Section 32 - Methods of implementation
Abstract
The main task of councils under the Resource Management Act 1991 (RMA) is to decide how to address environmental issues. In preparing plans and changes to them, section 32 of the RMA requires councils to consider the alternative ways to achieve the environmental outcomes being sought. Essentially, s32 tests to determine the most appropriate means, and the appropriateness of any selected methods. It assists in reasoning why changes are needed and formalises a process for working out how best to deal with environmental issues. This may be through a variety of alternatives of which rules may be just one option.
The requirements of s32 for councils apply to the preparation of regional and district plans, plan changes, variations, policy statements and reviews. Following the amendment to the RMA in 2003, the requirements of s32 also apply to the person who has made a request for a private plan change. The s32 evaluation should result in the production of a s32 report to accompany the actual amendments or new provisions to be inserted in a plan or developed as a plan.
This guidance note provides a context for s32 analysis and suggests best practice techniques for implementation. Summaries of relevant case law and current challenges in s32 implementation are also available for your assistance.
Guidance note
Section 32 of the RMA sets out a process for councils to test the appropriateness of any proposed provisions for district and regional plans. It requires councils to consider a broad range of policies, objectives and methods, and to use a rigorous analysis of the benefits and costs in deciding which provisions are the most efficient. This guidance note is primarily intended for council staff, but those persons who are requesting a private plan change and need to prepare a s32 analysis would also find this guidance note of assistance. For more information on the preparation of a private plan changes, read the guidance note on private plan changes.
In the context of s32, this term means the following:
Appropriateness - means the suitability of any particular option in achieving the purpose of the RMA. To assist in determining whether the option (whether a policy, rule or other method) is appropriate the effectiveness and efficiency of the option should be considered:
Figure: Deriving efficiency from benefits and costs

Rules in plans under the RMA is just one way that councils can achieve desired environmental goals. Sometimes methods other than RMA controls will also work. These may include methods such as voluntary agreements, use of by laws, and covenants. S32 explicitly requires councils to consider those other methods as well.
Councils must:
Using s32 is a duty, not an option. Councils must apply s32 to new plans, plan changes and variations, plan reviews, and policy statements. Those preparing a private plan change also must prepare a s32 report.
The value of s32 analysis
One of the stages of the s32 process requires a rigorous assessment of environmental, social, and economic benefits and costs. This analysis must be transparent and well documented, with all assumptions and decisions justified. This helps ensure that:
Ideally, good practice in implementing section 32 results in less opposition to proposed provisions, and fewer opposing submissions and appeals to the Environment Court. For private plan changes, it may also improve the chances of the council adopting or approving a private plan change request.
The process of documenting s32 considerations can also help satisfy obligations under the Local Government Act 2002 (LGA). Acknowledging in a s32 that the council has turned its mind to the requirements at LGA s76 reduces scope for potential challenge under that Act. This scope for challenge arises from s23 of RMA which does not remove the obligations for compliance with other legislation such as the LGA.
Meeting the requirements of s32
The application of s32 applies throughout plan preparation, from issue identification to decision release.
Council staff need to ensure that s32 requirements are met through the different stages of the process:
The importance of consultation
Although not specifically required by section 32, good consultation is essential when identifying and assessing issues, objectives, policies, and methods, and after preparing the draft plan or provision. Consultation enables councils to gather information from and understand the needs of resource users. Consultation can also assist in the assessment process, testing a council's section 32 analysis against community views and aspirations. Ultimately, consultation should help establish a mandate for the final plan provisions. For more information on consultation, refer to the consultation process guidance note.
How to apply S32
Like all good policy analysis, s32 follows an iterative process that requires a regular review of earlier steps and conclusions when necessary. It also follows a sequential process, in the sense that it begins with issue identification and ends with the final decision. The 2005 RMA amendments to section 75 reduced the required contents of a district plan to objectives, policies, and rules. Although objectives are considered separately from policies or rules as part of best practice, this does not eliminate the need to view the process sequentially and review objectives following an evaluation of policies or rules.
Throughout the process, the following questions are equally relevant to each objective, policy, rules, or (if necessary) other methods:
Is there sufficient information on the subject matter? Is the information certain?
Is it appropriate? How will it achieve environmental objectives? Do the net benefits outweigh the net costs? Is one method better than others? Does it have community support? Is it effective? Will it actually do what it is intended and achieve the environmental outcome desired? Does it meet the purpose of the Act?
