A waste management and minimisation plan (WMMP) is the term legally prescribed by the Waste Minimisation Act (WMA) for a territorial authority's (TA’s) waste management and minimisation planning document. Under previous legislation, the term was ‘waste management plan’. All territorial local authorities in New Zealand currently have some form of waste management plan.
TAs are enabled through legislation to use various tools to influence, promote and implement measures to reduce and minimise waste. The WMMP is intended to be the guiding document for TAs in directing their efforts towards achieving effective and efficient waste management and minimisation within their districts.
Having a WMMP will provide each district with a blueprint for achieving their waste management and minimisation aims in a structured way. The process for developing a WMMP should be inclusive, in terms of securing partnership and community support for the waste management and minimisation methods selected. This will help smooth transitions during the design, procurement and implementation of any major new services or programmes,
Councils are required by the WMA to review their existing waste management plan and develop and adopt a WMMP by 2012. While nearly all TAs have an existing waste management plan developed under Part 31 of the Local Government Act (LGA) 1974, each of these need to be thoroughly reviewed by 2012. For an overview of the anticipated timeframe for conducting the initial review, see table 4.1, page 22.
A WMMP should contain a summary of the council’s objectives, policies and targets with respect to waste management and minimisation. It should also clearly communicate how the council will deliver on these objectives through its activities.
The WMA (s 43) states that:
A WMMP must provide for the following:
The WMA does not prescribe specific waste management and minimisation targets, or the structure or content of WMMPs, thus allowing significant local flexibility in the approach taken. This also means that individual WMMPs may differ widely in terms of quality. However, there is the scope within the WMA for the Minister to set performance standards for the implementation of WMMPs. At the time of writing there have been no performance standards set, but any such standards in the future will need to be considered in the planning process because they may have a direct impact on a council’s targets, strategy and activities.
In this context it is worth reiterating a few points. This guidance aims to promote consistency in the approach to the WMMP process. It is also intended to help those involved in WMMP development by increasing understanding of the intent behind the legislation and how this might flow through into WMMPs. Although there is no single correct way to draft a WMMP, this guidance presents an approach to the planning process. The sample WMMP outline (see Appendix 1) may assist councils in plan preparation. The sample WMMP has considered the Government’s policy and legislative requirements as well as the recommendations of the Office of the Auditor General.
There is a distinction in the WMA between what needs to be provided for in a WMMP and what needs to be considered in the preparation and development of a WMMP. You may wish to obtain legal advice on how these terms apply to your WMMP.
The WMA (s 44) sets out specific requirements when preparing, amending or revoking WMMPs that are important considerations in the development of your plan:
In preparing, amending, or revoking a waste management and minimisation plan, a territorial authority must −
This clause demonstrates an emphasis on the waste hierarchy and the New Zealand Waste Strategy (NZWS), as well as on waste assessment. However, the WMA does not prescribe exactly how regard is to be given to these concepts. This guidance aims to provide you with a better understanding of the intent of these clauses and how they may be considered during the planning process. These clauses will be discussed further in the context of the planning process outlined in chapter 4.
The waste assessment, as prescribed in the WMA (s 51), plays a key role in determining the content of a WMMP, and councils are required to conduct a waste assessment before reviewing their WMMP (WMA s 50) and to have regard to it in the preparation of the document (WMA s 44). The WMA does not require that the waste assessment be specifically consulted on individually, but we recommend you review and ‘adopt’ the waste assessment before drafting the WMMP, as s 44 requires that the waste assessment be notified with the statement of proposal for the WMMP.
The purpose of the waste assessment is to provide the necessary background information on the waste and diverted materials streams that will enable a council to determine a logical set of priorities and inform its activities. The waste assessment incorporates the situation and options review steps in assessing waste information and selecting the specific methods for addressing the various waste and diverted material streams, as well as future demand for services, programmes and infrastructure.
The WMA (s 51) states:
Many of these provisions were contained in the solid waste provisions of the LGA 1974 that were repealed by the WMA. The waste assessment provisions go further by expanding the assessment to all waste and waste minimisation activities within the district − not just waste for disposal or those materials under a council’s direct control, as was previously required.
There are various ways to interpret the requirements of the waste assessment section. This guidance suggests that significant flexibility is allowed in terms of the information gathered for the assessment. This flexibility acknowledges the differences in ease of obtaining information from district to district. While, again, there is clearly no single correct method in terms of how a waste assessment should be carried out, this section is considered further in chapter 4 as it relates directly to the WMMP process.
The following diagram (figure 3.1) depicts some of the key national, regional and local circumstances, policies and plans that influence the development of a WMMP. It also shows how the WMMP fits with a community’s long term council community plan (LTCCP), in that the WMMP will be influenced by desired community outcomes (as contained in an existing LTCCP). Ultimately the WMMP will be adopted and then incorporated into the LTCCP for implementation.
Not only does the WMMP influence the content of the LTCCP, but any changes to waste activity resulting from a significant change in the LTCCP may result in a requirement to amend the council’s WMMP, and vice versa. Figure 3.1 is intended to give a general overview of these relationships and influences, but further details of the planning process itself and the interface between the WMA (and the LGA) and LTCCP processes are given in chapter 4.

This diagram shows influences on the development of a WMMP. Influences from a national, regional and local level should feed into the WMMP.
At a national level consideration should be given to the New Zealand Waste Strategy and the Waste Minimisation Act, at the local level a waste assessment and relevant LTCCP outcomes should be considered, at a regional level regional plans should be considered if they exist.
The WMMP then feeds in to schedule 10 of the LGA which in turn feeds into the LTCCP. The LTCCP then delivers services to the community.