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<br />........................................................................................................................................... F RAY E 0 S A F E T Y NET S <br /> <br />vegetation that the butterflies use and the extent <br />of exotic invasion. <br /> <br />By contrast, in the Fort Morgan Paradise <br />Joint Venture HCP for the Alabama beach <br /> <br />e <br /> <br />mouse, four times each year there are a survey <br />and control of house mice (which compete with <br />the beach mouse) and feral domestic cats (which <br />eat the beach mouse), but the responsibility for <br />monitoring the beach mouse is on FWS. <br />The approach for the Washington DNR <br />HCP emphasizes habitat monitoring with less <br />for endangered species. Although the program <br />was not expected to be complete and approved <br />by the services until late 1997, the HCP docu- <br />ment establishes three types of monitoring: (1) <br />compliance monitoring, involving reports on <br />whether harvesting activities are in compliance <br />with the HCP (each harvest will be recorded in a <br />Geographic Information System), (2) effective- <br />ness monitoring, in which DNR records the <br />stand structure and habitats that result from their <br /> <br />actions and (3) validation monitoring, in which <br />such species as the spotted owl are monitored in <br />relation to harvesting activities and habitat con- <br />ditions. Validation monitoring is at the heart of <br />whether the HCP is effective for endangered <br />species, yet the HCP indicates that this monitor- <br />ing will occur for only one portion of the plan- <br />ning area on the Olympic Peninsula, not in most <br />of the planning area. <br />In general, it appears that biological monitor- <br />ing is a secondary priority in implementing con- <br />servation plans and that monitoring funds take <br />away money from habitat conservation. For <br />example, in the Metropolitan Bakersfield HCP, <br />for the most part, qualitative assessment <br /> <br />in monitoring programs for biological <br />resources can provide sufficient information <br />to evaluate the status of the species of con- <br />cern.... While monitoring is an important <br />aspect of the plan, it should not overburden <br />the funding program and take funds away <br />from the land acquisition or management <br />programs. <br />That view is also summarized in the <br />Balcones Canyonlands Conservation Plan: <br />"While the importance of monitoring and <br />research is evident, it is likely to remain a sec- <br />ondary priority for funding by the permit hold- <br />ers" (pp. 2-41, HCP). When a bond measure <br />was rejected by Travis County voters (see section <br />on funding in this report), monitoring was <br />scaled back in favor of land acquisitions. A <br />comprehensive monitoring program for all of <br />the preserves is still under development. To <br />date, for the golden-cheeked warbler (an endan- <br />gered species), biologists have kept track of <br />where the birds' territories are located, including <br />establishment of permanent plots to be surveyed <br />each year, but the monitoring program does not <br />track nesting success, survival or adult and juve- <br />nile movement. Presence/absence data on the <br />warblers is unlikely to produce a clear picture of <br />how development and urbanization under the <br />plan affects the warblers. <br />Probably the best future models of monitor- <br />ing will combine applicant and public funds and <br />coordinate independent research or information <br />from ongoing study sites to supplement a large- <br />scale monitoring plan (this may occur under the <br />MSCP). Unfortunately, because monitoring has <br />been viewed as a secondary priority that steals <br />funds from real conservation, most monitoring <br />programs for plans reviewed here are not ade- <br />