Abstract
Climate change represents a major threat to lotic freshwater ecosystems and their ability to support the provision of ecosystem services. England’s chalk streams are in a poor state of health, with significant concerns regarding their resilience, the ability to adapt, under a changing climate. This paper aims to quantify the effect of climate change on hydroecological response for the River Nar, south-east England. To this end, we apply a coupled hydrological and hydroecological modelling framework, with the UK probabilistic climate projections 2009 (UKCP09) weather generator serving as input (CMIP3 A1B high emissions scenario, 2021 to the end-of-century). The results indicate a minimal change in the long-term mean hydroecological response over this period. In terms of interannual variability, the median hydroecological response is subject to increased uncertainty, whilst lower probability extremes are virtually certain to become more homogeneous (assuming a high emissions scenario). A functional matrix, relating species-level macroinvertebrate functional flow preferences to functional food groups reveals that, on the baseline, under extreme conditions, key groups are underrepresented. To date, despite this limited range, the River Nar has been able to adapt to extreme events due to interannual variation. In the future, this variation is greatly reduced, raising real concerns over the resilience of the river ecosystem, and chalk ecosystems more generally, under climate change.
Highlights
Under the Convention on Biological Diversity, biodiversity is defined as the variability among living organisms, within & between species and ecosystems [1,2]
The aim of this paper was to quantify the effect of climate change on hydroecological response in terms of both long-term change and interannual variability
A coupled hydrological and hydroecological modelling framework was forced with UK probabilistic climate projections 2009 (UKCP09) high emissions (CMIP3 A1B)
Summary
Under the Convention on Biological Diversity, biodiversity is defined as the variability among living organisms, within & between species and ecosystems [1,2]. The societal cost of biodiversity loss, in terms of ecosystem functionality, may be severe. Increased diversity fosters greater productivity of ecosystem functions; The diversity-stability hypothesis [5] states that biodiversity introduces redundancy in the system, thereby introducing both resistance and resilience to environmental change; The loss of certain species may have keystone effects which cascade through the ecosystem [6]; for example, Woodward, et al [7] observed that the presence and absence of freshwater shrimp (Gammarus pulex), a dominant predator in chalk streams, exerted a strong influence on detrital processing rates.
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