The section 32 evaluation process
1) Identify the resource management issue
An issue is a matter or subject that needs to be resolved. One of the key factors that a council must consider is identifying what the issue is. In considering a resource management issue the following questions should be considered:
2) Identify the objective
An objective states the outcome that would result from the resolution of the issue (such outcome may be long-term, and beyond the ten year life of the plan).
3) Assess whether the objective is the most appropriate
An objective is a statement of a desired outcome and should be evaluated prior to the identification of policies, rules, or other methods. If later analysis shows that the costs of pursuing the objective are disproportionately large in relation to benefits, the appropriateness of the objective should be reviewed, and possibly be revised or discarded as part of the sequential process of the s32 analysis.
4) Identify and evaluate policies
Policies relate directly to objectives. They are the broad action steps that address aspects of an objective. One objective can have several associated policies.
5) Identify and evaluate methods
S32 requires councils to examine, having regard to their efficiency and effectiveness, the methods (that may be within or outside the RMA) to achieve the stated objective.
Regulatory and non-regulatory methods to achieve each objective include: research, monitoring, education, information and training, council services, incentives, voluntary agreements, land purchase, levying charges, and rules.
- Be open-minded about the range of methods. While not explicitly required, consider all the alternatives to ensure that what ever the method is chosen, it is the most appropriate. The 2005 Amendment Act provides for the incorporation of documents by reference in plans and proposed plans (part 3 to Schedule 1 of the Act). Written material that is referred to in the plan or proposed plan has legal effect as part of that plan or proposed plan, and can only be removed or modified via a plan variation.
6) Assess the effectiveness of the selected method(s)
Following the amendment to the RMA in 2003, explicit consideration of alternative means is no longer required. In practice, to ensure that the most effective method is selected a degree of comparison of methods will be required. Focus on the selected method, but the evaluation must take into account the relative effectiveness of other methods.
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- The level of risk to the environment. A method with uncertain effectiveness may be worth keeping if the level of risk to the environment is high and vice versa (i.e., if the risk to the environment is low is the method worth pursuing?). Do note, however, that specific reasons must be given for imposing a rule that has a greater prohibition or restriction on an activity than a national environmental standard that prohibits or restricts the same activity.
7) Analyse the benefits and costs of the selected method(s)
Subsequent to the 2005 Amendment Act, a rule is the only method that is required in a district plan. Other methods may be used, but it is no longer mandatory to require them. The analysis of environmental, social, and economic benefits and costs of the proposed rule must be thorough and well documented. If other methods are employed, the associated benefits and costs should also be well analysed. The results will help determine the appropriateness of the selected rule/other method. Analyse different specific approaches available within each of the selected rule/other method, rather than the wider overall approach of each rule/other method. For example, zoning might be one of the type of rules first considered to address the effects of urban growth. If the assessment shows that the zoning rule is an appropriate and effective method, the cost/benefit analysis should focus on different zoning rule approaches.
Methods can be analysed in a package, if it is likely that a group of methods will be used to achieve one objective.
For each method or group of methods:
How do we calculate and compare costs and benefits?
Environmental benefits and costs are often hard to quantify. They describe the way a method will affect things like life-supporting capacity, amenity values, landscape and heritage, and health and safety.
An example of an environmental benefit is: an increase in the amount of habitat saved for wading birds where there are threats to their survival. An example of an environmental cost is: the loss of nutrients available to indigenous fauna as a result of further marine farms.
Social and economic costs have two dimensions: the total cost, and how much of the cost will be borne by each affected party. Resource users, councils, and the community or nation can all bear direct and indirect costs.
Social and economic costs can be difficult to separate, as one can have a direct bearing on the other. For example, one group in the community bearing most of the economic costs of a method could result in increased social costs and potential conflict.
An example of a social cost is the reduced recreational space in the coastal marine area from the development of marine farms.
An example of an economic cost is the financial loss to a marine farmer who may not be able to develop a new marine farm in a productive location due to rules that impose stringent standards.
Social and economic benefits in some cases can be directly related to beneficial environmental outcomes. For example, a method that protects significant landscapes and heritage might have benefits for tourism operators, and a method to improve land-use sustainability might result in increased farm productivity. Both these benefits might create additional flow-on economic benefits to the wider community.
An example of a social benefit is a rural community retaining its school and store as a result of increased population after more subdivision lots are permitted.
An example of an economic benefit is the financial gain to a farmer who is given the right to extract water for irrigation.
