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Natural Hazard Management - Research Report

8 Planning and legal framework (including case law)

This section provides an overview of relevant existing guidance and information on natural hazard management policy and planning, and decision-making processes. This includes:

8.1 The legal framework for natural hazard management

In New Zealand, the Resource Management Act 1991 (RMA) and the Building Act 2004 (BA) provide the primary legal framework for natural hazard management policy, planning and decision making. The Civil Defence Emergency Management Act 2002 (CDEMA) provides the primary legal framework for emergency management policy, planning and decision making.

A number of other acts also impact upon the management of natural hazards in New Zealand, including:

The first part of this section provides an overview of the natural hazard management legislative framework, highlighting for each Act the relevant authorities, their responsibilities and mechanisms used. The following sections provide additional details for each Act and discuss (where applicable) natural hazard management issues by reference to relevant case law.

8.1.1 Overview of the legal framework

The following tables provide an overview of each Act of relevance to natural hazard management, highlighting the key responsibilities and mechanisms used by each authority. Further detail is provided in subsequent sections.

Table 14. Resource Management Act 1991 (RMA) overview

Authority Ministry for the Environment / Department of Conservation Regional Councils Territorial Authorities

Responsibilities

Provide national guidance / standards / policy

Control use of land for the avoidance of natural hazards

Monitoring and keeping records of natural hazards*

Control effects of the use of land for the avoidance of natural hazards

Monitoring and keeping records of natural hazards*

Mechanisms

New Zealand Coastal Policy Statement

Other National Policy Statements

National Environmental Standards

Regional Policy Statements

Regional Coastal Plans

Other Regional Plans

Processing resource consent applications

District Plans

Processing resource consent applications

Exceptions for emergencies

Table 15. Building Act 2004 (BA) overview

Authority Central Government Territorial Authorities

Responsibilities

Establish a licensing regime

Set performance standards for buildings

Restrict construction of buildings on land subject to natural hazards

Identify and inform where land is subject to natural hazards

Control earthquake prone buildings

Mechanisms

Building Regulations (Building Code)

PIMs

Building consents and conditions on consents

Earthquake Prone Buildings policies and controls

Table 16. Civil Defence Emergency Management Act 2002 (CDEMA) overview

Authority Central Government Local Authorities

Responsibilities

Identification of hazards of national significance

Sustainable management of hazards

Planning and preparation for emergencies and for response and recovery*

Form a CDEM Group

Identify, and manage hazards and risks

Consult and communicate about risks

Implement risk reduction

Respond to emergencies

Carry out recovery activities

Planning and preparation for emergencies and for response and recovery*

Mechanisms

National Emergency Management Strategy

National Emergency Management Plans

(CDEM Group input)

CDEM Group Plans

Maintain organisational structure

Recruit and train volunteers

Conduct training exercises

Provide warning systems

Provide communications, equipment, accommodation

Participate in MCDEM Strategy/Plans

 

Table 17. Local Government Act 1974 (LGA74) overview

Authority Territorial authorities

Responsibilities

Manage sewerage and stormwater drainage

Manage land drainage and rivers clearance

Mechanisms

Powers to order to cut down trees / roots

Powers to make drainage channels

Powers to undertake land drainage works

Table 18. Local Government Act 2002 (LGA02) overview

Authority Local authorities

Responsibilities

Setting out the strategic direction and activities (including natural hazard management) of the local authority

Flood protection and flood control works

Mechanisms

LTCCP

Bylaws

Table 19. Local Government Official Information and Meetings Act 1987 (LGOIMA) overview

Authority Local authorities

Responsibilities

Provide for public availability of information held by local authorities (including the identification of natural hazards)

Mechanisms

LIMs

Table 20. Environment Act 1986 (EA) overview

Authority Ministry for the Environment Parliamentary Commissioner for the Environment

Responsibilities

Provide to the Government and other public authorities advice on the identification and likelihood of natural hazards and reduction of the effects of natural hazards

