•Accumulation of PTEs In Agricultural Soils: A Case Study Showing The Inability of The Current Legal Order And Legislation to Address Ecosystem Services •T. Ginige & Dr. I.D. Green •Working Paper www.bournemouth.ac.uk Introduction • Primary Ecosystems Services provided by Agroecosystems. • Ecosystems processes within the soil. soil g • Soil microorganisms. www.bournemouth.ac.uk 2 Soils And Potentially Toxic Elements • Threat to soil health due to accumulation of p potentially y toxic elements –i.e. heavy metals within plough layer layer. • Limits set for Zinc and Copper www.bournemouth.ac.uk 3 The Problem With Organic Fertilisers • Organic by-products with sufficient nutrient content can be used as organic fertilisers, but these materials also l contain t i PTE PTEs. www.bournemouth.ac.uk 4 Copper And Zinc Concentrations In UK www.bournemouth.ac.uk 5 Time taken (yrs) for organic fertiliser applications to raise an average UK rural soil to the Cu limit. Mean conc. fertiliser High conc. fertiliser 180 kg N ha-1 250 kg N ha-1 180 kg N ha-1 250 kg N ha-1 Sewage sludge 153 110 115 83 Diary slurry 1527 1100 270 195 Dairy manure 1261 908 847 610 Pig slurry 546 394 238 171 Pi manure Pig 147 106 71 51 Layer manure 1619 1167 1403 1011 Broiler manure 1018 733 569 410 www.bournemouth.ac.uk 6 Time taken (yrs) for organic fertiliser applications to raise an average UK rural soil to the UK code of practice limit for Zn. Mean conc. fertiliser High conc. fertiliser 180 kg N ha-1 250 kg N ha-1 180 kg N ha-1 250 kg N ha-1 Sewage sludge 112 81 83 60 Diary slurry 473 340 136 98 Dairy manure 321 231 206 149 Pig slurry 346 250 80 57 Pig manure 133 96 80 58 Layer manure 237 171 172 124 Broiler manure 271 195 216 156 www.bournemouth.ac.uk 7 Legal controls on Sewage Sludge • Council Directive 86/278/EEC of 12 June 1986 on the protection of the environment and in particular of environment, the soil, when sewage sludge is used d in i agriculture i lt www.bournemouth.ac.uk 8 Legal controls on PTE in Agroecosystem • Directive 2002/32/EC of the European Parliament and of the Council of 7 May 2002 on undesirable substances in animal feed (OJ L 140, 140 30 30.5.2002, 5 2002 p p. 10–22) 10 22), • Commission Regulation (EC) No 1881/2006 of 19 December 2006 setting g maximum levels for certain contaminants in foodstuffs (OJ L 364, 20.12.2006, p. 5) • Inorganic g fertilisers, Regulation g ((EC)) No 2003/2003 of the European Parliament and of the Council of 13 October 2003 relating to fertilisers (OJ L 304, 21.11.2003, p. 1–194) does not provide for heavy metal limits www.bournemouth.ac.uk 9 Inability Of The Current Legal Order To Address Ecosystem Services • E Ecosystems t as the th word d suggests t are systems t instead of goods, services, buyers and sellers, the y are plants, p , animals,, elements of ecosystems minerals, water, air, chemicals, nutrients etc • There are not property rights attached to ES and absence renders them in many applications as public good resources and subject to under – provision and over depletion in the absence of some moderating influence www.bournemouth.ac.uk 10 Inability Of The Current Legal Order To Address Ecosystem Services • Modern environmental laws are extensive and wide ranging but are aimed at the wrong targets. • They y govern g subjects j like water taking, g forestry, endangered species, air pollution, pesticides, toxic substances, fish stocks, p waste management etc but do not protect y as systems. y ecosystems www.bournemouth.ac.uk 11 Inability Of The Current Legal Order To Address Ecosystem Services • They are based on the erroneous premise that it is possible to protect an element of an ecosystem without protecting p g the system y that p produces and supports pp it • e.g. Endangered species legislation typically focuses on the endangerment of species rather than on the decline off habitats. h bit t • In some legislative regimes listing a species as endangered e da ge ed triggers gge s so some e deg degree ee o of p protection o ec o for o that a species’ habitat. The focus is on the population of the animal rather than the state of the ecosystem within which it lives lives. • This approach is of questionable value www.bournemouth.ac.uk 12 Inability Of The Current Legal Order To Address Ecosystem Services • • • • • The same could Th ld b be said id off any attempt tt t tto protect t t ES rather th th than ecosystems themselves . Ecosystem services is not the same as ecosystem functions The critical difference between the two and which makes the development of ES policy both complicated and controversial is that ecosystem services have relevance only to the extent that human populations benefit from them. Theyy are purelyy anthropocentric ES are products of ecosystems; if ecosystems function is preserved and protected then ES will also be sustained. It is suggested that the rationale for protecting ecosystems may well be utilitarian or anthropocentric purpose of maintaining ES for human benefit, the way to maintain ES is not to target those services themselves but to protect the system that produces them themselves, them. The solution to dwindling ES is to protect ecosystem functions www.bournemouth.ac.uk 13 Way Forward? www.bournemouth.ac.uk 14 Tort Law - Nuisance www.bournemouth.ac.uk 15 Nuisance • Nuisance may be private ( affecting a particular individual or property) or public (impacting on a wider group of people) • Private Nuisance is concerned with the protection of proprietary rights and interests. • Its essence is to uphold the right to quiet enjoyment of one’s one s own land www.bournemouth.ac.uk 16 Nuisance • It is a requirement of Public Nuisance that a section of the public is affected and it lacks any requirement for a nexus between the nuisance and property. • Both torts raise issues of environmental protection as they cover topics such as a noise and p pollution,, but this is jjust a side effect of the scope of nuisance – it is aimed at protecting individuals not the environment generally www.bournemouth.ac.uk 17 Ecosystem services and it potential application in common law • The use of “ecosystem services” can extend the reach of the common law. • Public nuisance actions can be brought with regard to damage to ecosystems services, and can assist in framing of legal action to resist the damage or claim compensation. www.bournemouth.ac.uk 18 Conclusions • Potential damage posed by PTEs to soil fertility recognised (e.g. 86/278/EEC) • Current C t llegisalation i l ti anthropocentric th t i and dd does not protect ecosystem function • Thus, Th potential t ti l h harm tto ES via i Z Zn and dC Cu b build ild up in soil possible • Torts related to Private Nuisance may offer protection to ES provision www.bournemouth.ac.uk 19
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