8) Establish the efficiency of each selected method(s)
The most efficient method will achieve the environmental outcome at the least overall cost.
Related methods can be assessed in a group, when whole plans or chapters of plans are being developed or reviewed.
For each method or group of methods:
Net environmental benefits minus net social and economic costs equals efficiency.
This often involves comparing environmental benefits that are difficult to quantify with monetary costs. It can be useful to check that the value of the benefits is reasonable. Giving the benefits the same monetary value as the monetary costs could do this. You can then make an assessment as to whether the cost of the benefits is in fact relative to or too high or low in comparison to the costs. The need to do this will vary according to the importance of the benefits to the community, and the method's importance in achieving the purpose of the RMA.
As a general rule, high economic and social costs will require in-depth analysis of the method's efficiency. The community will expect a clear explanation of the method's environmental benefits. The depth of analysis required will also be influenced by the issue's importance, complexity, and degree of 'newness.'
- Use the checklist for issues, objectives, policies and methods and the checklist of methods for achieving the purpose of the RMA as tools for assessment and analysis.
9) Identify the risks of acting or not acting
An evaluation of the risk of acting or not acting if there is uncertain or insufficient information about the subject matter of the policies, rules, or other methods needs to be clearly stated.
As with the approach for analysing benefits and costs, concentrate on the information relating to the selected methods, rather than the wider overall approach of each method. In some cases, there is no proof of cause and effect (particularly where there is significant risk to life-supporting capacity). This does not mean that the method should not be used, but it is necessary to document the risk of acting versus not acting in such situations. Ideally, the research and monitoring should indicate a preference on whether to act or not to act.
While every locality will require a different environmental response, other councils may have implemented similar methods and have built up a body of information that could assist in this evaluation. Monitoring data and feedback from operational staff will be a critical part of the evaluation. Document all references and source material.
For each method or group of methods:
For more information on monitoring, go to the monitoring and reporting one-stop-shop.
10) Choose the appropriate method
Choosing the most appropriate methods(s) to achieve the objective requires an overall assessment of the methods efficiency and effectiveness.
Choosing the appropriate method will be straightforward if:
In less straightforward cases, the right balance between effectiveness and efficiency will depend on:
Effectiveness will have more weight than efficiency if the level of risk to the environment, due to failure, is high, if the method is uncertain, or if there is a lack of information. Efficiency will have more weight than effectiveness if the level of risk is low.
11) Review the objectives and policies
After the analysis of the methods benefits and costs:
Managing the s32 process
The s32 process must be managed so that it is coordinated with each stage of plan preparation. It is useful to think of a s32 analysis as a project that runs parallel and integral to plan preparation.
Appoint a s32 champion
A s32 champion is a senior council staff member who leads and monitors the s32 process. They should be rigorous in their thinking and could be from any discipline. They should ensure that:
Create a 'project brief'
A good project brief for the s32 process will:
Applying s32 at notification
Before deciding to notify proposed provisions, councils must be satisfied that the requirements of s32 have been met.
The RMA also requires that a s32 record is publicly available at the time of notification.
Section 32 report
A comprehensive s32 record documents the process of s32 analysis from issue identification to notification. It provides a chronological record, states who was involved, summarises the evaluation and gives reasons for that evaluation. A council must formally adopt the s32 report before the report to which it relates is publicly notified.
A clear and thorough s32 record can encourage more focused submissions, and result in fewer challenges to the council decision. Where the report is provided in support of private plan change, it might be effective in persuading the council to adopt or approve the private plan change. It provides a good record for the council which must undertake its own further s32 evaluation and assists later monitoring for the appropriateness. Ultimately, the report must answer the question: 'Why is this provision in the plan?'
The level of detail in a s32 report will depend on the level of analysis required through the process, and the level of community interest in the issue.
Supplementary s32 report
The proposed plan provisions may change after a council hearing. This will require a supplementary s32 record or report that states:
Applying s32 after submissions are received
To meet the requirements of s32, the officer's report on submissions must state whether the submissions:
The officer's report must also:
The council's written decisions on submissions must state the issues discussed, and cover the evaluation of alternatives.
Applying s32 at a hearing
The Council or Environment Court must satisfy itself that the most appropriate methods are being used, after having heard the evidence at the hearing. It is common practice for Councils to produce s32 material in relation to appeals on plans to the Court.
Challenge to s32 process
A submitter can only challenge the s32 process specifically under s32A(1) by submission.
