Journal articles

The British river of the future: how climate change and human activity might affect two contrasting river ecosystems in England

Andrew C. Johnston, Centre for Ecology and Hydrology, Wallingford
Michael C. Acreman, Centre for Ecology and Hydrology, Wallingford
Michael J. Dunbar, Centre for Ecology and Hydrology, Wallingford
Stephen W. Feist, CEFAS Weymouth Laboratory
Anna Marie Giacomello, Centre for Ecology and Hydrology, Wallingford
Rodolph E. Gozlan, Centre for Ecology and Hydrology, Wallingford
Shelley A. Hinsley, Centre for Ecology and Hydrology, Monks Wood
Anton T. Ibbotson, Centre for Ecology and Hydrology, Wallingford
Helen P. Jarvie, Centre for Ecology and Hydrology, Wallingford
J Iwan Jones, Centre for Ecology and Hydrology, Wallingford
Matt Longshaw, CEFAS Weymouth Laboratory
Stephen C. Maberly, Centre for Ecology and Hydrology, Bailrigg
Terry J. Marsh, Centre for Ecology and Hydrology, Wallingford
Colin Neal, Centre for Ecology and Hydrology, Wallingford
Jonathon R. Newman, Centre for Ecology and Hydrology, Wallingford
Miles A. Nunn, Centre for Ecology and Hydrology, Oxford
Roger W. Pickup, Centre for Ecology and Hydrology, Bailrigg
Nick S. Reynard, Centre for Ecology and Hydrology, Wallingford
Caroline A. Sullivan, Southern Cross University
John P. Sumpter, Brunel University
Richard J. Williams, Centre for Ecology and Hydrology, Wallingford

Abstract

The possible effects of changing climate on a southern and a north-eastern English river (the Thames and the Yorkshire Ouse, respectively) were examined in relation to water and ecological quality throughout the food web. The CLASSIC hydrological model, driven by output from the Hadley Centre climate model (HadCM3), based on IPCC low and high CO2 emission scenarios for 2080 were used as the basis for the analysis. Compared to current conditions, the CLASSIC model predicted lower flows for both rivers, in all seasons except winter. Such an outcome would lead to longer residence times (by up to a month in the Thames), with nutrient, organic and biological contaminant concentrations elevated by 70–100% pro-rata, assuming sewage treatment effectiveness remains unchanged. Greater opportunities for phytoplankton growth will arise, and this may be significant in the Thames. Warmer winters and milder springs will favour riverine birds and increase the recruitment of many coarse fish species. However, warm, slow-flowing, shallower water would increase the incidence of fish diseases. These changing conditions would make southern UK rivers in general a less favourable habitat for some species of fish, such as the Atlantic salmon (Salmo salar). Accidental or deliberate, introductions of alien macrophytes and fish may change the range of species in the rivers. In some areas, it is possible that a concurrence of different pressures may give rise to the temporary loss of ecosystem services, such as providing acceptable quality water for humans and industry. An increasing demand for water in southern England due to an expanding population, a possibly reduced flow due to climate change, together with the Water Framework Directive obligation to maintain water quality, will put extreme pressure on river ecosystems, such as the Thames.