Schedule B1: Guideline on investigation levels for soil & groundwater
Schedule B1: Guideline on investigation levels for soil & groundwater
Schedule B1: Guideline on investigation levels for soil & groundwater
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Evaluati<strong>on</strong> and c<strong>on</strong>clusi<strong>on</strong><br />
The results indicate a human health risk from TCE, PCE and derivatives to ground floor<br />
occupants of the office building. The results indicate that appropriate resp<strong>on</strong>ses to protect<br />
human health, further management/assessment such as indoor air sampling to determine<br />
actual exposure and detailed health risk assessment and mitigati<strong>on</strong> measures are required.<br />
This assessment is limited to health risk c<strong>on</strong>siderati<strong>on</strong>s from VOCC exposure and does not<br />
c<strong>on</strong>sider any ecological risks related to <strong>soil</strong> and <strong>groundwater</strong> c<strong>on</strong>taminati<strong>on</strong>, <strong>for</strong> example,<br />
infiltrati<strong>on</strong> into sewer or stormwater drainage systems or discharge into a sensitive receptor.<br />
3.4.1 Ecological assessment<br />
EILs and ESLs provide screening criteria to assess the effect of c<strong>on</strong>taminants <strong>on</strong> a <strong>soil</strong><br />
ecosystem. They af<strong>for</strong>d the specified level of species protecti<strong>on</strong> within the SSD framework<br />
<strong>for</strong> organisms that frequent or inhabit <strong>soil</strong> and protect essential <strong>soil</strong> processes.<br />
<str<strong>on</strong>g>Schedule</str<strong>on</strong>g> A provides an overview of the site assessment process and the applicati<strong>on</strong> of<br />
investigati<strong>on</strong> and screening <strong>levels</strong> <strong>for</strong> site-specific Tier 1 human health and ecological risk<br />
assessment. While human health will drive the first stages of assessment, ecological<br />
assessment will need c<strong>on</strong>siderati<strong>on</strong> <strong>for</strong> all sites. Human health c<strong>on</strong>cerns may be addressed<br />
by the HSLs <strong>for</strong> petroleum hydrocarb<strong>on</strong>s. However, there are many HSLs that are denoted<br />
as NL (refer footnotes to HSL Tables) and high <strong>levels</strong> of petroleum hydrocarb<strong>on</strong>s, including<br />
free phase, may be present at the site. Similarly, many HILs <strong>for</strong> individual elements or<br />
compounds are elevated above the EILs.<br />
In these circumstances, ecosystem risks may become the driver <strong>for</strong> site assessment. In other<br />
sites impacted by petroleum hydrocarb<strong>on</strong>s, human health and ecological risks and protecti<strong>on</strong><br />
of <strong>groundwater</strong> resources may be addressed and ‘management limits’ applied to ensure that<br />
phase separated hydrocarb<strong>on</strong> and associated risks are appropriately c<strong>on</strong>sidered.<br />
3.4.1.1 Other c<strong>on</strong>siderati<strong>on</strong>s in assessing ecological risks<br />
In assessing the overall risk to the ecosystem from <strong>soil</strong> c<strong>on</strong>taminati<strong>on</strong> the following sitespecific<br />
aspects should be c<strong>on</strong>sidered with relevant ecological <strong>soil</strong> criteria and management<br />
limits:<br />
• the locati<strong>on</strong> of the site in relati<strong>on</strong> to any sensitive receptors, e.g. watercourses, estuaries,<br />
<strong>groundwater</strong> resources, sensitive ecological areas<br />
• the existing or proposed land use<br />
• the presentati<strong>on</strong> of any c<strong>on</strong>taminants including areal extent, depth below finished<br />
ground level, the presence of barriers or c<strong>on</strong>tainment that prevents or minimises the<br />
migrati<strong>on</strong> of c<strong>on</strong>taminati<strong>on</strong><br />
• the in-situ leaching characteristics of c<strong>on</strong>taminants of c<strong>on</strong>cern and the potential <strong>for</strong><br />
leachate to adversely affect any accessible sensitive receptor<br />
• the potential <strong>for</strong> any <strong>soil</strong> c<strong>on</strong>taminant to be transported from the site at <strong>levels</strong> of c<strong>on</strong>cern<br />
by erosive <strong>for</strong>ces.<br />
Site c<strong>on</strong>siderati<strong>on</strong>s in additi<strong>on</strong> to the land-use categories will determine if any additi<strong>on</strong>al<br />
assessment is required to address identified risks. For example, <strong>soil</strong> c<strong>on</strong>taminants may cause<br />
adverse ecological effects when the c<strong>on</strong>taminant is in a highly leachable <strong>for</strong>m or is<br />
incorporated in exposed readily erodible <strong>soil</strong>. In this situati<strong>on</strong> the c<strong>on</strong>taminant may be at risk<br />
of being transported off site by water and wind acti<strong>on</strong>.<br />
<str<strong>on</strong>g>Schedule</str<strong>on</strong>g> B (1) - <str<strong>on</strong>g>Guideline</str<strong>on</strong>g> <strong>on</strong> Investigati<strong>on</strong> Levels <strong>for</strong> Soil and Groundwater 26