Monitoring
The s32 analysis should provide information that will be useful for later monitoring - indeed s32 should assist in identifying requirements of the plan: what matters need to be monitored? In turn, the information and records gathered during monitoring should inform any future s32 analysis.
Roles and responsibilities
The persons responsible for making decisions on the plan provisions are responsible for ensuring that council duties under s32 are properly discharged. They must be satisfied that s32 requirements have been satisfied when they decide to notify, and when they decide on plan provisions. They are also responsible for ensuring that a s32 record is publicly available when provisions are notified.
Council staff are responsible for managing the s32 process, drafting provisions after consultation and analysis, providing information to decision makers, helping them understand s32, and giving quality policy advice.
Best practice examples
Following the amendment to the Act in August 2003, there are different requirements to s32. The following examples that were prepared pre August 2003 still illustrate best practice in particular aspects of plan preparation.
The following examples illustrate best practice in particular aspects of plan preparation, as described in the guidance note.
Section 32 - Proposed Christchurch city plan - officer [Reveal/Hide]
The example provided here relates to assessing the effectiveness of alternative approaches in dealing with the environmental effects of the issue.
Methods of implementing Section 32 - Assessment of effectiveness of alternatives
The Christchurch City Council is some considerable way through processing its Proposed City Plan. Throughout the process of hearing and considering submissions officers were required to prepare reports on submissions and recommend overall the appropriateness of any proposed provisions.
One issue that required specific provisions within the Plan was the conservation and restoration of heritage items. Heritage conservation was recognised within the Proposed Plan as being of significant importance to the City's overall amenity and character values. Because of this, it was necessary to give careful consideration to the effectiveness of alternative approaches to deal with the effects associated with the issue.
Effectiveness of alternative methods
In deciding on whether there was a need to regulate heritage protection in the City, the Council, in its officer's report for the hearing, considered a variety of methods and the benefits and costs associated with each of the relevant methods. In assessing their effectiveness the following steps were taken:
In taking this approach it was considered that a combination of the alternative methods considered would best deal with heritage protection within the city.
Contact: Bob Nixon at planitassociates@xtra.co.nz
Section 32 - Proposed variation 13 to the Manukau District Plan - Report 5: Management and provision of public open space 6 [Reveal/Hide]
The focus of this example is how to convey the necessity for new provisions in order to meet the purpose of the Resource Management Act 1991 to the public.
Methods of implementing Section 32 - Determining necessity for a provision
The Manukau City Council has compiled a Variation to the Proposed Manukau District Plan (Variation 13) to enable the urbanisation of land in Flat Bush. Flat Bush is a 1730ha area of land adjacent to the urban limits of Auckland.
Presently the land is zoned for rural and future urban use under the Transitional and Proposed Plans. However, the Council identified that the area is suitable for urban and semi-urban development in line with the Auckland Regional Growth Strategy.
The section 32 report gives consideration to the necessity of rezoning this land. The report has assessed various components of the proposed rezoning and considered the necessity for the provisions in relation to each zone and the activities to be provided in them. This example shows how the Council chose to convey the necessity to regulate the provision for an "environmental corridor - public space" zone in order to meet the purpose of the RMA.
Conveying the necessity for the provision
It is important that any section 32 finding is conveyed in a way that is easily interpreted by the receiving public. Some people will be used to reading such documents while others will be less familiar, consequently requiring a more user-friendly approach. To address this, the Manukau City Council took the following approach to explain the necessity for the imposition of environmental corridors:
The process and analysis here is simple to understand and sets out clearly what needs to be achieved by the variation at the outset. By dealing with each proposed zone individually, the overall report also provides a reasonable level of detail for a large piece of land to be rezoned for a variety of uses.
Contact: Ree Anderson at RAnderso@manukau.govt.nz or
Bruce Harland at BHarland@manukau.govt.nz
Section 32 - Section 32 Report: Air Quality Chapter of the Proposed Canterbury Natural Resources Regional Plan, 2002 [Reveal/Hide]
This example deals with both determining the issue and best practice in cost and benefit analysis.
Methods of implementing Section 32 - Determining the issue and cost/benefit analysis
Environment Canterbury has recently notified Chapters (1) - (3) of its Proposed Natural Resources Regional Plan. Chapter 3 is on Air Quality. Issue 2 of the Air Quality Chapter is concerned with winter ambient air quality, which is a significant issue for the community of Christchurch. Because of this the Council has taken particular care in identifying the issue and provided detailed cost/benefit analysis.
