We are consulting on:
- whether to give councils flexibility to deviate from:
- nationally defined thresholds (including bottom lines) that guide where the environmental limits (targets) are set
- detailed methods for monitoring attributes
- whether national bottom lines are required at all, or if instead councils should determine where limits are set based on community input.
Nationally defined thresholds are sometimes inappropriate in a specific catchment (eg, due to naturally high levels of suspended sediment), and we are consulting on enabling councils to deviate from those thresholds in certain circumstances. Similarly, developments in science and evidence, or monitoring methods, may mean the thresholds need to be revised.
There are also trade-offs involved in providing this flexibility. That is why any additional flexibility (described in proposal (1) above) would be subject to it being used for specific purposes and having regard to appropriate matters. For example, councils could deviate from nationally defined thresholds or detailed methods for monitoring attributes because:
- the science underpinning a threshold or method for monitoring an attribute has changed
- local conditions make a threshold or method for monitoring an attribute inappropriate
- more effective or efficient methods are developed
- achieving national bottom lines has a high social, cultural or economic cost.
Councils would need to follow the default thresholds and monitoring methods prescribed for individual attributes in Appendices 2A and 2B of the NPS-FM, except for the above purposes.
Figure 217 illustrates an example of which elements of an attribute could be deviated from (shown below in orange) and which elements would still need to adhere to national default settings (shown below in green).
Figure 2: Example of how flexibility could apply to an attribute
Table 5 – Ammonia (toxicity)
|
Value (and component) |
Ecosystem health (Water quality) |
Freshwater body type |
Rivers and lakes |
Attribute unit |
mg NH4-N/L (milligrams ammoniacal-nitrogen per litre) |
Attribute band and description |
Numeric attribute state |
|
Annual median |
Annual 95th percentile |
A
99% species protection level: No observed effect on any species tested.
|
≤0.03 |
≤0.05 |
B
95% species protection level: Starts impacting occasionally on the 5% most sensitive species.
|
>0.03 and ≤0.24 |
>0.05 and ≤0.40 |
National bottom line |
0.24 |
0.40 |
C
80% species protection level: Starts impacting regularly on the 20% most sensitive species (reduced survival of most sensitive species).
|
>0.24 and ≤1.30 |
>0.40 and ≤2.20 |
D
Starts approaching acute impact level (that is, risk of death) for sensitive species.
|
>1.30 |
>2.20 |
Numeric attribute state is based on pH 8 and temperature of 20°C. Compliance with the numeric attribute states should be undertaken after pH adjustment. |
|
|
Key
National default settings |
Could be deviated from |
This would mean amending various clauses throughout Part 3, Subpart 2 of the NPS-FM to create a new process for deviating from nationally defined thresholds or detailed methods for monitoring attributes. It would also require consequential changes to be made to processes that use attributes to set targets, and to monitor and respond to degradation.
For further information, refer to the impact analysis document entitled Interim Regulatory Impact Statement: Replacing the National Policy Statement for Freshwater Management.
17 Table 5 from Appendix 2A of the NPS-FM is used here as an example to illustrate where deviation would be possible.