Toxicant Guideline not met, or likely not to be met?
First check how often the trigger value is not met, - it may be due to natural variation (see Vol1 7.4-3)
Comparing Test Data with Background data from a Reference site
Some surface waters will contain background concentrations ( i.e. natural not caused by human disturbance ) of toxicants
that may naturally exceed the default guideline trigger values tabulated. The minimum data set for using reference
monitoring to derive a site specific trigger is two years, with a minimum of monthly sampling. New trigger values should
be derived from the background data as the 80th percentile. A trigger for further investigation is deemed to have occurred
when the median concentration of n independent samples taken at a test site exceeds the 80th percentile of the same indicator
at a suitably chosen reference site.
Comparing test data with default guideline trigger values
<<<< Level below guideline value
Level exceeds guideline value >>>>
Test data exceed modified trigger value >>>>
<<<< Local study shows modified guideline met
Action is triggered when the 95th percentile of the distribution of the test data, complied as a 'running' estimate of the
last n observations, exceeds the default trigger value in the lists (or in other terms, no action is triggered
if 95% of the values fall below the guideline value).
Therefore a trigger for further investigation is deemed to have occurred when the 95th percentile of n independent samples
taken at a test site exceeds the default guideline trigger value in the lists.
Next conduct the risk assessment using the Decision Tree Framework for Toxicants (Vol 1 page 3.4-14)
|
|
|
|
__________________________________
/
/
\
\
|
____________________________________
|
|
Define primary management aims ( see Vol 1 fig 3.1.1)
Determine appropriate guideline trigger values for selected indicators( see Vol 1. fig 3.1.1)
Monitor to test total contaminant concentration
against guideline 'trigger' values for ecosystem
type ( marine or freshwater )
*Low Risk of Damage or Impairment of Use
#Potential Risk of Damage or Impairment of Use
Examine whether site specific factors may be ameliorating the toxic effects
at the trigger value concentration. Determine a site specific guideline value
that accounts for these local conditions.
Consider the following issues:
1. High natural background levels - monitor to set new trigger level
2. Analytical limits - set guideline at limit of detection
3. Locally important species - set guideline values that protect these species
4. Chemical water quality modifiers - modify guideline value for to account for these
5. Mixture Interaction - set guideline values that consider these mixture effects
#Potential Risk of Damage or Impairment of Use
Perform biological effects assessment using
local species (e.g. Direct Toxicity Assessment
or Laboratory Toxicity Tests)
|
|
/
\
Initiate Remedial Actions or Accept Level of Change
*Low Risk of Damage or Impairment of Use
Toxic >>>>
<<<< Non Toxic
__________________________________
#High Risk of Damage or Impairment of Use
*Low Risk of Damage or Impairment of Use
WQG - Australian and New Zealand Water Quality Guidelines (ANZECC & ARMCANZ 2000)
* Possible refinement of trigger value after regular monitoring.
# Further investigations are not mandatory; users may opt to proceed to remedial action.