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Characterization of Phosphorus Sources in Rural Watersheds
Corresponding Author
P. J. A. Withers
Environment Group, ADAS Gleadthorpe, Meden Vale, Mansfield, Nottinghamshire, NG20 9PF
Corresponding author ([email protected]).Search for more papers by this authorH. P. Jarvie
Centre for Ecology and Hydrology, Maclean Building, Crowmarsh Gifford, Wallingford, Oxfordshire, OX10 8BB
Search for more papers by this authorR. A. Hodgkinson
Environment Group, ADAS Gleadthorpe, Meden Vale, Mansfield, Nottinghamshire, NG20 9PF
Search for more papers by this authorE. J. Palmer-Felgate
Centre for Ecology and Hydrology, Maclean Building, Crowmarsh Gifford, Wallingford, Oxfordshire, OX10 8BB
Search for more papers by this authorA. Bates
Environment Group, ADAS Gleadthorpe, Meden Vale, Mansfield, Nottinghamshire, NG20 9PF
Search for more papers by this authorM. Neal
Centre for Ecology and Hydrology, Maclean Building, Crowmarsh Gifford, Wallingford, Oxfordshire, OX10 8BB
Search for more papers by this authorR. Howells
Environment Group, ADAS Gleadthorpe, Meden Vale, Mansfield, Nottinghamshire, NG20 9PF
Search for more papers by this authorC. M. Withers
Environment Group, ADAS Gleadthorpe, Meden Vale, Mansfield, Nottinghamshire, NG20 9PF
Search for more papers by this authorH. D. Wickham
Centre for Ecology and Hydrology, Maclean Building, Crowmarsh Gifford, Wallingford, Oxfordshire, OX10 8BB
Search for more papers by this authorCorresponding Author
P. J. A. Withers
Environment Group, ADAS Gleadthorpe, Meden Vale, Mansfield, Nottinghamshire, NG20 9PF
Corresponding author ([email protected]).Search for more papers by this authorH. P. Jarvie
Centre for Ecology and Hydrology, Maclean Building, Crowmarsh Gifford, Wallingford, Oxfordshire, OX10 8BB
Search for more papers by this authorR. A. Hodgkinson
Environment Group, ADAS Gleadthorpe, Meden Vale, Mansfield, Nottinghamshire, NG20 9PF
Search for more papers by this authorE. J. Palmer-Felgate
Centre for Ecology and Hydrology, Maclean Building, Crowmarsh Gifford, Wallingford, Oxfordshire, OX10 8BB
Search for more papers by this authorA. Bates
Environment Group, ADAS Gleadthorpe, Meden Vale, Mansfield, Nottinghamshire, NG20 9PF
Search for more papers by this authorM. Neal
Centre for Ecology and Hydrology, Maclean Building, Crowmarsh Gifford, Wallingford, Oxfordshire, OX10 8BB
Search for more papers by this authorR. Howells
Environment Group, ADAS Gleadthorpe, Meden Vale, Mansfield, Nottinghamshire, NG20 9PF
Search for more papers by this authorC. M. Withers
Environment Group, ADAS Gleadthorpe, Meden Vale, Mansfield, Nottinghamshire, NG20 9PF
Search for more papers by this authorH. D. Wickham
Centre for Ecology and Hydrology, Maclean Building, Crowmarsh Gifford, Wallingford, Oxfordshire, OX10 8BB
Search for more papers by this authorAll rights reserved. No part of this periodical may be reproduced or transmitted in any form or by any means, electronic or mechanical, including photocopying, recording, or any information storage and retrieval system, without permission in writing from the publisher.
Abstract
Correct identification of P sources in rural watersheds is critical for the development of cost-effective measures to combat agriculturally-driven eutrophication. The chemical composition of various storm runoff types (field surface runoff, field drain outfalls, roads, farmyards, and septic tanks) and the receiving streams in three micro (<10 km2) watersheds of varying agricultural intensity were monitored over a 2-yr period. Mean weekly stream soluble reactive phosphorus (SRP) and total phosphorus (TP) concentrations increased from 29 and 69 μg L−1, respectively in the watershed with the lowest intensity agriculture to 382 and 503 μg L−1, respectively in the watershed with high intensity agriculture and a village sewage treatment works. Concentrations of TP in storm runoff varied by up to two orders of magnitude reflecting the complex origins, routing, and composition of contributing source areas. Application of the DESPRAL test suggested field runoff TP concentrations were influenced by both P and organic matter in soil. However, runoff from impervious surfaces (farmyard and roads), and/or influenced by septic tank discharges, was significantly more concentrated (0.08–16 mg TP L−1, mean ≫1 mg L−1) than surface and subsurface runoff from cultivated land and pasture (0.02–3.6 mg TP L−1, mean <1 mg L−1), and/or contained a significantly greater proportion (>50% vs. <50%) of P in dissolved forms. It is concluded that P sources associated with the functioning of rural communities (impervious surfaces, detergents, and wastewater) may be more ecologically relevant than those associated with agriculture and should be better quantified and controlled to avoid localized eutrophication impacts.
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