Skip to main content
. Author manuscript; available in PMC: 2014 Dec 16.
Published in final edited form as: Ecology. 2014 Aug;95(8):2069–2076. doi: 10.1890/13-1486.1

Figure 1.

Figure 1

Four population abundance time series (circles), with expected values of true abundances given the other observations (short dashed lines), and bootstrapped 95% confidence intervals for true abundances (long dashed lines), estimated with restricted maximum likelihood under the Ornstein-Uhlenbeck state space model. Upper left: bobcat furbearer harvest records from Idaho, USA (parameter estimates with bootstrapped 95% confidence intervals: μ^=6.79(6.61,6.97), θ^=1.26(3.91×107,20.2), β^2=0.272(7.43×103,3.94), τ^2=7.48×104(9.14×1010,0.0847)). Upper right: bobcat furbearer harvest records from Maine, USA (μ^=5.78(5.47,6.08), θ^=0.877(0.0226,10.3), β^2=0.735(0.0202,2.40), τ^2=0.00475(1.79×108,0.334)). Lower left: elk population estimates from Grand Teton National Park, Wyoming, USA (μ^=7.29(7.14,7.44), θ^=0.868(0.229,19.3), β^2=0.0990(0.0296,1.45), τ^2=9.80×109(2.93×1011,1,22×103)). Lower right: grasshopper density estimates from the western mountainous region of Montana, USA (μ^=1.56(1.31,1.82), θ^=0.722(0.272,2.01), β^2=0.347(0.160,0.752), τ^2=2.27×107(3.81×108,2.27×105)).