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      Small Water Bodies in Great Britain and Ireland: Ecosystem function, human-generated degradation, and options for restorative action

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          Abstract

          Small, 1st and 2nd-order, headwater streams and ponds play essential roles in providing natural flood control, trapping sediments and contaminants, retaining nutrients, and maintaining biological diversity, which extend into downstream reaches, lakes and estuaries. However, the large geographic extent and high connectivity of these small water bodies with the surrounding terrestrial ecosystem makes them particularly vulnerable to growing land-use pressures and environmental change. The greatest pressure on the physical processes in these waters has been their extension and modification for agricultural and forestry drainage, resulting in highly modified discharge and temperature regimes that have implications for flood and drought control further downstream. The extensive length of the small stream network exposes rivers to a wide range of inputs, including nutrients, pesticides, heavy metals, sediment and emerging contaminants. Small water bodies have also been affected by invasions of non-native species, which along with the physical and chemical pressures, have affected most groups of organisms with consequent implications for the wider biodiversity within the catchment. Reducing the impacts and restoring the natural ecosystem function of these water bodies requires a three-tiered approach based on: restoration of channel hydromorphological dynamics; restoration and management of the riparian zone; and management of activities in the wider catchment that have both point-source and diffuse impacts. Such activities are expensive and so emphasis must be placed on integrated programmes that provide multiple benefits. Practical options need to be promoted through legislative regulation, financial incentives, markets for resource services and voluntary codes and actions.

          Graphical abstract

          Highlights

          • Small Water Bodies (SWB) provide a suite of vital ecosystem services.

          • Hydromorphology of SWBs makes them highly vulnerable to anthropogenic pressures.

          • Land-use and environmental changes are disrupting the ecosystem functions of SWBs.

          • 3-tier restoration is needed: channel, riparian and wider catchment management.

          • Success will require government prioritization, expert advice, and stakeholder buy-in.

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          Most cited references224

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          Microplastics in freshwater and terrestrial environments: Evaluating the current understanding to identify the knowledge gaps and future research priorities.

          Plastic debris is an environmentally persistent and complex contaminant of increasing concern. Understanding the sources, abundance and composition of microplastics present in the environment is a huge challenge due to the fact that hundreds of millions of tonnes of plastic material is manufactured for societal use annually, some of which is released to the environment. The majority of microplastics research to date has focussed on the marine environment. Although freshwater and terrestrial environments are recognised as origins and transport pathways of plastics to the oceans, there is still a comparative lack of knowledge about these environmental compartments. It is highly likely that microplastics will accumulate within continental environments, especially in areas of high anthropogenic influence such as agricultural or urban areas. This review critically evaluates the current literature on the presence, behaviour and fate of microplastics in freshwater and terrestrial environments and, where appropriate, also draws on relevant studies from other fields including nanotechnology, agriculture and waste management. Furthermore, we evaluate the relevant biological and chemical information from the substantial body of marine microplastic literature, determining the applicability and comparability of this data to freshwater and terrestrial systems. With the evidence presented, the authors have set out the current state of the knowledge, and identified the key gaps. These include the volume and composition of microplastics entering the environment, behaviour and fate of microplastics under a variety of environmental conditions and how characteristics of microplastics influence their toxicity. Given the technical challenges surrounding microplastics research, it is especially important that future studies develop standardised techniques to allow for comparability of data. The identification of these research needs will help inform the design of future studies, to determine both the extent and potential ecological impacts of microplastic pollution in freshwater and terrestrial environments.
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            Assessing the effects of climate change on aquatic invasive species.

            Different components of global environmental change are typically studied and managed independently, although there is a growing recognition that multiple drivers often interact in complex and nonadditive ways. We present a conceptual framework and empirical review of the interactive effects of climate change and invasive species in freshwater ecosystems. Climate change is expected to result in warmer water temperatures, shorter duration of ice cover, altered streamflow patterns, increased salinization, and increased demand for water storage and conveyance structures. These changes will alter the pathways by which non-native species enter aquatic systems by expanding fish-culture facilities and water gardens to new areas and by facilitating the spread of species during floods. Climate change will influence the likelihood of new species becoming established by eliminating cold temperatures or winter hypoxia that currently prevent survival and by increasing the construction of reservoirs that serve as hotspots for invasive species. Climate change will modify the ecological impacts of invasive species by enhancing their competitive and predatory effects on native species and by increasing the virulence of some diseases. As a result of climate change, new prevention and control strategies such as barrier construction or removal efforts may be needed to control invasive species that currently have only moderate effects or that are limited by seasonally unfavorable conditions. Although most researchers focus on how climate change will increase the number and severity of invasions, some invasive coldwater species may be unable to persist under the new climate conditions. Our findings highlight the complex interactions between climate change and invasive species that will influence how aquatic ecosystems and their biota will respond to novel environmental conditions.
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              Large microplastic particles in sediments of tributaries of the River Thames, UK - Abundance, sources and methods for effective quantification.

