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REFERENCES Broadmeadow S and Nisbet T (2005). The effects of riparian forest management on the freshwater environment: a literature review of best management practice. Hydrology and Earth System Sciences 8, 286–305. Carroll ZA, Bird SB, Emmett BA, Reynolds B and Sinclair FL (2004). Can tree shelter belts on agricultural land reduce flood risk? Soil Use and Management 20, 357– 359. Cree Valley Community Woodland Trust (2004). Sustainable forestry to protect water quality and aquatic biodiversity. Final Report on EU LIFE Project UK 182. CVCWT, Newton Stewart. Environment Change Research Centre (2001). Acidification of freshwaters: the role of nitrogen and the prospects for recovery. Environmental Change Research Centre Report No 79, University College London, London Forestry Commission (1988). Forests and Water Guidelines. Forestry Commission, Edinburgh. Forestry Commission (1998). The UK Forestry Standard. Forestry Commission, Edinburgh. Forestry Commission (2003). Forests and Water Guidelines. Fourth Edition. Forestry Commission, Edinburgh Forestry Commission (2004). The UK Forestry Standard. Second Edition. Forestry Commission, Edinburgh. Lees FM and Tervet DJ (1994). Final Report on the Effect of Fertiliser Application to the Ellergower Knowe Plantation. Solway River Purification Board, Dumfries. Neal C and Reynolds B (1998). The Impact of Conifer Harvesting and Replanting on Upland Water Quality. Environment Agency Research & Development Technical Report P211. Environment Agency, Bristol. Nisbet TR (1997). The sustainability of afforestation development within highland catchments supporting important salmonid fisheries – the Upper Halladale River. In: Forest Research Annual Report and Accounts 1997–1998. The Stationary Office, Edinburgh. Nisbet TR (2001). The role of forest management in controlling diffuse pollution in UK Forestry. Forest Ecology and Management 143, 215–226. Nisbet TR and Stonard JS (1995). The effect of aerial applications of urea fertiliser on stream water quality. Forestry Commission Research Information Note 266. Forestry Commission, Edinburgh. Nisbet TR, Fowler D and Smith IR (1995). An investigation of the impact of afforestation on stream-water chemistry in the Dee catchment, SW Scotland. Environmental Pollution 90, 111–120. 151
Nisbet TR, Orr H and Broadmeadow S (2004). A Guide to Using Woodland for Sediment Control. Forest Research, Farnham. Nisbet TR, Welch D and Doughty R (2002). The role of forest management in controlling diffuse pollution from the afforestation and clearfelling of two public water supply catchments in Argyll, West Scotland. Forest Ecology and Management 158, 141–154. Pratt JE, Nisbet TR, Tracy DR and Davidson J (1996). Boron content in surface water run-off from a clearfelled crop in West Scotland following stump treatment with Disodium octaborate tetrahydrate. Scandinavian Journal of Forest Research 11, 370–374. 152
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International Water Association AGR
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2006 Conference Organising Committe
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Theme 2: Cost-effectiveness of Best
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Poster Presentations The Farm Soils
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viii
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managers need support in understand
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During the past 20 years, it became
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infiltration); and (4) capture, sto
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DOMINATING PARAMETERS OF IMPAIRMENT
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Using the results of the unsupervis
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Kohonen T (2001). Self-Organizing M
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WATER FRAMEWORK DIRECTIVE IMPLEMENT
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Table 1: Modelled total annual loss
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• It should be possible to apply
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Scottish Executive against 18 measu
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REFERENCES Anthony S, Betson M, Lor
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ased on the ‘drainage basin’ in
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management practices’ (BMPs) toge
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It is envisaged that these data wil
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testing (including climate change)
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Council of the European Communities
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DECREASING THE NITROGEN SOIL SURFAC
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Table 1: Overview of the measures c
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Table 2: Costs (C), effects (E) and
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Figure 2: Combination of ‘best av
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MATERIALS AND METHODS At the 5-km 2
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REFERENCES Jordan P, Menary W, Daly
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Although the TMDL programme origina
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grassland and heather moorland, sup
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Given that the release of P from th
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to the underlying causes, and thus
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All water body use attainment infor
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indicate the possible presence of p
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DEVELOPMENT AND IMPLEMENTATION OF M
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BMP is being implemented and the ap
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THE USE OF PONDS TO REDUCE POLLUTIO
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established pond/wetland for nutrie
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Table 1: Hydraulic load, mean water
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Comparable SS removals have been re
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Reddy GB, Hunt PG, Phillips R, Ston
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In general, the combinations of mea
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final word on the POMs selection an
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CONCLUSIONS The ERBD project team i
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Table 1: A summary of the measures
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Table 3: A summary of the represent
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cost (£'000/farm) or reduction in
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ECONOMIC IMPLICATIONS OF MINIMISING
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spread cattle slurry in the autumn
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£25,000. The investment in trailin
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Studies on a drained clay soil at B
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REFERENCES Anon (2000). Fertiliser
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(Haygarth and Jarvis, 1999). The vo
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Application Representative farm sys
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Table 2: Modelled cost-curve for th
Page 109 and 110: ASSESSING THE SIGNIFICANCE OF DIFFU
Page 111 and 112: In the absence of data on the sourc
Page 113 and 114: Magnitude of Impacts The magnitude
Page 115 and 116: D. Use relative area of farm and wh
Page 117 and 118: ADAS has developed a matrix for Def
Page 119 and 120: Dickson JW, Edwards T, Jeffrey WA,
Page 121 and 122: 60% phosphorus and 50% nitrogen of
Page 123 and 124: RESULTS AND DISCUSSION Landscape St
Page 125 and 126: was contributed to the low vegetati
Page 127 and 128: iological uptake in a grassed area.
