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Soil Generic Assessment Criteria for Human Health Risk ... - ESdat

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• Are all the exposure pathways used <strong>for</strong> the derivation of GAC appropriate at the site For example,<br />

the presence of hard-standing may prevent the generation of dusts and/or direct contact with<br />

soil;<br />

• Are the generic parameter values used <strong>for</strong> the derivation of GAC reasonable <strong>for</strong> the site For<br />

example, the residential GAC may not be protective <strong>for</strong> a house with a large garden used almost<br />

exclusively <strong>for</strong> the cultivation of homegrown fruit and vegetables.<br />

Like the SGV, the EIC/AGS/CL:AIRE GAC represent minimal or tolerable risk. As such, they present useful screening<br />

criteria <strong>for</strong> the assessment of risks. Care should be taken if adopting these values <strong>for</strong> other purposes, such as<br />

acceptance criteria <strong>for</strong> imported topsoil. Although the GAC may prove convenient screening criteria <strong>for</strong> this purpose<br />

it should always be recognised that they are based on generic assumptions and parameter values and that the<br />

development of site-specific assessment criteria protective of human health may be more appropriate at some<br />

sites.<br />

2.2.3<br />

Consultation<br />

Definition and Use<br />

One key difference between the EIC/AGS/CL:AIRE GAC and the SGV relates to the degree of consultation<br />

undertaken in their derivation / publication. The SGV (and associated HCV) have been derived by the Environment<br />

Agency of England and Wales in consultation with other Government departments and agencies, including the<br />

Food Standards Agency and the <strong>Health</strong> Protection Agency. The EIC/AGS/CL:AIRE GAC have not been subject to<br />

this level of consultation and unlike the SGV are not endorsed by DEFRA, the HPA or the Environment Agency of<br />

England and Wales.<br />

Nevertheless, the EIC/AGS/CL:AIRE GAC do carry a level of authority <strong>for</strong> the following reasons:<br />

• They have been derived using the CLEA model (v 1.06) in general accordance with the CLEA<br />

framework of guidance documents;<br />

• They have been researched and agreed on by a group of experienced human health risk assessors<br />

from 26 EIC and AGS member companies;<br />

• They have been subject to a high degree of internal review (see Sections 3.1.2 and 3.1.3); and<br />

• Various external authoritative bodies were invited to read and comment on a pre-publication<br />

version of the EIC/AGS/CL:AIRE GAC report (see Section 3.1.3). Comments were received from the<br />

Environment Agency of England and Wales, the Royal Environmental <strong>Health</strong> Institute of Scotland<br />

(REHIS), Environmental Protection UK, the Northern Ireland Environment Agency, the Chartered<br />

Institute of Environmental <strong>Health</strong> (CIEH) and the Scottish Environment Protection Agency (SEPA).<br />

These comments mostly related to the overall approach and wording of the main text and included<br />

recommendations <strong>for</strong> improving the clarity of the report. These comments have all been considered<br />

and with few exceptions addressed in the final version of the report. All of the comments significant<br />

to the derivation or application of the GAC have been addressed. Comments not addressed related<br />

to style and/or presentation of report. It is noteworthy that the Environment Agency of England<br />

and Wales commented that the approach described <strong>for</strong> derivation of the EIC/AGS/CL:AIRE GAC<br />

appeared to be broadly consistent with the CLEA guidance with some exceptions (which are<br />

highlighted in this report).<br />

It should be noted that none of the external authoritative bodies have carried out a detailed technical review of<br />

any of the recommended physico-chemico and toxicological properties or GAC values presented in this report.<br />

8

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