Ensure that in carrying out functions under the Act regard must be had to matters that would be likely to result in natural hazards*

Assess New Zealand's system of environmental administration

Provide advice to environmental managers

Ensure that in carrying out functions under the Act regard must be had to matters that would be likely to result in natural hazards*

Mechanisms

Advice

Committees

Annual report

Can be heard at proceedings

Table 21. Conservation Act 1987 (CA) overview

Authority Department of Conservation

Responsibilities

Manage natural hazards in conservation areas

Close conservation areas for public safety or emergency

Mechanisms

Policy

Conservation or hazard and risk management plans / strategies

Close conservation areas

Table 22. Soil Conservation and Rivers Control Act 1941 (SCRCA)overview

Authority Regional Councils

Responsibilities

Manage soil conservation reserves

Maintain and improve defences against water

Mechanisms

Make grants

Construct and maintain flood protection works

Undertake afforestation and destruction of animals

Undertake surveys and investigation

Table 23. Land Drainage Act 1908 (LDA) overview

Authority Regional Councils

Responsibilities

Ensure watercourses and drains do not become a nuisance

Cleaning, repairing and maintaining watercourse and drains

Mechanisms

Powers to order removal of obstructions

Powers to construct and maintain drains and water courses

Table 24. Forest and Rural Fires Act 1977 (FRFA) overview

Authority Territorial authorities Minister of Conservation

Responsibilities

Act as fire authority for territorial area over which have territorial jurisdiction

Safeguard life and property related to fire in forests and rural areas

Act as fire authority for state areas

Safeguard life and property related to fire in forests and rural areas

Mechanisms

Bylaws

Powers to carry out fire control measures

Bylaws

Powers to carry out fire control measures

8.1.2 Planning and decision making under the Resource Management Act 1991 (RMA)

Resource Management Act 1991 (RMA) summary of provisions

Legislation

Section/part

Relevance to natural hazard management

Resource Management Act 1991 (RMA)

s2

Defines 'natural hazard '.

Part II

Part II explains the purpose of the Act and identifies matters of national importance and other matters (includes climate change).

s30

Regional councils have responsibility to control of the use of land for the avoidance or mitigation of natural hazards.

s31

Territorial authorities have responsibility to control the effects of the use of land for the avoidance or mitigation of natural hazards.

s35

General duty for local authorities to gather information and undertake monitoring - applies to natural hazards.

s45

Preparation of National Policy Statements

s58

Contents of NZCPS - National priorities for the preservation of the natural character of the coastal environment

s59 - s62

Preparation of Regional Policy Statements, including reference to natural hazards.

s63 - s68

Preparation of Regional Plans in accordance with functions (includes avoidance or mitigation of natural hazards).

s72 - 76

Preparation of District Plans in accordance with functions (includes avoidance or mitigation of natural hazards).

s106

Subdivision consent can be refused, or granted subject to conditions, if land is likely to be subject to natural hazards.

s108

Allows resource consents to be granted subject to conditions, including conditions relating to natural hazards.

s220

Allows conditions to be placed on subdivision consents, including specific requirements.

s229

Purposes of esplanade reserves and esplanade strips to contribute to the protection of conservation values by, mitigating natural hazards

s418

Certain existing permitted uses may continue

s329-330B

Provides for the issuing of water shortage directions to apportion, restrict or suspend the talking, use, damming or diversion of water at any time there is a serious temporary shortage of water; and resource consent exceptions for immediate preventative or remedial works as a result of natural hazards, and for works undertaken in accordance with the Civil Defence Emergency Management Act 2002.

4th Schedule

Matters that should be considered when preparing an assessment of effects on the environment any person preparing an assessment of the effects on the environment should consider any risk to the neighbourhood, the wider community, or the environment through natural hazards.

Part II RMA

Part II of the RMA explains the purpose of the Act and identifies matters of national importance, other matters and Treaty of Waitangi matters.

