Crazy Woman Creek Basin
- Enl. Negro Creek Reservoir (MLN 35): 13,900 acre-foot reservoir in Clear Creek drainage; diversion to Crazy Woman Creek
- Crazy Woman Reservoir (MLN 36): 64,300 acre-foot reservoir; annual yield 3,700 to 10,500 acre-feet
- North Fork Crazy Woman Reservoir (MLN 37): 2,759 acre-foot reservoir
- Hazelton Watershed Site “A” SCS (MLN 38): 2,700 acre-foot reservoir, serves 1,580 acres
- Hazelton Watershed Site “B” SCS (MLN 39): 9,000 acre-foot reservoir, serves 3,000 acres
- Lower Crazy Woman Creek Reservoir (MLN 40): 496,300 acre-foot reservoir on Crazy Woman Creek with pumped diversion from the Powder River; annual yield 67,200 acre-feet
- Crazy Woman Watershed Project* (MLN 41): rehabilitation or replacement of various facilities of the Crazy Woman Watershed Improvement District
Reasons for elimination: rehabilitation is currently being addressed by WWDC and DEQ
- Doyle Creek Reservoir (MLN 42): Middle Fork Crazy Woman Creek Project, 9,000 acre-foot reservoir, serves 3,000 acres
- Groundwater Development
Powder River Basin
- Middle Fork Powder River Reservoir (MLN 43): 59,600 acre-foot reservoir; annual yield 27,000 acre-feet
- Pumpkin Reservoir (MLN 45): 643,900 acre-foot reservoir; annual yield 60,000 acre-feet
- Bass Industrial Reservoir (MLN 46): 123,380 acre-foot reservoir
- Moorhead Reservoir (MLN 47): 211,600 acre-foot reservoir; annual yield 35,000 acre-feet for Wyoming
- Arvada Reservoir (MLN 48): 1,309,000 acre-foot reservoir; annual yield 35,000 acre-feet
- Fortification Creek Reservoir (MLN 49): 427,000 acre-foot reservoir; annual yield 63,300 acre-feet; 610 cfs diversion from the Powder River
- Fence Creek Reservoir (MLN 50): 106,700 acre-foot reservoir on Fence Creek; diversion from the Powder River
- Gibbs Reservoir (MLN 51): 195,600 acre-foot reservoir; annual yield 10,800 acre-feet
- Morgareidge No. 7 Reservoir (MLN 52): 1,200 acre-foot reservoir providing 1,100 acre-feet per year to serve 4,600 acres.
- Red Fork Powder River Reservoir (MLN 53): proposed reservoir of unspecified capacity to provide supplemental irrigation supply
- Buffalo Creek Reservoir (MLN 54): proposed reservoir of unspecified capacity to improve downstream water quality by removing significant chemical and silt problems and possibly create additional agricultural water
- Clarks Fork Exchange: two reservoirs with a combined capacity of 99,700 acre-feet in the Clarks Fork drainage, Badger Basin Reservoir and supply ditch, and Clarks Reservoir; releases to Montana in exchange for increases in Powder River depletions by Wyoming
- Groundwater Development
Little Powder River Basin
- Coal Mine Reclamation Reservoirs: small reservoirs developed as part of reclamation of surface coal mines.
- Groundwater Development
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