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An exploration of spatial risk assessment for soil protection: estimating risk and establishing priority areas for soil protection.
Kibblewhite, M G; Bellamy, P H; Brewer, T R; Graves, A R; Dawson, C A; Rickson, R J; Truckell, I; Stuart, J.
Afiliação
  • Kibblewhite MG; Department of Environmental Science and Technology, School of Applied Sciences, Cranfield University, Bedfordshire, MK43 0AL, United Kingdom.
  • Bellamy PH; Department of Environmental Science and Technology, School of Applied Sciences, Cranfield University, Bedfordshire, MK43 0AL, United Kingdom.
  • Brewer TR; Department of Environmental Science and Technology, School of Applied Sciences, Cranfield University, Bedfordshire, MK43 0AL, United Kingdom.
  • Graves AR; Department of Environmental Science and Technology, School of Applied Sciences, Cranfield University, Bedfordshire, MK43 0AL, United Kingdom.
  • Dawson CA; Department of Environmental Science and Technology, School of Applied Sciences, Cranfield University, Bedfordshire, MK43 0AL, United Kingdom.
  • Rickson RJ; Department of Environmental Science and Technology, School of Applied Sciences, Cranfield University, Bedfordshire, MK43 0AL, United Kingdom.
  • Truckell I; Department of Environmental Science and Technology, School of Applied Sciences, Cranfield University, Bedfordshire, MK43 0AL, United Kingdom.
  • Stuart J; Department for the Environment, Food and Rural Affairs (Defra), Horseferry Road, London, SW1P 2AL, United Kingdom.
Sci Total Environ ; 473-474: 692-701, 2014 Mar 01.
Article em En | MEDLINE | ID: mdl-24412915
ABSTRACT
Methods for the spatial estimation of risk of harm to soil by erosion by water and wind and by soil organic matter decline are explored. Rates of harm are estimated for combinations of soil type and land cover (as a proxy for hazard frequency) and used to estimate risk of soil erosion and loss of soil organic carbon (SOC) for 1 km(2)pixels. Scenarios are proposed for defining the acceptability of risk of harm to soil the most precautionary one corresponds to no net harm after natural regeneration of soil (i.e. a 1 in 20 chance of exceeding an erosion rate of <1 tha(-1)y(-1) and SOC content decline of 0 kg t(-1)y(-1) for mineral soils and a carbon stock decline of 0 tha(-1)y(-1) for organic soils). Areas at higher and lower than possible acceptable risk are mapped. The veracity of boundaries is compromised if areas of unacceptable risk are mapped to administrative boundaries. Errors in monitoring change in risk of harm to soil and inadequate information on risk reduction measures' efficacy, at landscape scales, make it impossible to use or monitor quantitative targets for risk reduction adequately. The consequences for priority area definition of expressing varying acceptable risk of harm to soil as a varying probability of exceeding a fixed level of harm, or, a varying level of harm being exceeded with a fixed probability, are discussed. Soil data and predictive models for rates of harm to soil would need considerable development and validation to implement a priority area approach robustly.
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Texto completo: 1 Coleções: 01-internacional Base de dados: MEDLINE Contexto em Saúde: 2_ODS3 Problema de saúde: 2_quimicos_contaminacion Assunto principal: Solo / Carbono / Monitoramento Ambiental / Conservação dos Recursos Naturais Tipo de estudo: Etiology_studies / Prognostic_studies / Risk_factors_studies Idioma: En Revista: Sci Total Environ Ano de publicação: 2014 Tipo de documento: Article País de afiliação: Reino Unido

Texto completo: 1 Coleções: 01-internacional Base de dados: MEDLINE Contexto em Saúde: 2_ODS3 Problema de saúde: 2_quimicos_contaminacion Assunto principal: Solo / Carbono / Monitoramento Ambiental / Conservação dos Recursos Naturais Tipo de estudo: Etiology_studies / Prognostic_studies / Risk_factors_studies Idioma: En Revista: Sci Total Environ Ano de publicação: 2014 Tipo de documento: Article País de afiliação: Reino Unido
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