Determining the issue
The debate has long focused on the contribution of domestic fires and older wood burners to the air pollution of Christchurch and whether they should be banned or strictly controlled. However, the level of control has attracted much scrutiny because of the costs to the community of using alternative heating (i.e., electricity or gas or pellet burners) or having to upgrade wood burners. For this reason Environment Canterbury had to carefully identify the health issues, not only from the discharge of smoke from domestic fires, but also pollution from other sectors. This included taking the following steps:
This level of detailed issue analysis was considered necessary given the potential economic and social costs to the city. It also enables submitters to better scrutinise the assumptions behind the objective and policy alternatives.
Cost/benefit analysis
The economic costs and benefits to the community could be quantified for some of the alternative methods. For example, it states that there is a net economic benefit, in the long term, in banning open fires because of their poor heat output for the amount of fuel used. On the other hand, it states that there is an overall net economic cost to the community in upgrading old wood burners and banning new wood burners in new houses. (An incentive program funded by the ratepayer has been established to help offset the costs to households needing assistance).
The environmental costs and benefits are qualitative. This is given the difficulty in quantifying health and amenity benefits costs generally.
The analysis then combines the qualitative and quantitative parts of the cost benefit analysis to give an overall qualitative efficiency rating (low, moderate, high). The cost and benefits are easily identified in a table with the more feasible methods being highlighted.
Environment Canterbury is continuing to refine its section 32 reports, including the introduction of a clearer link between each objective or policy and its associated method.
Contact: Linda Kirk at linda.kirk@ecan.govt.nz
Section 32 - Variation 3 to the Marlborough Sounds Resource Management Plan - Shipping activity in the Marlborough Sounds, 2002 [Reveal/Hide]
This example focuses on issue determination and the importance of background research and consultation.
Methods of implementing Section 32 - Research and consultation
The Marlborough District Council has undertaken a Variation to the Proposed Marlborough Sounds Resource Management Plan (Variation 3) to deal with the effects of shipping activity within the Marlborough Sounds. The variation was done to address the new environmental effects attributed to fast ferry use in the Sounds.
This variation provides a detailed analysis of a complex issue and provides an example of the value of consultation and research investigation.
Research
As part of determining the issue and the level of its significance, the Council undertook a number of initiatives and actions to determine if the issue needed to be addressed under the RMA and to assist in developing a response to the community concerns. The initiatives included:
From this work it was apparent that there were adverse effects on shipping activity in the Sounds and highlighted what they were. This led to the careful identification that there was in fact an environmental effect that was of significance to address under the RMA.
Consultation
Because of the wide-ranging concern in relation to fast ferries the Council chose to consult with the public and specific interest groups about their concerns at an early stage. The consultation also assisted in determining the full extent of the issue and options for resolving it. The process included the following:
While consultation is not a requirement under section 32, Councils can decide to undertake consultation. Often it helps when considering contentious issues. It can often help ensure that a wide range of alternative methods for resolving the issue are considered.
This section 32 analysis can be downloaded from http://www.marlborough.govt.nz/rma/sounds_changes.cfm
Contact: Linda Craighead, Marlborough District Council at lcr@marlborough.govt.nz
Section 32 Report on the proposed Gore District Plan - Officer [Reveal/Hide]
This example illustrates one way of determining the efficiency of methods in dealing with a variety of district-wide issues.
Methods of implementing Section 32 - Efficiency
The Gore District Council compiled a section 32 analysis for its entire Proposed Plan which was notified in 2001. It deals with a multitude of issues within a district that has a number of small settlements, a predominant rural character and a significant town.
This report summarises the findings extracted from a consultation process and through the use of past records, which have been referenced within the document. To simplify the document and make the findings easier to understand, both the use of flow diagrams and tables have been used to illustrate how efficient the proposed methods will be in achieving the objectives and desired environmental outcomes.
Efficiency
In determining the efficiency for each feasible method the Council followed these steps:
Contact: Francis Cowan at fcowan@goredc.govt.nz
RMA provisions
The following are other sections of the Resource Management Act 1991 that are relevant to Section 32:
Local Government Act 2002
Practice in relation to the linkage between the RMA and LGA is evolving and case law is not available yet. To avoid a risk of challenge via judicial review under LGA it may be prudent to briefly canvass in the RMA s32 that the Council has turned its mind to the LGA requirements. This guidance arises from:
Case law
The following cases contain discussion of Section 32 related matters (note all these cases except the last deal with s32 before the 2003 amendment:
Related guidance notes
The following guidance notes are related:
Relevant publications
Think Piece Two: Improving implementation of the Resource Management Act at the local level can produce better outcomes (PDF 1 MB)
Published by Federated Farmers - August 2003
The report focuses on transaction costs and offers practical solutions to improve the implementation of the RMA at local and regional levels.
