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REFERENCE DOCUMENTS - RAL25/0004 (As Published)
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G NEPM GIL’s for Fresh Waters as presented in Appendix N. Note that HSL’s for Vapour Intrusion have
not been used for TRH C6-C10 minus BTEX (F1) in the absence of other guidance. HSL’s to assess
vapour risk are generally higher than criteria relating to environmental or other human health criteria, with
vapour intrusion also assessed via the soil HSL criteria.
H Colour – not noticeable after 100 times dilution.
I NEPM Groundwater Health Screening Levels for vapour intrusion 2m to <4m, sand (conservative) that
may be adjusted subject to site specific geology and groundwater conditions.
J PFAS NEMP January 2018, 99% species protection ecological protection criteria to account for potential
bioaccumulation risks until these are discounted through site specific assessment for application of 95%
species protection for slightly to moderately disturbed conservation value systems.
K SW EPP aquatic ecosystem WQO’s for aquatic ecosystem – moderately disturbed. For toxicants, the
SW EPP recommended ANZECC 2000 trigger values for slightly–moderately disturbed systems have
been adopted.
M The values have been calculated using a hardness of 30 mg/L CaCO3. These should be adjusted to the
site-specific hardness.
N GW EPP values not specified - where ground waters interact with surface waters, groundwater quality
should not compromise identified EVs and WQOs for those waters. For toxicants, the GW EPP
recommended ANZECC 2000 trigger values for freshwater 99% protection have been adopted.
# Various sub-criteria. Refer to specific guidance should these contaminants be detected within
groundwater.
7.3. LANDFILL GAS
Land fill gas assessment criteria are presented in Table 17 below. The selected (lowest) SAC is
presented in bold.
Table 17: Landfill gas assessment criteria
Units ERA 60 NSW EPA 2020 NSW EPA 2016
Methane (at 5cm above ppm (v/v) 500 500 500
ground surface)
Methane (sub-surface) % (v/v) - <1A 1
Carbon Dioxide (sub-surface) % (v/v) - < background + 1.5A < background + 1.5
Explosivity (structures) LEL % (v/v) 1.25 1 -
Explosivity (soil/geology) LEL % (v/v) 5 - -
Explosivity (services such as LEL % (v/v) 1.25 - -
pipes, drains and trenches)
Notes
A – for closure purposes the monitoring period is 24 months
Criteria presented in Table 17 is based on the following information sources:
125 Lot 105 SP118458 Cooroy DSI 12062024 Rev0 Lot 105 SP118458, Cooroy, QLD, 4563
12/06/2024 61 Detailed Site Contamination Investigation
Document Set ID: 23717062
Version: 0, Version Date: 01/01/1900
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