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

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3<br />

3.1<br />

Methodology<br />

Overview of Process<br />

The project was conducted over a number of phases detailed below.<br />

3.1.1<br />

Phase 1: Project scoping<br />

A scoping study was conducted in December 2008 to assess the level of ef<strong>for</strong>t required to produce GAC compliant<br />

with the current CLEA methodology and to enable realistic goals and timescales to be set <strong>for</strong> the project. Contributing<br />

organisations were asked to indicate the contaminants <strong>for</strong> which they had previously derived GAC. This resulted in<br />

a list of a possible 150+ substances. These were ranked according to the number of consultants that had derived<br />

GAC <strong>for</strong> each substance and the top 44 contaminants were selected. In preparing the priority list, the project team<br />

conferred with both the Environment Agency of England and Wales and LQM/CIEH to ensure that there was no<br />

duplication of ef<strong>for</strong>t with the <strong>for</strong>thcoming publication of SGV or LQM/CIEH GAC.<br />

A workshop was held in February 2009 <strong>for</strong> all participating organisations to finalise the list of contaminants, agree<br />

procedures <strong>for</strong> the collation of data and peer review, allocate tasks and set the project schedule.<br />

3.1.2<br />

Phase 2: Data compilation and peer review<br />

Methodology<br />

Phase 2 involved the collation of data, selection of appropriate contaminant specific parameter values <strong>for</strong> use in<br />

the CLEA model and peer review. To ensure that this process was efficient and transparent as possible, a series<br />

of pro<strong>for</strong>mas were designed to capture the relevant data and justify why particular parameter values had been<br />

chosen. This ensured that the process of collecting data and selecting parameter values was consistent <strong>for</strong> all 44<br />

contaminants reviewed.<br />

Each contaminant had three pro<strong>for</strong>mas as described in Table 3.1. The finalised pro<strong>for</strong>mas <strong>for</strong> all 44 contaminants<br />

are provided in Appendix B. Further details of the contents of these pro<strong>for</strong>mas are provided in Sections 3.2, 3.3<br />

and 3.4.<br />

Table 3.1: Pro<strong>for</strong>mas used <strong>for</strong> data collation and parameter value selection<br />

Pro<strong>for</strong>ma<br />

<strong>Health</strong> <strong>Criteria</strong> Values<br />

Mean Daily Intakes<br />

Physico-chemical<br />

Properties<br />

Description<br />

Used to present pertinent toxicological in<strong>for</strong>mation from authoritative bodies. Pro<strong>for</strong>ma<br />

also shows recommended health criteria values and justification <strong>for</strong> the choice of values.<br />

Used to present pertinent background exposure in<strong>for</strong>mation. Pro<strong>for</strong>ma also shows<br />

recommended mean daily intake values and justification <strong>for</strong> the choice of values.<br />

Used to present relevant physico-chemical in<strong>for</strong>mation from authoritative data sources.<br />

Pro<strong>for</strong>ma also shows recommended physico-chemical parameter values and justification<br />

<strong>for</strong> the choice of values.<br />

Each of the 26 volunteering organisations was generally allocated 3 to 4 contaminants to review (although some<br />

reviewed up to 6 contaminants). Peer review partners were assigned so that each group of contaminants was<br />

allocated to two volunteering organisations. This ensured that each contaminant was independently researched<br />

by a pair of volunteers.<br />

11

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