The primary purpose of the RMA is the promotion of the 'sustainable management of natural and physical resources ', which includes enabling people and communities to provide for their social, economic and cultural wellbeing, and for their health and safety (s5).  Under the Act, natural and physical resource include land, water, air, soil, minerals, and energy, all forms of plants and animals (whether native to New Zealand or introduced), and all structures.  New Zealand is susceptible to a great range of natural hazards which have the potential to adversely affect natural and physical resources, and to impact upon the ability of people and communities to provide for their wellbeing and health and safety.  Management of natural hazards is therefore necessary in order to help achieve the purpose of the Act.

Part II includes matters of national importance (section 6), other matters (section 7), and Treaty of Waitangi (section 8) matters, which must be considered when exercising functions and powers under the Act.

Of note is 'other matters ' within section 7 which includes '(i) the effects of climate change '.  Climate change is likely to have important implications for natural hazard management within New Zealand in the future. The primary effect of climate change is expected to be in changing the level of risk from weather-related natural hazards (Ministry for the Environment, Climate Change Guidance Note).

Case law relating to Part II RMA

The Courts have enforced the importance of considering the RMA 's purpose of sustainable management when making decisions on hazard management under the RMA.

For example, in the context of making a decision on a resource consent application, it is not consistent with the principles of sustainable management to locate a facility for the reception, recovery and rehabilitation of wild birds for release back into the wild, which would include a café and an education facility, in an area that is demonstrably subject to coastal hazards Lowry Bay Residents Association v Eastern Bays Little Blue Penguin Foundation Inc W45/01 EnvC, Kenderdine J.

Similarly, in the context of making decisions on the content of a district plan, Bollard J in Bay of Plenty Regional Council v Western Bay of Plenty District Council A27/02 stated that "failure to manage known actual or potential effects of natural hazards … under the Act 's regime would not, in our view, be consistent with the legislative purpose of sustainability".

The importance of considering the purpose of sustainable management when making decisions on plans was also evident in Franks v Canterbury Regional Council, HC Christchurch, CIV2003-485-1131, 10 June 2004, Panckhurst J. In this case the appellant submitted that the Environment Court had not considered the social and economic aspects of sustainability when deciding where to place a building restriction line. However, the High Court decided that the Environment Court 's decision making process had appropriately considered the sustainable management purpose of the Act.

Functions of Central Government

National Policy Statements and National Environmental Standards

 

Sections 43-58 of the RMA provide for the preparation of National Policy Statements (NPS) and National Environmental Standards (NES).

The RMA allows the Minister for the Environment (the Minister) to prepare NPS to guide local authorities on matters of national significance.  Once a NPS has been approved, local authorities must ensure that their plans give effect to it.  The New Zealand Coastal Policy Statement (NZCPS) is the only NPS required by the RMA and is currently the only NPS in place.

A NPS on natural hazards could potentially be prepared under s45 where a natural hazard is of national significance

 

Similarly, the RMA allows the Minister to prepare NES.  These regulations apply nationally and are binding on local government.  Each regional, city or district council must enforce the same standard, although councils can impose stricter standards in certain circumstances.  NES aim to ensure a consistent approach and decision making process throughout the whole country.  Currently, only a series of 14 air quality NES are operative.

NES can be made that regulate matters referred to in s9 and s11-15 (duties and restrictions under the RMA), and include restrictions on the use of land, restrictions on the use of the coastal marine area, restrictions on the subdivision of land, and restrictions relating to water - this could potentially include natural hazards.

New Zealand Coastal Policy Statement (NZCPS)

New Zealand Coastal Policy Statement (NZCPS) summary of provisions

Plan

Section

Relevance to natural hazard management

New Zealand Coastal Policy Statement (NZCPS)

s8.7

Regard to be had to the susceptibility of the coastal environment to the effects of natural hazards.

