Land use drives detritivore size structure and decomposition through shifts in resource quality and quantity.

Land use change and nutrient pollution are two pervasive stressors that can modify carbon cycling, as they influence the inputs and the transformation of detritus. Understanding their impact on stream food webs and on diversity is particularly pressing, as streams are largely fuelled by detrital material received from the adjacent riparian environment. Here we assess how a switch from native deciduous forest to Eucalyptus plantations and nutrient enrichment alter the size distribution of stream detritivore communities and decomposition rates of detritus. As expected, more detritus resulted in higher size-independent, or overall, abundance (i.e. higher intercept of size spectra). This change in overall abundance was mainly driven by a change of the relative contribution of large taxa (Amphipoda and Trichoptera), which changed from an average relative abundance of 55.5 to 77.2 % between the sites compared for resource quantity differences in our study. In contrast, detritus quality modified the relative abundance of large vs small individuals (i.e. size spectra slopes), with shallow slopes of size spectra (proportionately more large individuals) associated with sites with nutrient-richer waters and steeper slopes (proportionately fewer large individuals) associated with sites draining Eucalyptus plantations. Decomposition rates of alder leaves due to macroinvertebrates increased from 0.0003 to 0.0142 when relative contribution of large organisms increased (modelled slopes of size spectra: -1.00 and - 0.33, respectively), highlighting the importance of large sized individuals for ecosystem functioning. Our study reveals that land use change and nutrient pollution can greatly impair the transfer of energy through the detrital or 'brown' food web by means of intra- and inter-specific responses to quality and quantity of the detritus. These responses enable linking land use change and nutrient pollution to ecosystem productivity and carbon cycling.

[1]  A. Larrañaga,et al.  Resource preference of two stream detritivores in the laboratory largely differs from the supply of detritus below eucalypt plantations , 2022, Hydrobiologia.

[2]  S. Sabater,et al.  Energy limitation or sensitive predators? Trophic and non-trophic impacts of wastewater pollution on stream food webs. , 2021, Ecology.

[3]  E. Galbraith,et al.  The global ocean size spectrum from bacteria to whales , 2021, bioRxiv.

[4]  M. Jackson,et al.  Systematic variation in food web body-size structure linked to external subsidies , 2021, Biology Letters.

[5]  H. Sarmento,et al.  The riverine bioreactor: An integrative perspective on biological decomposition of organic matter across riverine habitats. , 2021, The Science of the total environment.

[6]  R. Sibly,et al.  Multiple environmental controls explain global patterns in soil animal communities , 2020, Oecologia.

[7]  A. Larrañaga,et al.  Effects of changes in food resources due to variations in forest cover on stream macroinvertebrate community size structure , 2020, Aquatic Sciences.

[8]  A. M. Edwards,et al.  Accounting for the bin structure of data removes bias when fitting size spectra , 2020 .

[9]  B. Klarner,et al.  Linking size spectrum, energy flux and trophic multifunctionality in soil food webs of tropical land-use systems. , 2019, The Journal of animal ecology.

[10]  A. Rossberg,et al.  Dome patterns in pelagic size spectra reveal strong trophic cascades , 2019, Nature Communications.

[11]  A. Perna,et al.  Energetic equivalence underpins the size structure of tree and phytoplankton communities , 2019, Nature Communications.

[12]  Iván Prieto,et al.  The leaf economic spectrum drives leaf litter decomposition in Mediterranean forests , 2018, Plant and Soil.

[13]  J. Harding,et al.  Anthropogenic mining alters macroinvertebrate size spectra in streams , 2018, Freshwater Biology.

[14]  M. Jackson,et al.  Bending the rules: exploitation of allochthonous resources by a top-predator modifies size-abundance scaling in stream food webs. , 2018, Ecology letters.

[15]  H. Jarvie,et al.  Weekly water quality monitoring data for the River Thames (UK) and its major tributaries (2009–2013): the Thames Initiative research platform , 2018, Earth System Science Data.

[16]  C. Hsieh,et al.  Systematic deviations from linear size spectra of lake fish communities are correlated with predator-prey interactions and lake-use intensity , 2018, Oikos.

[17]  B. Cardinale,et al.  Interactions between large and small detritivores influence how biodiversity impacts litter decomposition , 2018, The Journal of animal ecology.

[18]  A. Kaiser,et al.  Body-size shifts in aquatic and terrestrial urban communities , 2018, Nature.

