Analysis of Methods
for Determining
Minimum Instream Flows
for Recreation
Idaho Forest, Wildlife and Range Policy Analysis Group
Report No. 9
by
Troy Merrill1
and
Jay O'Laughlin2
March 1993
__________________________
1Research Assistant, Idaho Forest, Wildlife and Range Policy Analysis Group, University of Idaho, Moscow, ID 83843
2Director, Idaho Forest, Wildlife and Range Policy Analysis Group, University of Idaho, Moscow, ID 83843.
ACKNOWLEDGEMENTS
The efforts of the Technical Advisory Committee, listed below, are gratefully acknowledged. These individuals provided guidance on the design of the plan for this study, and provided technical review of the final draft of the report.
| Chuck Harris, Ph.D. Associate Professor Dept. of Resource Recreation and Tourism University of Idaho |
Bill Graham Idaho Dept. of Water Resources Boise, Idaho |
| Bo Shelby, Ph.D. Professor of Recreation Resources Dept. of Forest Resources Oregon State University Corvallis, Oregon |
Rinda Just, J.D. Idaho Attorney General's Office Idaho Dept. of Parks and Recreation Boise, Idaho |
| Douglas L. Grant, J.D. Professor College of Law University of Idaho |
Two others provided technical review of portions of the final draft of the report:
| David J. Walker, Ph.D. Professor of Resource Economics Department of Agricultural Economics and Rural Sociology University of Idaho |
Joel R. Hamilton, Ph.D. Professor of Resource Economics Department of Agricultural Economics and Rural Sociology University of Idaho |
We especially would like to thank the 68 individuals who took time from their busy schedules to respond to our survey questionnaire.
TABLE OF CONTENTS
| Acknowledgements | i |
| List of Tables and Figures | iv |
| Foreword | v |
| Executive Summary | 1 |
| Introduction | 2 |
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| Laws and Regulations for Protecting Instream Flow | 6 |
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| Deciding What to Protect | 12 |
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| Methods for Quantifying Instream Flow: Literature Review | 31 |
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| Survey Results: Methods for Quantifying Instream Flow | 37 |
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| Conclusions | 40 |
| Literature Cited | 42 |
LIST OF TABLES
| Table 1. Variables affecting canoeing and aesthetics on two slow-moving rivers in east Texas | 19 |
| Table 2. Instream flow regimens for fish, wildlife, recreation, and related environmental resources | 31 |
| Table 3. Required stream width and depth minima for various recreation craft as determined by the single cross section method | 33 |
| Table 4. Recreation streamflow criteria by activity: safety range and optimal range for stream depth and velocity | 34 |
LIST OF FIGURES
| Figure 1. Which organizations responded to the survey on instream flows? | 2 |
| Figure 2. In which states have respondents been involved with instream flow protection? | 4 |
| Figure 3. Which organizations perceive the need to protect instream flows? | 5 |
| Figure 4. Existing laws and regulations used to protect instream flows for recreation. | 6 |
| Figure 5. Approaches to reduce controversy over instream flow protection and the relative likelihood of their success | 14 |
| Figure 6. Recreation activities used to justify establishing minimum instream flow | 16 |
| Figure 7. Importance of protecting the recreation experience | 17 |
| Figure 8. Importance of protecting different elements of the stream environment for the recreation experience | 20 |
| Figure 9. Adequacy of protection for different elements of the stream environment offered by various quantification methods | 23 |
| Figure 10. Frequency of use of different methods of quantifying instream flow | 37 |
| Figure 11. Which is the most reliable method of quantifying instream flow? | 38 |
| Figure 12. How confident are you in defending the quantity of water at different levels of review? | 39 |
FOREWORD
The Idaho Forest, Wildlife and Range Policy Analysis Group (PAG) was created by the Idaho legislature in 1989 to provide Idaho decision makers with timely and objective data and analyses of pertinent natural resource issues. A standing nine-member advisory committee (see inside cover) suggests issues and priorities for the PAG. Results of each analysis are reviewed by a technical advisory committee selected separately for each inquiry (see the acknowledgements on page i). Findings are made available in a policy analysis publication series. This is the ninth report in the series. The other eight reports are listed in the inside cover.
