12.07.2015 Views

Fraser River sockeye salmon: data synthesis and cumulative impacts

Fraser River sockeye salmon: data synthesis and cumulative impacts

Fraser River sockeye salmon: data synthesis and cumulative impacts

SHOW MORE
SHOW LESS
  • No tags were found...

You also want an ePaper? Increase the reach of your titles

YUMPU automatically turns print PDFs into web optimized ePapers that Google loves.

The results show strong support for M10 (all marine life stages), with weak support for M4(Inshore Migration) <strong>and</strong> M6 (Return to the <strong>Fraser</strong>). Despite the large number of parameters (41)M10 had the lowest AICc providing strong support for this model. The next two models hadsubstantially fewer parameters but their AICc scores were 5-7 units higher than that of M10indicating some information loss as a result of the reduced number of parameters. Overall theseresults indicate that the marine component of the life stage is more important in explaining theoverall productivity than the freshwater component. However, it must be noted that there werelimited stressor <strong>data</strong> available for the freshwater component <strong>and</strong> those <strong>data</strong> available may nothave been the most appropriate <strong>data</strong>. The true interpretation of this result is that the marine <strong>data</strong>available do a better job of explaining the overall productivity of <strong>Fraser</strong> <strong>sockeye</strong>, than thefreshwater <strong>data</strong> available over this time period. Estimates of effect sizes are presented in TableA4.3-5 for all models. Interpretation of the actual estimates, their magnitude <strong>and</strong> sign is difficultparticularly for very complex models with many covariates. As described in the previous section(Interpretation of results) models with only a few stressors are easier to interpret. If interested indigging into the estimates in detail, one should also obtain the estimates of variability for each ofthese parameters. These are available, but not provided in this document in the interest of space.Table A4.3-4. A4c c<strong>and</strong>idate models ordered by AICc from best (lowest) to worst (biggest). M.ID=modelidentification, M.AIC=the estimated AIC for the model, num.obs=the total number of observations (i.e.,complete rows in the <strong>data</strong> set), num.par=the total number of fixed effects + r<strong>and</strong>om effects, Correction= thedifference between the AICc (corrected for small sample size compared to number of parameters) <strong>and</strong> theAIC, M.AICC= the AICc for the model, min.AICC = the smallest AICc observed within the model set,delta= the difference between the min.AICC <strong>and</strong> each M.AICC, <strong>and</strong> AICC_wts= the Akaike weight (i.e.,support) for each model.M.ID M.AIC num.obs num.par Correction M.AICC min.AICC delta AICC_wtsM10 1127.51 463 41 8.18 1135.69 1135.69 0 88.43M4 1135.78 463 32 4.91 1140.69 1135.69 5.00 7.25M6 1139.55 463 26 3.22 1142.77 1135.69 7.08 2.56M1 1131.35 463 50 12.38 1143.73 1135.69 8.04 1.59M5 1146.65 463 21 2.10 1148.75 1135.69 13.06 0.13M8 1151.31 463 19 1.72 1153.02 1135.69 17.33 0.02M2 1151.31 463 19 1.72 1153.02 1135.69 17.33 0.02M7 1152.93 463 23 2.51 1155.44 1135.69 19.75 0.0045M3 1155.74 463 25 2.97 1158.71 1135.69 23.02 0.00089M9 1156.46 463 26 3.22 1159.68 1135.69 23.99 0.00055238

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!