Contrasting effects of anthropogenic and natural acidity in streams: a meta-analysis

Large-scale human activities including the extensive combustion of fossil fuels have caused acidification of freshwater systems on a continental scale, resulting in reduced species diversity and, in some instances, impaired ecological functioning. In regions where acidity is natural, however, species diversity and functioning seem to be less affected. This contrasting response is likely to have more than one explanation including the possibility of adaptation in organisms exposed to natural acidity over evolutionary time scales and differential toxicity due to dissimilarities in water chemistry other than pH. However, empirical evidence supporting these hypotheses is equivocal. Partly, this is because previous research has mainly been conducted at relatively small geographical scales, and information on ecological functioning in this context is generally scarce. Our goal was to test whether anthropogenic acidity has stronger negative effects on species diversity and ecological functioning than natural acidity. Using a meta-analytic approach based on 60 datasets, we show that macroinvertebrate species richness and the decomposition of leaf litter—an important process in small streams—tend to decrease with increasing acidity across regions and across both the acidity categories. Macroinvertebrate species richness, however, declines three times more rapidly with increasing acidity where it is anthropogenic than where it is natural, in agreement with the adaptation hypothesis and the hypothesis of differences in water chemistry. By contrast, the loss in ecological functioning differs little between the categories, probably because increases in the biomass of taxa remaining at low pH compensate for losses in functionality that would otherwise accompany losses of taxa from acidic systems. This example from freshwater acidification illustrates how natural and anthropogenic stressors can differ markedly in their effects on species diversity and one aspect of ecological functioning.

[1]  D. Niyogi,et al.  Effects of Stress from Mine Drainage on Diversity, Biomass, and Function of Primary Producers in Mountain Streams , 2002, Ecosystems.

[2]  S. Arnott,et al.  Adaptive reversals in acid tolerance in copepods from lakes recovering from historical stress. , 2007, Ecological applications : a publication of the Ecological Society of America.

[3]  Tadashi Fukami,et al.  Long-term ecological dynamics: reciprocal insights from natural and anthropogenic gradients , 2005, Proceedings of the Royal Society B: Biological Sciences.

[4]  Jessica Gurevitch,et al.  STATISTICAL ISSUES IN ECOLOGICAL META‐ANALYSES , 1999 .

[5]  Michael J. Winterbourn,et al.  Do Organic and Anthropogenic Acidity Have Similar Effects on Aquatic Fauna , 1990 .

[6]  J. Elwood,et al.  The effects of stream acidity on benthic invertebrate communities in the south‐eastern United States , 1992 .

[7]  Benthic macroinvertebrate community structure in 20 streams of varying pH and humic content. , 1992, Environmental pollution.

[8]  M. Winterbourn,et al.  Benthic faunas of streams of low pH but contrasting water chemistry in New Zealand , 1996, Hydrobiologia.

[9]  B. Walker Biodiversity and Ecological Redundancy , 1992 .

[10]  D. Schindler Detecting Ecosystem Responses to Anthropogenic Stress , 1987 .

[11]  Hjalmar Laudon,et al.  Naturally acid freshwater ecosystems are diverse and functional: evidence from boreal streams , 2004 .

[12]  Göran Englund,et al.  The importance of data-selection criteria: meta-analyses of stream predation experiments , 1999 .

[13]  G. Arnqvist,et al.  Meta-analysis: synthesizing research findings in ecology and evolution. , 1995, Trends in ecology & evolution.

[14]  L. Aarssen,et al.  The evolutionary species pool hypothesis and patterns of freshwater diatom diversity along a pH gradient , 2005 .

[15]  M. Gessner,et al.  A CASE FOR USING LITTER BREAKDOWN TO ASSESS FUNCTIONAL STREAM INTEGRITY , 2002 .

[16]  Eugene P. Odum,et al.  Trends Expected in Stressed Ecosystems , 1985 .

[17]  H. Laudon,et al.  A Novel Environmental Quality Criterion for Acidification in Swedish Lakes – An Application of Studies on the Relationship Between Biota and Water Chemistry , 2007 .

[18]  P. Campbel,et al.  Acidification and Toxicity of Metals to Aquatic Biota , 1985 .

[19]  J. Herrmann,et al.  Acid-stress effects on stream biology , 1993 .

[20]  D. Schindler,et al.  Effects of Acid Rain on Freshwater Ecosystems , 1988, Science.

[21]  Anthony R. Ives,et al.  Ecological history affects zooplankton community responses to acidification , 2001 .

[22]  H. Laudon,et al.  Quantifying sources of acid neutralisation capacity depression during spring flood episodes in Northern Sweden , 1999 .

[23]  O. Schmitz,et al.  Biodiversity and the productivity and stability of ecosystems. , 1996, Trends in ecology & evolution.

[24]  D. Reznick,et al.  The population ecology of contemporary adaptations: what empirical studies reveal about the conditions that promote adaptive evolution , 2004, Genetica.

[25]  H. Laudon,et al.  Does freshwater macroinvertebrate diversity along a pH-gradient reflect adaptation to low pH? , 2007 .

[26]  S. Ormerod,et al.  Acidic episodes retard the biological recovery of upland British streams from chronic acidification , 2007 .

[27]  D. Breitburg,et al.  GEOGRAPHICAL DIFFERENCES IN BEHAVIORAL RESPONSES TO HYPOXIA: LOCAL ADAPTATION TO AN ANTHROPOGENIC STRESSOR? , 2003 .

[28]  Craig Loehle,et al.  On the relationship between r/K selection and environmental carrying capacity: a new habitat templet for plant life history strategies. , 1990 .