[19]  A. Lecerf Methods for estimating the effect of litterbag mesh size on decomposition , 2017 .

[20]  M. Evans‐White,et al.  Comparing the Ecological Stoichiometry in Green and Brown Food Webs – A Review and Meta-analysis of Freshwater Food Webs , 2017, Front. Microbiol..

[21]  Andrew M. Edwards,et al.  Fishing degrades size structure of coral reef fish communities , 2017, Global change biology.

[22]  J. Koricheva,et al.  A meta-analysis on the effects of changes in the composition of native forests on litter decomposition in streams , 2016 .

[23]  Julia Koricheva,et al.  A meta‐analysis of the effects of nutrient enrichment on litter decomposition in streams , 2015, Biological reviews of the Cambridge Philosophical Society.

[24]  U. Brose,et al.  Unifying elemental stoichiometry and metabolic theory in predicting species abundances. , 2014, Ecology letters.

[25]  T. Rewicz,et al.  The profile of a 'perfect' invader - the case of killer shrimp, Dikerogammarus villosus , 2014 .

[26]  D. Bates,et al.  Fitting Linear Mixed-Effects Models Using lme4 , 2014, 1406.5823.

[27]  R. Aerts,et al.  Consequences of biodiversity loss for litter decomposition across biomes , 2014, Nature.

[28]  Akash R. Sastri,et al.  Linking secondary structure of individual size distribution with nonlinear size-trophic level relationship in food webs. , 2014, Ecology.

[29]  U. Brose,et al.  Lack of energetic equivalence in forest soil invertebrates. , 2014, Ecology.

[30]  Shinichi Nakagawa,et al.  A general and simple method for obtaining R2 from generalized linear mixed‐effects models , 2013 .

[31]  A. Larrañaga,et al.  Stream regulation by small dams affects benthic macroinvertebrate communities: from structural changes to functional implications , 2013, Hydrobiologia.

[32]  Brendan G. McKie,et al.  Continental-Scale Effects of Nutrient Pollution on Stream Ecosystem Functioning , 2012, Science.

[33]  Samraat Pawar,et al.  Dimensionality of consumer search space drives trophic interaction strengths , 2012, Nature.

[34]  E. Wohl,et al.  Mechanisms of carbon storage in mountainous headwater rivers , 2012, Nature Communications.

[35]  A. Larrañaga,et al.  Leaf-litter decomposition in headwater streams: a comparison of the process among four climatic regions , 2011, Journal of the North American Benthological Society.

[36]  A. Lecerf,et al.  Assessing the functional importance of large-bodied invertebrates in experimental headwater streams , 2011 .

[37]  C. Piscart,et al.  Effects of coexistence on habitat use and trophic ecology of interacting native and invasive amphipods. , 2011 .

[38]  A. Rosemond,et al.  Nutrient enrichment differentially affects body sizes of primary consumers and predators in a detritus‐based stream , 2010 .

[39]  Owen L. Petchey,et al.  Body-size distributions and size-spectra: universal indicators of ecological status? , 2010, Biology Letters.

[40]  J. Elser,et al.  Soil acidity, ecological stoichiometry and allometric scaling in grassland food webs , 2009, Global Change Biology.

[41]  A. Larrañaga,et al.  Impacts of Eucalyptus globulus plantations on Atlantic streams: changes in invertebrate density and shredder traits. , 2009 .

[42]  Sandra Díaz,et al.  Plant species traits are the predominant control on litter decomposition rates within biomes worldwide. , 2008, Ecology letters.

[43]  S. Ernest,et al.  Relationships between body size and abundance in ecology. , 2007, Trends in ecology & evolution.

[44]  G. Carr,et al.  Reducing the cost of benthic sample processing by using sieve retention probability models , 2007, Hydrobiologia.

[45]  A. Rosemond,et al.  Nutrients stimulate leaf breakdown rates and detritivore biomass: bottom-up effects via heterotrophic pathways , 2007, Oecologia.

[46]  Werner Ulrich,et al.  Consumer-resource body-size relationships in natural food webs. , 2006, Ecology.

[47]  S. Jennings,et al.  Predicting abundance–body size relationships in functional and taxonomic subsets of food webs , 2006, Oecologia.

[48]  Takehito Yoshida,et al.  Threshold elemental ratios of carbon and phosphorus in aquatic consumers. , 2006, Ecology letters.

[49]  J. Benstead,et al.  Ecological stoichiometry in freshwater benthic systems: recent progress and perspectives , 2005 .