Page 129 and 130: Tim US, Jolly R and Liao HH (1995).
Page 131 and 132: to control SS and P loads from agri
Page 133 and 134: Total P inputs in fertilisers and m
Page 135 and 136: Within the Teme catchment, largest
Page 137 and 138: A RISK ASSESSMENT AND MITIGATION ST
Page 139 and 140: Environmental Monitoring The primar
Page 141 and 142: BMP measure 1 (exclusion of stock f
Page 143 and 144: (a) With reference to the increase
Page 145 and 146: ACKNOWLEDGEMENTS SAC acknowledges f
Page 147 and 148: The Environment Sensitive Farming (
Page 149 and 150: improved further as a result of att
Page 151 and 152: to do more to reduce pesticide impa
Page 153 and 154: MANAGING DIFFUSE POLLUTION FROM A F
Page 155 and 156: turbulent air mixing. The effect th
Page 157 and 158: Although nitrate leaching can be re
Page 159: infiltration of water sheeting off
Page 163 and 164: anthropogenic activities are pollut
Page 165 and 166: monitoring is determined up front b
Page 167 and 168: (USEPA). Nevertheless, by applying
Page 169 and 170: • Sampling equipment •Laborator
Page 171 and 172: Reinert RE, Knuth BA, Kamrin MA and
Page 173 and 174: Tier 3 - Tier 3 of LMCs is planned
Page 175 and 176: policy literature, although this is
Page 177 and 178: Figure 1: Individual-collective spe
Page 179 and 180: • tailoring activities to local c
Page 181 and 182: ACKNOWLEDGEMENTS The support of the
Page 183 and 184: THE EFFECT OF DIFFUSE POLLUTION FRO
Page 185 and 186: equires the Minister to designate a
Page 187 and 188: protection and restoration, sustain
Page 189 and 190: expensive. One-to-one contact becom
Page 191 and 192: farmers. In England, recent policy
Page 193 and 194: practices but, hopefully, the chang
Page 195 and 196: A CASE STUDY: ADOPTION OF BEST MANA
Page 197 and 198: The approaches taken by Brittany to
Page 199 and 200: MANURE TREATMENT By January 2005, t
Page 201 and 202: REGULATORY OPTIONS FOR THE MANAGEME
Page 203 and 204: There are also measures that contro
Page 205 and 206: widely recognised as needing much a
Page 207 and 208: ploughed, of rivers and streams tha
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PHOSPHORUS STORAGE IN FINE CHANNEL
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structure and minimum level of main
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REFERENCES May L, Place C, O’Hea
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LOUND CATCHMENT PROJECT: WORKING WI
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MINIMISING THE PRESSURES AND IMPACT
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Predicting Bathing Water Quality Vi
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Risk of illness percentages were ca
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Table 4: Expected lifetime benefits
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DETERMINATION OF THE VETERINARY ANT
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Thin Layer Chromatography The sampl
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Table 2: Regression functions and c
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OPPORTUNITIES AND CONSTRAINTS FOR U
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to land managers and agency staff t
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stakeholders, together with their i
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REFERENCES EC (2000). Directive 200
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A third scenario was applied to Clu
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Based on a detailed distribution of
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could be misleading. The results of
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TACKLING DIFFUSE NITRATE POLLUTION:
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AMMONIA VOLATILISATION FROM CATTLE
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and 27% of the soil surface at 80 m
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FIELD TESTING OF MITIGATION OPTIONS
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techniques can significantly reduce
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NITRATE CONTAMINATION OF GROUNDWATE
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MATERIALS AND METHODS At two UK sit
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ACKNOWLEDGEMENTS Funding of this wo
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y standard methods and fresh, end o
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comparable to those in water draini
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Results may be influential in deter
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• numbers and distribution of liv
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Using this method of classification
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Table 5: Results of land use scenar
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CONCLUSIONS As a decision support t
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types. This paper reports results f
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N Losses in Drainage Water Mean nit
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SOIL AND CROP MANAGEMENT EFFECTS ON
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treatments, typically 10 storm even
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Tramline Effects In both years, obs
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Notes 278
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