Difference between revisions of "Bishop Study"

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==The 1987 Bishop Study ==
 +
The research reported here focused on the effects of Glen Canyon Dam operations on the quality of
 +
recreation downstream. Two types of
 +
recreation were studied in detail, fishing and white-water boating. From a recreational
 +
perspective, different discharges from the dam affect the conditions under which downstream fishing
 +
and white-water boating occur. Flows in the river could be a significant determinant of
 +
recreational quality.
  
----
+
The study was conducted as part of the Glen Canyon Environmental Studies (GCES), a multi-agency
 +
effort to examine the impacts of dam operations on the environmental and recreational resources
 +
downstream. The mission of the initial phase of GCES was to determine whether operations were
 +
adversely affecting downstream environmental and recreational resources and, if so, whether ways
 +
could be found, within existing institutional constraints, to improve or better protect
 +
environmental and recreational resources. The overall goal of GCES -- and hence the work on
 +
recreation reported here -- was
 +
not to prescribe specific actions to be taken, since this would have involved much broader
 +
trade-offs between recreation, power generation, environmental effects, and other social
 +
objectives. Rather, our goals were the more limited ones of determining the effects of dam
 +
operations on recreational quality and developing options that would benefit recreation considered
 +
alone. The results reported here will eventually be combined with results from studies on the
 +
downstream environment, electric power generation, and other resources in order to construct and
 +
evaluate dam management options.
  
 +
We used dollar measures to quantify recreational impacts. Thus, the study design, as described
 +
later in the paper, was built on theoretical links between environmental quality and consumer
 +
surplus explored thoroughly by Maler (1974) and Freeman (1979). Using dollar values not only
 +
conveys recreational quality impacts in a commonly used metric, but may also eventually facilitate
 +
the analysis of trade-offs between recreation and other goals using the tools of benefit-cost
 +
analysis.
  
 +
In the next section, the relationships between dam operations and recreation will be explored.
 +
Following this, the design of the study is summarized and the measured consumer surplus values for
 +
fishing and boating reported. We then illustrate ways that dam operations could be modified to
 +
improve downstream recreation.[http://www.swrcb.ca.gov/water_issues/programs/ocean/cwa316/docs/cwa316may2010/comments041310/bishop_etal.pdf]
  
 
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! <h2 style="margin:0; background:#cedff2; font-size:120%; font-weight:bold; border:1px solid #a3bfb1; text-align:left; color:#000; padding:0.2em 0.4em;">Issues</h2>
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! <h2 style="margin:0; background:#cedff2; font-size:120%; font-weight:bold; border:1px solid #a3bfb1; text-align:left; color:#000; padding:0.2em 0.4em;"> The 8k Cap </h2>
 
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Revision as of 09:37, 28 August 2019


Granite Gorge- SJansen.JPG

The 1987 Bishop Study

The research reported here focused on the effects of Glen Canyon Dam operations on the quality of recreation downstream. Two types of recreation were studied in detail, fishing and white-water boating. From a recreational perspective, different discharges from the dam affect the conditions under which downstream fishing and white-water boating occur. Flows in the river could be a significant determinant of recreational quality.

The study was conducted as part of the Glen Canyon Environmental Studies (GCES), a multi-agency effort to examine the impacts of dam operations on the environmental and recreational resources downstream. The mission of the initial phase of GCES was to determine whether operations were adversely affecting downstream environmental and recreational resources and, if so, whether ways could be found, within existing institutional constraints, to improve or better protect environmental and recreational resources. The overall goal of GCES -- and hence the work on recreation reported here -- was not to prescribe specific actions to be taken, since this would have involved much broader trade-offs between recreation, power generation, environmental effects, and other social objectives. Rather, our goals were the more limited ones of determining the effects of dam operations on recreational quality and developing options that would benefit recreation considered alone. The results reported here will eventually be combined with results from studies on the downstream environment, electric power generation, and other resources in order to construct and evaluate dam management options.

We used dollar measures to quantify recreational impacts. Thus, the study design, as described later in the paper, was built on theoretical links between environmental quality and consumer surplus explored thoroughly by Maler (1974) and Freeman (1979). Using dollar values not only conveys recreational quality impacts in a commonly used metric, but may also eventually facilitate the analysis of trade-offs between recreation and other goals using the tools of benefit-cost analysis.

In the next section, the relationships between dam operations and recreation will be explored. Following this, the design of the study is summarized and the measured consumer surplus values for fishing and boating reported. We then illustrate ways that dam operations could be modified to improve downstream recreation.[1]

--- --- ---

Summary


The 8k Cap

In Bishop et al. (1987; on page 410 of the 30 page report: “Grand Canyon Recreation and Glen Canyon Dam Operations: An Economic Evaluation) fluctuating flows are defined as any operation where the daily flow fluctuation was equal to or more than 10,000 cfs/day. Bishop treated daily flow fluctuations of less than 10,000 cfs/day as “constant flow releases.” Bishop identified that this “10,000 cfs threshold was determined to be the point at which fluctuations begin to be perceptible to recreationists.”

Additionally, Stewart et al.’s (2000) follow-up of the Bishop et al. (1987) study found that angler’s did not identify river level fluctuations, at least under the MLFF operating regime, as an issue. Based on information from Stewart et al (2000) and Bishop et al. (1987), any flow fluctuation below 10,000 cfs/day should be treated the same as a steady flow release.



INFORMATION


Reports and Links

2000

1987

Other Stuff