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Recovery Plan for the Northern Spotted Owl - DRAFT

Recovery Plan for the Northern Spotted Owl - DRAFT

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size declines. In <strong>the</strong> <strong>for</strong>mer case, <strong>the</strong> age ratio would be of little value as anearly warning sign, whereas in <strong>the</strong> latter case it could be of significant help.Ages of first time breeders should be obtained <strong>for</strong> a series of populations, and<strong>the</strong> behavior of nonterritorial birds should be studied so that computer simulationscan be made more realistic. The age ratio usually are obtained in <strong>the</strong>course of monitoring adult survival rates so this in<strong>for</strong>mation can be obtainedwith little or no extra cost.The second early warning method is <strong>the</strong> time that vacancies in <strong>the</strong> territorialpopulation remain unfilled. Much <strong>the</strong> same argument as was made earlier canbe applied to this variable. If a large nonterritorial population exists, <strong>the</strong>n onewould expect replacement times to be short, whereas eventually, as <strong>the</strong> populationdeclines, some vacancies will not be filled at all. Thus, <strong>the</strong> replacementtime should increase gradually as a population declines. Also, if nonterritorialbirds search widely <strong>for</strong> vacancies, <strong>the</strong>n <strong>the</strong> upward trend in replacement timemight not begin until nearly all nonterritorial birds had disappeared, whereas if<strong>the</strong>y search only locally, <strong>the</strong> upward trend might begin much sooner. Thisissue could be investigated to some extent by recording replacement times andtracking <strong>the</strong> change in <strong>the</strong>ir average value as a population changes in size.Empirical in<strong>for</strong>mation about <strong>the</strong> behavior of nonterritorial birds, however, alsowould be of great value in understanding this variable and using its behaviorto make inferences about population trends. This method would probably onlywork when some vacancies remain unfilled <strong>for</strong> at least a year.A Comprehensive Monitoring ProgramThis section contains preliminary recommendations <strong>for</strong> a comprehensivemonitoring program. The suggestions will need review and refinement, butenough in<strong>for</strong>mation exists to develop <strong>the</strong> general outlines <strong>for</strong> <strong>the</strong> program.Considerable overlap exists (Table A.8) in <strong>the</strong> in<strong>for</strong>mation needed by fourapproaches to estimate trends described earlier. For example, <strong>the</strong> "Demographicrates" approach and <strong>the</strong> "Population modeling" approach requirein<strong>for</strong>mation on productivity and adult survival rates, and in<strong>for</strong>mation on <strong>the</strong>behavior of nonterritorial birds will be useful in population modeling and in <strong>the</strong>early warning approaches. Study of Table A.8 suggests that <strong>the</strong> monitoringef<strong>for</strong>t might be subdivided into five programs (Table A.9).The first program is <strong>the</strong> roadside surveys <strong>for</strong> territorial birds. Details of thisapproach have been described previously. The second program, activity sitemonitoring, would provide much of <strong>the</strong> in<strong>for</strong>mation needed <strong>for</strong> demographicanalyses and population projections. The difference in requirements of <strong>the</strong>setwo approaches is that demographic analyses require that sites be selectedrandomly and habitat in<strong>for</strong>mation is not required, whereas population projectionsrequire that sites be selected in different habitats and habitat in<strong>for</strong>mationis required. These differences can be accommodated by stratifying <strong>the</strong> rangeinto habitat types and selecting sites randomly within each stratum. Specifichabitat in<strong>for</strong>mation about <strong>the</strong> sites also should be collected. In<strong>for</strong>mationcollected at <strong>the</strong>se sites (age ratios and replacements times) will provide much of<strong>the</strong> data needed <strong>for</strong> <strong>the</strong> two early warning methods. The third program is aseries of transmitter studies. Studies are needed of dispersing juveniles andterritorial and nonterritorial adults. As noted earlier, intensive monitoring isneeded in some of <strong>the</strong>se studies, even if this means that <strong>the</strong> sample size mustbe ra<strong>the</strong>r small. The fourth program includes miscellaneous studies that donot fit easily into <strong>the</strong> categories discussed earlier, and <strong>the</strong> fifth program iscoordination of <strong>the</strong> first four ef<strong>for</strong>ts.269

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