This analysis was requested by the Director of the Idaho Department of Parks and Recreation and, at the inception of the project, the request was endorsed by the Director of the Idaho Department of Water Resources.
The report does not address the political question of whether or not minimum instream flows for recreation should be established on various streams and rivers in Idaho. The legislature has designed a process for that purpose. This report provides an analysis of existing methods for determining or quantifying instream flows for recreation purposes, an important and timely topic because several different methods are being applied in this evolving field. The results of this analysis should provide useful information.
John C. Hendee, Dean
College of Forestry, Wildlife and Range Sciences
University of Idaho
EXECUTIVE SUMMARY
What methods are available for determining or quantifying instream flows for recreation purposes? Several methods are described in the literature. Respondents to a survey we conducted used survey-based quantification methods most often, and said they were the most reliable methods.
To put the results of this analysis in context, we briefly describe the legal process whereby minimum instream flows for recreation are established in Idaho, along with a capsule history of the recognition of instream flows as a beneficial use of Idaho's water by the state legislature.
Accompanying the decision to establish an instream flow for recreation purposes is the question, how much water should be protected? To help answer this question, we reviewed pertinent literature, developed a questionnaire based on the literature, and sent it to the 114 people who attended an instream flow conference in Corvallis, Oregon, in March 1991. We received 68 responses from people throughout the West with experience determining instream flow quantities. The complete questionnaire and responses to it are published separately (see Merrill and O'Laughlin 1992). Survey results are summarized as follows.
Most of the 68 respondents work for federal agencies, but a wide variety of state and private organizations also responded (see Figure 1, page 2). Fishing and boating are, not surprisingly, the recreation activities most often used to justify establishing minimum instream flows (Fig. 6, p. 16). The most frequently used laws and regulations for instream flow protection are state water appropriations and federal hydropower permits (Fig. 4, p. 6). Instream flow appropriations are controversial, and the quantification of flows is necessary as proof of beneficial use for any appropriation. Flow quantification studies along with public education are the approaches most likely to reduce controversy over instream flow determination (Fig. 5, p. 14).
The term "minimum instream flow for recreation" is somewhat misleading because there is no single minimum flow for recreation. Each recreation activity has different requirements (Table 4, p. 34), and recreation is an experience, not just an activity. To provide opportunities for satisfactory recreational experiences over a long time period, the stream environment needs to be protected, not just the activities presently occurring within that environment. Both the literature review and our survey results reinforce this point (Fig. 7, p. 17). As a practical matter, then, various elements of the stream environment that contribute to the recreation experience require protection, including (in the order ranked by the survey respondents (Fig. 8, p. 20), water quality, riparian vegetation, natural channel features, adjacent wetlands, and the opportunity to see and hear moving water. Of these stream features, water quality, riparian vegetation, and adjacent wetlands are, according to the respondents, not very adequately considered for protection by the various quantification methods (Fig. 9, p. 23). Which is the most reliable method of quantifying instream flow needs for recreation? Respondents have used a variety of methods (Fig. 10, p. 37). Of the 53 replies to this question, 22 said a survey of experts and 14 said a survey of users were the most reliable methods. The rather technical incremental method ranked in third place, receiving only 4 votes (Fig. 11, p. 38).
Establishing minimum instream flows is neither a legal problem nor an overwhelmingly difficult technical problem. It is a political problem. A legal process for appropriating instream flows in Idaho was established in 1978. A variety of technical methods are available for quantifying the amount of water for recreation activities and relating streamflow to environmental attributes of the stream that contribute to the recreation experience. The political challenge in allocating water is determining which uses of water and water courses are in the best interests of society.