Length–mass relationships for adult aquatic and terrestrial invertebrates in a California watershed

By J. Sabo, J. Bastow, M. Power. Journal of The North American Benthological Society, 2002

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Warming, eutrophication, and predator loss amplify subsidies between aquatic and terrestrial ecosystems (2012, methodology): “Samples were pooled each week, and all individuals were identified to family level and measured with an ocular micrometer to calculate dry mass from length-mass regressions (Rogers et al., 1976; Sabo et al., 2002).”
Declining abundance of beetles, moths and caddisflies in the Netherlands (2019, methodology): “For that purpose we used known species length measurements and known relationships of length to weight (Sabo et al., 2002; García-Barros, 2015).”
RIVER–WATERSHED EXCHANGE: EFFECTS OF RIVERINE SUBSIDIES ON RIPARIAN LIZARDS AND THEIR TERRESTRIAL PREY (2002, methodology): “Experiments took place along a 4-km reach of the South Fork (SF) Eel River (39?”
Seeing Double:: Size-Based and Taxonomic Views of Food Web Structure (2011, methodology): “Dry mass of prey items and invertebrate predators was estimated using of published regression equations (Benke et al., 1999; Burgherr and Meyer, 1997; Edwards et al., 2009a,b; Ganihar, 1997; Gonzalez et al., 2002; Meyer, 1989; Sabo et al., 2002; Smock, 1980).”