Policy 3.4.1

Identify areas in the coastal environment where natural hazards exist.

Policy 3.4.2

Recognise the possibility of a rise in sea level.

Policy 3.4.3

Recognise the ability of natural features to protect subdivision, use, or development.

Policy 3.4.4

Recognise that in relation to future subdivision, use and development, some natural features may migrate inland.

Policy 3.4.5

Locate and design new subdivision, use and development to avoid the need for hazard protection works.

Policy 3.4.6

Coastal protection works permitted only where they are the best option.

 

Policy 3.4.1 requires that local authority policy statements and plans should identify areas in the coastal environment where natural hazards exist.

Policy 3.4.2 requires that policy statements and plans should recognise the possibility of a rise in sea level, and should identify areas which would as a consequence be subject to erosion or inundation. Also, natural systems which are a natural defence to erosion and/or inundation should be identified and their integrity protected.

Policy 3.4.3 requires recognition and maintenance of the ability of natural features such as beaches, sand dunes, mangroves, wetlands and barrier islands, to protect subdivision, use, or development.

Policy 3.4.4 requires that in relation to future subdivision, use and development, policy statements and plans should recognise that some natural features may migrate inland as the result of dynamic coastal processes (including sea level rise).

Policy 3.4.5 requires that new subdivision, use and development should be located and designed so that the need for hazard protection works is avoided.

Policy 3.4.6 requires that where existing subdivision, use or development is threatened by a coastal hazard, coastal protection works should be permitted only where they are the best practicable option for the future, and that the abandonment or relocation of existing structures should be considered among the options.

Hierarchy of coastal hazard management options

The NZCPS considers the management of hazards within the coastal environment according to the potential environmental effects of the selected technique (New Zealand Climate Change Office, 2004a). This provides a broad hierarchy of management options for coastal areas (refer to Outcomes 3 and 3.3 or Policies 3.3.1 and Policy 3.3.2 of the NZCPS) which is outlined below, with 1 being the most preferable and 4 the least preferable.

Source: New Zealand Climate Change Office (2004a)

Functions of Regional Councils

Under s30 of the RMA, regional councils are responsible for (among other things) the control of the use of land for the avoidance or mitigation of natural hazards.

Regional councils are able to exercise this control through regional policy statements (s59-62) and regional plans and rules (s63-68).

Regional policy statements allow regional councils to address regionally significant natural hazards.  They may contain issues, objectives, policies and methods (excluding rules) relating to natural hazard management.  Under s62(1)(i), a regional council must state in a regional policy statement the local authority responsible for setting objectives, policies and methods for the control of the use of land to avoid or mitigate natural hazards to an identified local authority.  However, if no such responsibilities are specified, this function is retained by the regional council (s62(2)).

Regional plans, which must contain objectives, policies, and rules, must give effect to any regional policy statements and national policy statements.  Section 65(3)(c) requires a regional council to consider the desirability of preparing a regional plan where, among other things, there is any threat from natural hazards.

The objectives, policies and rules set by regional councils in regional plans establish the basis for assessing land use, water permit, discharge permit, and coastal permit resource consent applications.  They can specify particular natural hazard matters that are to be considered when making decisions on applications for particular activities, or for activities within a particular area.

Section 108 allows conditions to be placed on granted resource consents.  For controlled and restricted discretionary activities, if the regional plan reserves council control to natural hazard matters, these conditions can relate to avoiding and/or mitigating the effects of natural hazards. For discretionary and non-complying activities, conditions can be placed on granted consents regardless of the content of the plan.

Functions of Territorial Authorities

Under s31 of the RMA territorial authorities are responsible for (among other things) the control of the effects of the use of land for the avoidance or mitigation of natural hazards.

Territorial authorities are able to exercise this control through district plan objectives, policies and rules (s72-76), and through processing subdivision and land use resource consent applications and placing conditions on granted resource consents (s106, s108, s220).

