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Exploring the Use of Species Sensitivity Distributions to Define Protective Limits for the Use of Organic Wastes as Soil Amendments.
Renaud, Mathieu; Chelinho, Sónia; Alvarenga, Paula; Mourinha, Clarisse; Palma, Patrícia; Sousa, José Paulo; Natal-da-Luz, Tiago.
Afiliação
  • Renaud M; Centre for Functional Ecology, Department of Life Sciences, University of Coimbra, Calçada Martim de Freitas, Coimbra, Portugal.
  • Chelinho S; Centre for Functional Ecology, Department of Life Sciences, University of Coimbra, Calçada Martim de Freitas, Coimbra, Portugal.
  • Alvarenga P; Linking Landscape, Environment, Agriculture, and Food Research Unit, School of Agronomy, University of Lisbon, Tapada da Ajuda, Lisbon, Portugal.
  • Mourinha C; Department of Applied Sciences and Technologies, Polytechnic Institute of Beja, Beja, Portugal.
  • Palma P; Department of Applied Sciences and Technologies, Polytechnic Institute of Beja, Beja, Portugal.
  • Sousa JP; Institute of Earth Sciences, University of Évora, Évora, Portugal.
  • Natal-da-Luz T; Centre for Functional Ecology, Department of Life Sciences, University of Coimbra, Calçada Martim de Freitas, Coimbra, Portugal.
Environ Toxicol Chem ; 38(7): 1569-1576, 2019 07.
Article em En | MEDLINE | ID: mdl-30985941
ABSTRACT
The use of organic wastes as soil amendments can be an important measure to improve soil quality and reduce waste accumulation and landfilling. However, the potential contaminant loads of such wastes, can be a source of environmental concern. Consequently, legislation has been developed to regulate the use of these wastes in agricultural soils. However, the regulations only consider chemical parameters, which are insufficient to establish the level of environmental risk. A possible solution is the use of species sensitivity distributions (SSDs), employing ecotoxicological data from test batteries that could be incorporated into legislation. In the present study, 2 different hazardous concentrations affecting 5 and 50% of the soil community (HC5 and HC50, respectively) were determined using ecotoxicological data (effect concentrations, 10 and 50% [EC10 and EC50, respectively]) for 5 different wastes. The results demonstrate that, as expected, current legislative thresholds do not translate to environmental risk/protection and that SSDs may be an important tool allowing the simple inclusion and interpretation of ecotoxicological data from test batteries in legislation. On the other hand, SSDs must be used with caution because there are still doubts about their actual value in risk prediction and about which estimates provide adequate protection. For instance, the use of HC50EC10 values is not recommended; these values overlap with the more conservative HC5EC50 data, highlighting the fact that the use of lower effect concentrations may not always provide the most protective approach. Also, hazardous concentrations need to be calibrated at the field or semifield level, to verify environmental protection in different soils/environments and the adequacy of standard test organisms. Environ Toxicol Chem 2019;381569-1576. © 2019 SETAC.
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Texto completo: 1 Coleções: 01-internacional Base de dados: MEDLINE Assunto principal: Esgotos / Poluentes do Solo Tipo de estudo: Diagnostic_studies / Prognostic_studies Limite: Animals Idioma: En Revista: Environ Toxicol Chem Ano de publicação: 2019 Tipo de documento: Article País de afiliação: Portugal

Texto completo: 1 Coleções: 01-internacional Base de dados: MEDLINE Assunto principal: Esgotos / Poluentes do Solo Tipo de estudo: Diagnostic_studies / Prognostic_studies Limite: Animals Idioma: En Revista: Environ Toxicol Chem Ano de publicação: 2019 Tipo de documento: Article País de afiliação: Portugal