Appendix S4 Full description of meta-analysis The effect sizes for primary and secondary consumers were estimated using mixed-effects models (Borenstein et al. 2009; Viechtbauer 2010). Here, we performed separate mixed-effects models (n=6) with trophic position (i.e. primary vs. secondary consumers) as categorical moderators to compare differences in effect size for a given food web, using the restricted maximum likelihood estimator (REML) (Mengersen & Schmid 2013). In mixed-effects models, a fixed effect is used to model variability among groups (i.e. trophic level), while a random effect is used to model within-group variability (Viechtbauer 2010). The QM test was employed to test the difference in mean effects size between each trophic level, i.e. to evaluate the probability that effect size differed between the levels of moderators (Rosenberg 2013). In addition, we report I2 values as a separate measure of heterogeneity (Higgins & Thompson 2002). I2 values typically range from 0 to 100% and is interpreted as the percentage of variability in effect-size estimates that is due to between-study heterogeneity rather than sampling error (Rosenberg 2013). We report 1-I2 values to represent the actual proportion of variance in d explained by differences between trophic levels. We also estimated the influence of publication bias, which is the probability that statistically significant (P<0.05) results are more likely to be published than non-statistically significant results, using the trim-and-fill method (Duval & Tweedie 2000). This is a sensitivity analysis that corrects for funnelplot asymmetry by adding values for “missing” studies to generate a symmetric funnel plot from which a new mean effect size can be estimated (Jennions et al. 2013). REFERENCES 1. Borenstein, M., Hedges, L.V., Higgins, J.P.T. & Rothstein, H.R. (2009). Introduction to Meta-analysis. John Wiley & Sons, Chichester, UK. 2. Duval, S. & Tweedie, R. (2000). A nonparametric “trim and fill” method of accounting for publication bias in meta-analysis. J. Am. Stat. Assoc., 95, 89-98. 3. Higgins, J.P.T. & Thompson, S.G. (2002). Quantifying heterogeneity in a meta-analysis. Stat. Med., 21, 1539-1558. 1 Appendix S4 4. Jennions, M., Lortie, C., Rosenberg, M. & Rothstein, H. (2013). Publication and Related Biases. In: Handbook of Meta-analysis in Ecology and Evolution (eds. Koricheva, J, Gurevitch, J & Mengersen, K). Princeton University Press Princeton, NJ, pp. 207-236. 5. Mengersen, K. & Schmid, C. (2013). Maximum Likelihood Approaches to Meta-analysis. In: Handbook of Meta-analysis in Ecology and Evolution (eds. Koricheva, J, Gurevitch, J & Mengersen, K). Princeton University Press Princeton, NJ, pp. 125-144. 6. Rosenberg, M. (2013). Moment and Least-Squares Based Approaches to Meta-analytic Inference. In: Handbook of Meta-analysis in Ecology and Evolution (eds. Koricheva, J, Gurevitch, J & Mengersen, K). Princeton University Press Princeton, NJ, pp. 108-124. 7. Viechtbauer, W. (2010). Conducting meta-analyses in R with the metafor package. Journal of Statistical Software, 36, 1-48. 2 Appendix S4 Table A1 The results from the mixed-effect models with trophic level as a categorical moderator and the mean effect size calculated for each trophic level individually. This analysis represents data without outliers. The P-value for the QM test is given for each model. Trophic Ecosystem Type P-value of mixed-effects model 1-I2 level Mean effect size 95% CI n Wetlands Green 0.027 Brown 0.209 Woodlands Green 0.552 Brown 0.080 Grasslands Green 0.942 Brown 0.925 35% Primary Secondary 12% Primary Secondary -0.65 0.56 0.32 -0.49 -0.97/-0.34 0.06/1.2 -0.14/0.79 -1.3/0.27 8 5 11 7 33% Primary Secondary 11% Primary Secondary -0.57 -0.27 -0.58 0.83 -1.1/-0.02 -1.8/0.63 -1.2/0.04 -0.11/1.9 7 5 11 6 5% Primary Secondary 12% Primary Secondary 0.01 0.05 -0.23 0.04 -0.86/0.88 -1.3/1.4 -0.64/0.19 -0.68/0.76 9 6 15 8 Total 98 3 Appendix S4 Table A2 This analysis represents the same information as Table A1 except that the data was calculated with outliers (in bold and underlined). The outliers only occurred in the green food web of grassland ecosystems. Trophic Ecosystem Type P-value of mixed-effects model 1-I2 level Mean effect size 95% CI n Wetlands Green 0.027 Brown 0.209 Woodlands Green 0.552 Brown 0.080 Grasslands Green* 0.581 Brown 0.925 35% Primary Secondary 12% Primary Secondary -0.65 0.56 0.32 -0.49 -0.97/-0.34 0.06/1.2 -0.14/0.79 -1.3/0.27 8 5 11 7 33% Primary Secondary 10% Primary Secondary -0.57 -0.27 -0.58 0.83 -1.1/-0.02 -1.8/0.63 -1.2/0.04 -0.11/1.9 7 5 11 6 0.5% Primary Secondary 12% Primary Secondary 1.35 -1.18 -0.23 0.04 -1.4/4.14 -5.4/3.0 -0.64/0.19 -0.68/0.76 10 8 15 8 Total 101 4 Appendix S4 Trim-and-Fill Funnel Plots: P-values greater than 0.05 indicates no sensitivity to publication bias. Open circles are estimated number of missing studies, whereas dark circles are observed estimates from the meta-analysis. Data is shown without outliers. 5 Appendix S4 6 Appendix S4 7 Appendix S4 8 Appendix S4 9 Appendix S4 10