We agree with the authors (WSV) that the environment in Cook Inlet changes in complicated ways. However, WSV’s listing of several unresolved questions (chiefly, in our view, whether the results apply to smaller fish or to very shallow inshore environments and whether the bottom depth of fish nets can be predicted with sufficient accuracy) is insufficient rationale for discounting the large potential benefits to both commercial and sport fishery sectors of using shallower nets. Our paper included an example that illustrated the likely relative harvest rates of using nets fishing at two specific depths (3.5 and 5.5 m). As we specifically noted in the caption to figure nine, we assumed net depths ‘…to be directly proportional to the number of meshes; if the effective maximum depth of the net is different (because mesh size varies or nets billow under strong tidal currents), this would amount to a lateral shift of the curves along the x-axis’. The analysis remains valid if we were to replace an assumed fixed-depth net with a variable net depth that oscillates over the tidal cycle; in this case, we would integrate the relative harvest rates of the nets as their effective depth changes over time. In practical terms, we would substitute the average effective depth of the net during that part of the tidal cycle chosen for a fishery opening and read off the relative harvest rates from the existing figure nine. It is important to remember that the current management regime in Cook Inlet is neither the result of a carefully tailored biological analysis nor one based on a careful economic analysis of what management system will provide the best economic value to the state. Rather, the current system is a set of inherited rules now nearly 50 years old that managed harvest levels adequately in an earlier time when severe conservation concerns for Chinook did not exist and which more or less satisfied the competing interests of the stakeholders. As a result, all fishing sectors could obtain satisfactory livelihoods and co-exist. Because the regulations allowed ‘co-existence,’ no one really questioned whether they were economically and biologically optimal, and there was thus little pressure to change. In our view, the advent of new information derived from telemetry technologies should allow managers to fill in key knowledge gaps and re-assess management regulations in this light. As WSV note, fisheries management in Cook Inlet has become ‘highly contentious;’ we agree, but do not agree that maintaining status quo management in the face of recent major environmental change is the best option, because major social, economic, and (possibly) biological loss is occurring. The key questions are as follows: (a) Is the existing management structure close to the best possible? and (b) If not, what steps could be taken to improve the management? Our results suggest that improvements to the management structure are indeed possible, because technological developments in acoustic telemetry provide an unprecedented ability to measure the movements of fish. The ability of properly implemented telemetry systems to identify radical alternatives to the status quo is widely underappreciated in our view, not just in Alaska but worldwide. In broad terms, our past inability to know where and how fish move has blinded us to opportunities to improve our management. In the current case, telemetry data allows us to identify a possible new regulatory solution that should improve the economic utility of both fishing sectors, a previously unrecognized possibility. Major restrictions have been imposed on the Eastside Setnet (ESSN) Fishery relative to earlier periods. These resulted in huge declines in fishing effort and revenue, which also occur at a time when the target species (sockeye) is at high levels of abundance, exacerbating
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