Current challenges in practice
The following are current challenges which are being experienced by practitioners undertaking section 32 analysis:
Recording and reporting section 32 analysis
Keeping clear and concise records of section 32 analysis is a critical component of the implementation process. It helps to make the development of any plan transparent. A s32 report that summarises the evaluation and gives reasons for that evaluation must be available for public inspection at the time of public notification. Deciding on how to present and store information on section 32 analysis can be a difficult task, especially when dealing with large quantities of information and significant and/or particularly contentious issues. The financial costs associated with this can also be significant and Councils can find it challenging to finance good section 32 analysis and record keeping.
It is important that the section 32 records and/or reports are constantly readdressed throughout the planning process. This is to ensure that any changes or decisions are appropriately recorded and reasoned. This can be difficult to achieve when there are tight time constraints and limited finances available.
Recording and reporting section 32 analysis is also critical where a considerable amount of information held within a Council may be institutional knowledge which is not already documented. Where changes in staff occur this important information may be lost where there has been no record of the knowledge held.
Choosing suitable methods
It can be difficult to decide what methods, particularly non-regulatory ones, are suitable to address an issue when they have not been previously tested. Section 32 does not prescribe that only regulatory methods should be applied to environmental issues. However, Councils may find to use such methods, as their performance can be better measured through previous implementation. Non-regulatory methods tend to be monitored to a lesser extent even though they may be a more plausible option for dealing with some issues.
What is the right amount and type of consultation?
Consultation assists the production of a sound and transparent section 32 assessment. It can be difficult to determine what type and how extensive the consultation should be. The extent and type of consultation should be relative to the nature and scale of the issue and the level of public interest. Wide ranging consultation does not necessarily equate to any less potential for any new provisions to be challenged.
Using monitoring in section 32 analysis
Monitoring existing activities that are subject to resource consents and state of the environment monitoring can be useful in determining environmental issues but also in assessing the effectiveness of existing plan provisions. Sound monitoring can be a key mechanism in determining the need for future plan revisions. Inadequate monitoring and recording results can be detrimental to the entire process and could lead to the development of inappropriate methods for dealing with an issue.
Risk of acting v not acting
This is a new provision that was introduced in the August 2003 amendment.
The risk of implementing a method, even if the information is uncertain or insufficient, may outweigh the risk of not implementing a method. If the decision is appealed, the parties may undertake more extensive research. Subsequent research may change the position of whether to implement a particular method. Changes at this late stage can create unnecessary delays and costs to all parties. It is preferable that such information forms part of the initial evaluation.
The length of time before a plan change may become operative can be years. In the meantime, the risk of not acting on the basis of the information to hand is that the environment could be degraded. The risk of acting is that a method is chosen that is not efficient or effective and in the long term, may not prevent the environment from being degraded. The decision on whether to act on the basis of the information known at the time will be finely balanced.
Evaluation of private plan change assessments
As with resource consent auditing, the challenge in reviewing a private plan s32 report is not to duplicate the assessment, but to identify errors or omissions in the analysis. It is important that the Council carefully consider the s32 report in the wider context of the existing plan or other mechanisms that may sit outside the plan to achieve the environmental issue or objective.
Linkages of the Local Government Act 2002 and the RMA
Practice is evolving in terms of linking the LGA 2002 obligations with those of RMA.
Section 23 of RMA does not absolve a council of its obligations under s76 of the LGA. These decision-making obligations are similar in nature to what is needed for a s32 report.
Prudence suggests that cross-referencing to the LGA considerations as a part of the s32 will reduce the risk of challenge to this aspect of a council's decision-making.
Acknowledgements and editorial comments
This guidance note has been prepared by Sarah Dawson, Carey Barnett and Andrew Purves from Boffa Miskell. It is based on guidance published in July 2000 by the Ministry for the Environment.
The note was subsequently updated by Tania Richmond from Richmond Planning Limited in 2004, and by Incite in 2005 to reflect the RMAA05.