              Sewage effluent input and population were chosen as predictors of microplastic presence in sediments at four sites in the River Thames basin (UK). Large microplastic particles (1mm-4mm) were extracted using a stepwise approach to include visual extraction, flotation and identification using Raman spectroscopy. Microplastics were found at all four sites. One site had significantly higher numbers of microplastics than other sites, average 66 particles 100g(-1), 91% of which were fragments. This site was downstream of a storm drain outfall receiving urban runoff; many of the fragments at this site were determined to be derived of thermoplastic road-surface marking paints. At the remaining three sites, fibres were the dominant particle type. The most common polymers identified included polypropylene, polyester and polyarylsulphone. This study describes two major new findings: presence of microplastic particles in a UK freshwater system and identification of road marking paints as a source of microplastics.
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                Author and article information

                Contributors
                Journal
                Sci Total Environ
                Sci. Total Environ
                The Science of the Total Environment
                Elsevier
                0048-9697
                1879-1026
                15 December 2018
                15 December 2018
                : 645
                : 1598-1616
                Affiliations
                [a ]The Centre for Environment, Fisheries & Aquaculture Science, Lowestoft Laboratory, Lowestoft, Suffolk, NR33 0HT, UK
                [b ]Freshwater Habitats Trust, Bury Knowle House, North Place, Oxford, OX3 9HY, UK
                [c ]Sustainable Agriculture Sciences, Rothamsted Research, North Wyke, Okehampton, Devon EX20 2SB, UK
                [d ]NERC Centre for Ecology & Hydrology, Maclean Building, Crowmarsh Gifford, Wallingford, Oxfordshire OX10 8BB, UK
                [e ]Queen Mary University of London, The River Laboratory, East Stoke, Wareham, Dorset BH20 6BB, UK
                [f ]School of Biology & Environmental Science, University College Dublin, Belfield, Dublin 4, Ireland
                [g ]UK Cardiff School of Biosciences and Water Research Institute, Cardiff University, Cardiff CF10 3AX, UK
                [h ]Department of Geography & Environment, University of Southampton, Highfield, Southampton, Hampshire SO17 1BJ, UK
                [i ]Department of Geography, Loughborough University, Loughborough, Leicestershire LE11 3TU, UK
                [j ]Forestry Commission, Forest Research, Alice Holt Lodge, Farnham, Surrey GU10 4LH, UK
                [k ]Environment Department, University of York, Wentworth Way, Heslington, York, Yorkshire YO10 5NG, UK
                [l ]North View Cottage, Union Road, Crediton, Devon EX17 3AL, UK
                [m ]Hull International Fisheries Institute, School of Biological, Biomedical and Environmental Sciences, The University of Hull, Hull, East Yorkshire HU6 7RX, UK
                [n ]RSPCA Wildlife Department, Wilberforce Way, Southwater, West Sussex RH13 9RS, UK
                [o ]Department of GeoData, University of Southampton, Highfield, Southampton, Hampshire SO17 1BJ, UK
                [p ]Environment Agency, Lateral, 8 City Walk, Leeds, Yorkshire LS11 9AT, UK
                [q ]11 Monteigne Drive, Bowburn, Durham DH6 5QB, UK
                [r ]River Restoration Centre, Cranfield University, Cranfield, Bedfordshire MK43 0AL, UK
                [s ]Waterland Management Ltd, 4a Spa Hill, Kirton Lindsey, Gainsborough, Lincolnshire, DN21 4NE, UK
                [t ]British Trust for Ornithology, The Nunnery, Thetford, Norfolk, IP24 2PU, UK
                Author notes
                [* ]Corresponding author. bill.riley@ 123456cefas.co.uk
                Article
                S0048-9697(18)32726-8
                10.1016/j.scitotenv.2018.07.243
                6162339
                30248877
                01e265e2-736e-4bc4-87f6-83c5a52a51b4
                Crown Copyright © 2018 Published by Elsevier B.V. All rights reserved.
                History
                : 4 May 2018
                : 16 July 2018
                : 17 July 2018
                Categories
                Article

                General environmental science
                streams,ponds,headwaters,anthropogenic pressures,remediation,ecosystem services

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