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<br />Technical Clarity in Inter-Agency Negotiations: Lessons From Four Hydropower Projects <br /> <br />fact that little biological data had actually been col- <br />lected. The utility was reluctant to commit to major <br />expenditures without data showing that many fish <br />would benefit from project modifications. <br />When the application was submitted to the FERC, <br />it reflected the various areas of disagreement. When <br />the license was issued in August 1987, FERC includ- <br />ed five articles pertaining to environmental mitiga- <br />tion, and they reflected each disagreement. The <br />applicant and the resource agencies were charged <br />with resolution of conditions contained in the license <br />articles. A new round of negotiations commenced and <br />had not concluded at the time of our interviews. <br />Throughout these consultations, applicants and <br />resource agencies disagreed about appropriate mitiga- <br />tion. One reason for this was lack of agreement on the <br />proper use of various techniques and methodologies. <br />From the beginning of the process, the state resource <br />agencies expressed concern about the loss of wild fish <br />due to entrainment and turbine mortality. When an <br />attempt was made to quantify potential losses, each <br />group arrived at different conclusions about fish mor- <br />tality. In addition to that problem, there appeared to <br />be very different views on the value of wild fish ver- <br />sus hatchery fish. In the opinion of some resource <br />agency representatives, the applicant seemed to <br />believe that (1) the fish were there to be caught, and <br />(2) there is no qualitative difference between catching <br />a wild fish and catching a hatchery fish. Resource <br />agency personnel believed that the wild fish popula- <br />tion was intrinsically valuable and worth preserving. <br />Indeed, the resource agencies believed that the utility <br />ought to be required to mitigate for past damages and <br />make some attempt to return the fishery to pre- <br />project conditions, but this request was never made <br />explicit. <br />Another problem became apparent when designing <br />studies for evaluating the effectiveness of a fish pas- <br />sage window in the diversion dam. The applicant's <br />consultants planned on using hydro-acoustics to <br />detect fish passing through the dam. The resource <br />agencies warned the applicant that in the particular <br />situation, the solid wall of the dam would result in <br />blind spots. Undeterred, the consultants proceeded <br />with plans for hydroacoustic monitoring, only to find <br />that the plan failed - because of blind spots. Eventu- <br />ally, these problems were overcome and a permanent <br />fish passage facility was constructed. <br /> <br />ANALYSIS AND DISCUSSION <br /> <br />Of the four consultations analyzed, one (Koma Kul- <br />shan) was rated as fully successful, and three (Oswe- <br />gatchie, Cataract, and Ashton-St.Anthony) were rated <br /> <br />as minimally successful. The Koma Kulshan case <br />exhibited the highest level of technical clarity. <br /> <br />Technical Clarity Enhanced by Simple Project Design <br /> <br />The most obvious reason for Koma Kulshan's tech- <br />nical clarity was that the engineering design was not <br />complex and only moderate environmental impacts <br />were expected. Project operations posed certain prob- <br />lems, but for most of the potential drawbacks a mutu- <br />ally acceptable solution was available. For example, <br />one concern was possible erosion in the case of a pen- <br />stock rupture. The solution: the penstock was routed <br />over a lava field with low erosion potential. This prob- <br />lem-solving approach characterized the Koma Kul- <br />shan negotiations. _ . <br />This is not to say that parties had no disagree- <br />ments over technical issues. Throughout the negotia- <br />tions there was some distrust between resource <br />agencies and the applicant. This stemmed from a <br />belief held by all parties that their form of expertise <br />was most appropriate in solving problems. The appli- <br />cant questioned the ability of the resource agencies to <br />interpret engineering designs, and the resource agen- <br />cies held fast to the notion that their interpretation of <br />biological studies was the only valid one. Despite <br />these differences, there was consensus about the actu- <br />al scope of the issues to be addressed; sometimes par- <br />ties disagreed on how to study the problems or even <br />how to interpret the studies but agreed on the validity <br />of the issues themselves. Because of a generally coop- <br />erative atmosphere and a desire on the part of all par- <br />ticipants to finalize the negotiations, disagreements <br />on methodology and interpretation were resolved. <br /> <br />Technical Clarity Enhanced in New Projects <br /> <br />The Koma Kulshan project was the only new pro- <br />ject we studied. Each of the other projects involved an <br />application for a renewal license for an existing pro- <br />ject. At first glance, it might appear that renewing a <br />license would be less complicated than starting from <br />the ground with a new project. In fact, the Koma Kul- <br />shan process required about as much time to resolve <br />as the other cases, ten years. Nonetheless, some inter- <br />esting dynamics added to the complexity of relicens- <br />ing. In the Koma Kulshan case, the potential impacts <br />were believed to be minor. To verify this, the parties <br />conducted studies and assessed the project area's bio- <br />logical resources. Because no concrete had actually <br />been poured, the applicant had the flexibility to work <br />around problems that were identified. <br /> <br />193 <br /> <br />WATER RESOURCES BULLETIN <br />