Urbanisation reduces litter breakdown rates and affects benthic invertebrate structure in Pampean streams

Abstract

The Pampean region has become one of the most urbanised areas in South America with more than 91% of the Argentinean population. This region is ideal for human settlements that have historically chosen riverine grassland areas to settle. Consequently, urban streams are increasingly subjected to pressures affecting their functioning. The aim of this study was to assess urbanisation effects on two proxies of stream integrity: leaf litter decay and benthic invertebrate assemblage colonizing litter in streams draining urbanised versus reference grassland areas. We placed plastic coarse‐ and fine‐mesh bags containing Populus nigra leaf litter along three urban and three reference reaches, and these were retrieved periodically to determine the remaining leaf mass and the identity and quantity of detritivore assemblage colonizing bags. The decay rate was negatively affected by urbanisation, and it followed a negative relationship with increasing Nitrogen concentration (mostly ammonia) and a hump‐shape relationship against soluble reactive phosphorus. Urban invertebrate assemblages were significantly different from the reference reaches, and were species‐poorer and characterized by tolerant taxa belonging to Naididae, Glossiphoniidae, and Nematoda, whereas Hyalellidae, Aeglidae, Chironomidae, Caenidae, Baetidae, and Hydrobiidae represented the reference reaches. Our proxies of structural (i.e., invertebrate assemblages) and functional (i.e., leaf litter breakdown) stream integrity were mostly driven by a nutrient‐enrichment gradient and responded in a similar direction but with different magnitude to urban alterations.

Specific indicator invertebrates of urbanized habitats in tributary streams of the Luján River basin (Buenos Aires, Argentina)

“…The high and moderate urbanization sites presented a high relative abundance of gatherer collectors, predators and shredders, which was significantly higher than in the low urbanization sites. Similar results have found Tagliaferro et al, (2020) in urban streams of the Pampean region. H. curvispina is the most abundant shredder taxa, as was also reported by Solis et al, (2019) in the coastal strip of the Río de la Plata (Buenos Aires).…”

Anthropogenic Carrion Subsidy and Herbicide Glyphosate Depressed Leaf-Litter Breakdown: Effects on Environmental Health in Streams

“…Because we found higher macroinvertebrate richness and diversity especially for detritivore abundance and richness, as well as better water quality (e.g., higher DO and lower ammonium-N concentration), in forest streams than urban streams. Richness and abundance of macroinvertebrates in urban streams were usually lower than those in forest streams, especially for shredders, the main contributor to macroinvertebrate-mediated LL breakdown (Iñiguez-Armijos et al, 2016;Tagliaferro et al, 2020). Even though, we found higher abundance of grazing snails (e.g., Viviparidae and Planorbidae) in urban than in forest streams, these snails did not compensate for the loss of detritivore insects for macroinvertebrate-mediated LL decomposition.…”

Organic Matter Decomposition and Ecosystem Metabolism as Tools to Assess the Functional Integrity of Streams and Rivers–A Systematic Review

“…Anthropogenic activities generally lead to simultaneous changes in multiple environmental variables, which may have contrasting effects on aquatic communities and litter decomposition. For instance, forestry, agriculture, urbanization, industry, and mining can lead to changes in the following environmental variables, the magnitude and direction of the change depending on the type, and the extent and intensity of human activities: riparian vegetation cover and diversity, litter inputs, solar irradiation, water temperature, DO concentration, water flow, channel form, sedimentation, and nutrient concentrations [76,[106][107][108][109][110]. Some activities can also result in the input of pharmaceuticals, pesticides, heavy metals, and organic pollution, which are generally not present in streams in the absence of human activities.…”