[50]  S. Carpenter,et al.  Global Consequences of Land Use , 2005, Science.

[51]  J. Pozo,et al.  Impact of a eucalyptus (Eucalyptus globulus Labill.) plantation on the nutrient content and dynamics of coarse particulate organic matter (CPOM) in a small stream , 2004, Hydrobiologia.

[52]  S. Jennings,et al.  Predicting abundance-body mass relationships in benthic infaunal communities , 2004 .

[53]  James H. Brown,et al.  Toward a metabolic theory of ecology , 2004 .

[54]  J. Blanchard,et al.  Fish abundance with no fishing: Predictions based on macroecological theory , 2004 .

[55]  Sean C. Thomas,et al.  The worldwide leaf economics spectrum , 2004, Nature.

[56]  J. Cebrian Role of first‐order consumers in ecosystem carbon flow , 2004 .

[57]  J. Elser,et al.  Growth rate–stoichiometry couplings in diverse biota , 2003 .

[58]  K. Rothhaupt,et al.  Predictive Length–Dry Mass Regressions for Freshwater Invertebrates in a Pre‐Alpine Lake Littoral , 2003 .

[59]  A. Rosemond,et al.  Consumer‐resource stoichiometry in detritus‐based streams , 2003 .

[60]  A. Basaguren,et al.  Life history patterns and dietary changes of several caddisfly (Trichoptera) species in a northern Spain stream , 2002 .

[61]  A. Elosegi,et al.  Woody Debris in North Iberian Streams: Influence of Geomorphology, Vegetation, and Management , 2001, Environmental management.

[62]  A. Elosegi,et al.  Effect of removal of wood on streambed stability and retention of organic matter , 2000, Journal of the North American Benthological Society.

[63]  R. Betts,et al.  Acceleration of global warming due to carbon-cycle feedbacks in a coupled climate model , 2000, Nature.

[64]  Elser,et al.  The evolution of ecosystem processes: growth rate and elemental stoichiometry of a key herbivore in temperate and arctic habitats , 2000 .

[65]  A. Huryn,et al.  Length-Mass Relationships for Freshwater Macroinvertebrates in North America with Particular Reference to the Southeastern United States , 1999, Journal of the North American Benthological Society.

[66]  M. Graça,et al.  Leaf Barriers to Fungal Colonization and Shredders (Tipula lateralis) Consumption of Decomposing Eucalyptus globulus , 1999, Microbial Ecology.

[67]  B. Whitton,et al.  NITROGEN AND PHOSPHORUS IN EAST COAST BRITISH RIVERS: SPECIATION, SOURCES, AND BIOLOGICAL SIGNIFICANCE , 1998 .

[68]  J. Díez,et al.  Inputs of Particulate Organic Matter to Streams with Different Riparian Vegetation , 1997, Journal of the North American Benthological Society.

[69]  J. Meyer,et al.  Multiple Trophic Levels of a Forest Stream Linked to Terrestrial Litter Inputs , 1997 .

[70]  Paul H. Harvey,et al.  The relationship between abundance and body size in British birds , 1991, Nature.

[71]  E. Meyer,et al.  The relationship between body length parameters and dry mass in running water invertebrates , 1989, Archiv für Hydrobiologie.

[72]  J. Damuth,et al.  Population density and body size in mammals , 1981, Nature.

[73]  R. Cook Influential Observations in Linear Regression , 1979 .

[74]  F. O. Howard,et al.  The Utilization of Leaf Litter by Stream Detritivores , 1973 .

[75]  G. Woodward,et al.  Litter Decomposition as an Indicator of Stream Ecosystem Functioning at Local-to-Continental Scales: Insights from the European RivFunction Project , 2016 .

[76]  G. Yvon‐Durocher,et al.  Land use change affects macroinvertebrate community size spectrum in streams: the case of Pinus radiata plantations , 2016 .

[77]  G. Woodward,et al.  Environmental Warming and Biodiversity-Ecosystem Functioning in Freshwater Microcosms: Partitioning the Effects of Species Identity, Richness and Metabolism , 2010 .

[78]  R. Law,et al.  How does abundance scale with body size in coupled size-structured food webs? , 2009, The Journal of animal ecology.

[79]  G. Woodward,et al.  Chapter 1 Allometry of Body Size and Abundance in 166 Food Webs , 2009 .

[80]  Peter Burgherr,et al.  Regression analysis of linear body dimensions vs. dry mass in stream macroinvertebrates , 1997 .