Published Project View

State-wide Purpose Permit Activities

PROJECT 1

Project name: Baldivis Sewage Pump Station to East Rockingham Wastewater Treatment Plant Pressure Main
Project location: The project is located between the Baldivis Sewage Pump Station and the proposed East Rockingham Wastewater Treatment Plant. The alignment predominantly follows Eighty Rd, Mundijong Rd and Mandurah Rd.
Approved project area: 6.8ha
Project bioregion: Swan Coastal Plain
Assessment criteria: Clearing Principle H - the clearing of the vegetation is likely to have an impact on the environmental values of any adjacent or nearby conservation area, Clearing Principle F - it is growing in, or in association with, an environment associated with a watercourse or wetland, Clearing Principle B - it comprises the whole or a part of, or is necessary for the maintenance of, a significant habitat for fauna indigenous to Western Australia, Clearing Principle A - it comprises a high level of biological diversity
Residual impact: Loss of up to 6.8 hectares of native vegetation in completely degraded to good (Keighery 1994) condition that includes:
- 4.73 hectares of foraging habitat suitable for Carnaby's cockatoo, forest red-tailed black cockatoo and Baudin's cockatoo;
- potential breeding habitat and roosting trees for Carnaby's cockatoo, forest red-tailed black cockatoo and Baudin's cockatoo;
- 0.1 hectares of vegetation growing in association with a conservation category wetland (Kerosene Lane Swamp); and
- 1.07 hectares of Bush Forever site 356.
Related offset(s): 1

PROJECT 2

Project name: Baldivis DN1400 Outlet Tamworth
Project location: The project involves the installation of a pressure main between the Tamworth reservoir and the intersection of Baldivis Road and Fifty Road
Approved project area: 1.64ha
Project bioregion: Swan Coastal Plain
Assessment criteria: Clearing Principle H - the clearing of the vegetation is likely to have an impact on the environmental values of any adjacent or nearby conservation area, Clearing Principle B - it comprises the whole or a part of, or is necessary for the maintenance of, a significant habitat for fauna indigenous to Western Australia, Clearing Principle A - it comprises a high level of biological diversity
Residual impact: Loss of up to 1.64 hectares of native vegetation in completely degraded to very good (Keighery 1994) condition that includes:
- 1.64 hectares of foraging habitat suitable for Carnaby's cockatoo, forest red-tailed black cockatoo and Baudin's cockatoo; and
- 1.19 hectares of Bush Forever site 356.
Related offset(s): 2

CPS 185/6 (active from 10/04/2014 to 10/12/2014):

PART I - TYPE OF CLEARING AUTHORISED
4. Requirements prior to undertaking clearing
(a) Prior to clearing any native vegetation under this Permit, the permit holder must:
(ii) if an offset is required to be implemented pursuant to condition 8(c), provide the CEO with an offset proposal for the CEO’s approval.

PART III - ASSESSMENT PRINCIPLES
8. Assessment against the Clearing Principles
(c) If part or all of the clearing to be done is or is likely to be at variance with one or more of the clearing principles, then the permit holder must implement an offset in accordance with Part V of this Permit with respect to that native vegetation.

PART V – OFFSETS
14. Determination of offsets
(a) In determining the offset to be implemented with respect to a particular area of native vegetation proposed to be cleared under this Permit, the permit holder must have regard to the offset principles contained in condition 15 of this Permit.

(b) Once the permit holder has developed an offset proposal, the permit holder must provide that offset proposal to the CEO for the CEO’s approval in accordance with condition 4(a)(ii), prior to undertaking any clearing to which the offset related, and prior to implementing the offset.

15. Offset principles
For the purpose of this Part, the offset principles are as follows:
(a) direct offsets should directly counterbalance the loss of the native vegetation;
(b) contributing offsets should complement and enhance the direct offset;
(c) offsets are implemented only once all avenues to avoid, minimise, rectify or reduce environmental impacts have been exhausted;
(d) the environmental values, habitat, species, ecological community, physical area, ecosystem, landscape, and hydrology of the offset should be the same as, or better than, that of the area of native vegetation being offset;
(e) a ratio greater than 1:1 should be applied to the size of the area of native vegetation that is offset to compensate for the risk that the offset may fail;
(f) offsets must entail a robust and consistent assessment process;
(g) in determining an appropriate offset, consideration should be given to ecosystem function, rarity and type of ecological community, vegetation condition, habitat quality and area of native vegetation cleared;
(h) the offset should either result in no net loss of native vegetation, or lead to a net gain in native vegetation and improve the condition of the natural environment;
(i) offsets must satisfy all statutory requirements;
(j) offsets must be clearly defined, documented and audited;
(k) offsets must ensure a long-term (10-30 year) benefit; and
(l) an environmental specialist must be involved in the design, assessment and monitoring of offsets.

16. Duration of offsets
(a) The permit holder must ensure that an offset implemented under this Permit continues to be implemented for the term of this Permit.

(b) If for any reason an offset is not continually implemented for the term of this Permit, the permit holder must:
(i) implement the offset again within 12 months of becoming aware that the offset is not being maintained; and
(ii) if necessary, modify the offset in a manner that increases the likelihood that the offset will be implemented for the term of this Permit.