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Recovery Plan for the Northern Spotted Owl - DRAFT

Recovery Plan for the Northern Spotted Owl - DRAFT

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<strong>the</strong> FWS Breeding Bird Survey on population trends in several species ofhawks and owls. We calculated long-term trends and <strong>the</strong>n estimated <strong>the</strong>number of years required to obtain reliable estimates of <strong>the</strong>se trends. Thisanalysis provides much less detailed results but involves real, ra<strong>the</strong>r thansimulated, data. Each analysis provides useful in<strong>for</strong>mation, but even incombination <strong>the</strong>y provide only preliminary estimates of <strong>the</strong> sample sizes thatwill be necessary to obtain reliable estimates of long-term trends in spotted owlpopulations.Computer simulations: This investigation required specification of anautocorrelation model describing <strong>the</strong> process by which <strong>the</strong> survey data wouldbe obtained. The specific autocorrelation structure of <strong>the</strong> model is not critical,so an analytically tractable Markov chain model was used. The model insimplest <strong>for</strong>m is defined by <strong>the</strong> probability 4 that a site is initially occupied, <strong>the</strong>probability p that a site occupied in one year will be occupied <strong>the</strong> next year,and <strong>the</strong> probability r that a site not occupied in one year will be occupied <strong>the</strong>next year. These define a Markov chain on <strong>the</strong> two states of nature, " 1" <strong>for</strong>occupied and "0" <strong>for</strong> unoccupied, as shown below.Transition probability matrixConditionInitialprobability Condition 1 0f 1 p i-p1-f 0 r I-rThe expected proportion of occupied sites converges to a limiting value, r/( I -p+r), independent of <strong>the</strong> initial fraction 4 of occupied sites, so if <strong>the</strong> initialoccupancy rate is less than this equilibrium value <strong>the</strong>n an upward trendoccurs. As an illustration of this phenomenon <strong>the</strong> trend over an 8-year periodwas calculated <strong>for</strong> <strong>the</strong> case p=0.9 and r=0.01 giving a limiting value of .01 /.1 1= .090909 <strong>for</strong> <strong>the</strong> fraction occupied after a large number of years. The initialfraction was chosen to be 30 percent smaller than this; namely, f = .070 (TableA.4). During <strong>the</strong> 8-year interval, this fraction increased 17 percent to 0.082,which is equivalent to an annual, proportional, or multiplicative, change of1.019626 (i.e., 1.0196268 = 1.17). In <strong>the</strong> analyses below, we would describesuch a change by stating that <strong>the</strong> population grew at an average annual rate of1.96 percent.Detectability bias and noise were introduced into <strong>the</strong> model by assuming thatan occupant is detected with probability d, and "detection" is independent fromsite to site and year to year. Only "false negatives" are allowed: i.e., a true 0 isalways recorded as 0 while a true 1 is sometimes (with probability 1 -d) recordedas 0. This has <strong>the</strong> effect of i) reducing <strong>the</strong> expected slope by <strong>the</strong> factord, ii) reducing <strong>the</strong> variance by <strong>the</strong> factor d 2 but iii) adding a noise variancecomponent:d(I-d)ac 2 awhere c denotes <strong>the</strong> contrast year-coefficients and "a" denotes <strong>the</strong> yearlyexpected true-occupancy per site; i.e.,Expected sample slope = dyca.Stochasticity in <strong>the</strong> transition probabilities p and r was introduced as randommultiplicative effects. A year-specific, site-specific p became a product of a257

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