District plans allow territorial authorities to create objectives, policies and rules relating to the control of the effects of the use of land for the avoidance or mitigation of natural hazards.  District plans must give effect to national and regional policy statements, and must not be inconsistent with regional plans.  As such, the directive set by the regional council in relation to natural hazard management by regional objectives, policies and rules must be carried through to district plans.

The objectives, policies and rules set by district plans establish the basis for assessing land use and subdivision resource consent applications.  They can specify particular natural hazard matters that are to be considered when making decisions on applications for particular activities, or for activities within a particular area.

Section 106 of the RMA provides an important directive to territorial authorities when assessing subdivision resource consent applications.  Under s106, a subdivision consent can be refused, or granted subject to conditions, if land (or any structure on the land) is likely to be subject to material damage by erosion, falling debris, subsidence, slippage or inundation from any source, or if any subsequent use likely to be made of the land is likely to accelerate, worsen, or result in material damage to the land, other land, or structure by the same.

Section 106 requires the territorial authority to undertake an assessment of how natural hazards might impact a proposed development, and of how the proposed development might impact any natural hazards.

Sections 106, 108 and 220 allow conditions to be placed on resource consent applications.  Placing conditions on granted consents allows territorial authorities to exercise control over the effects of development on natural hazards.  This is particularly so in the case of s106. Conditions set under s106 can be placed on a granted subdivision consent regardless of the activity status of the application and relate directly to mitigating the effects of subdivision on natural hazards.

Conditions set under s108 and s220 are limited to some extent by the activity status of the application. For controlled and restricted discretionary activities, if the district plan reserves council control to natural hazard matters or subdivision matters, conditions under s108 and s220 can relate to avoiding and/or mitigating the effects of natural hazards. For discretionary and non-complying activities, conditions can be set under s108 and s220 regardless of the content of the plan.

Case law relating to s106

a. The meaning of 'material damage '

Section 106 refers to material damage caused by various natural hazards and allows territorial authorities to decline subdivision consent, or to grant consent subject to conditions, if there is or is likely to be material damage to land or structures.

The meaning of material damage was discussed in Henry v Kapiti Coast DC W024/03, 8 NZED 483. In this case the Court explained that there are three types of damage:

 

An earlier case also considered the meaning of material damage. In Paviour v Napier CC W106/96 (PT), noted [1996] BRM Gazette 130, the Court decided that material implied something which is of great import, rather than minor slippage, subsidence or slumpage.

b. The meaning of 'likely '

The case of Kotuku Parks Ltd v Kapiti Coast DC EnvC A73/2000 noted [2000] BRM Gazette 89 has implications for deciding when material damage is "likely". In this case, the Court decided that because it is not standard practice to design for catastrophic events with long return periods (events that occur every 250 to 400 years were discussed in the case), s106 would not apply to damage from such events. This implies that catastrophic events are not "likely" to occur for the purposes of s106.

c. Meeting the requirements of s106

Having decided that material damage is likely to occur, the next step is to consider whether to decline consent under s106, or to grant consent subject to conditions. When making this decision, a territorial authority is able to take into account any measures put forward by the applicant that would avoid, remedy or mitigate the hazard effects referred to in s106.

In Foreworld Developments Ltd v Napier CC W089/98, 4 NZED 24, the Court stated that the onus is on the applicant, rather than the council, to propose measures to satisfy s106. It is then the Council's role to determine whether the proposed measures will be sufficient to meet the requirements of s106. If the Council decides that it is not satisfied, it does have a duty to indicate why it is unsatisfied.

The test used to determine if measures proposed by an applicant are sufficient to meet the requirements of s106 is set out in Maruia Soc Inc v Whakatane DC 8/3/91, Doogue J, HC Rotorua, partially reported at (1991) 15 NZTPA 65. The test outlined by this case is whether the measures put forward will result in the land being sufficiently protected to be suitable for subdivision.

The Court stated that the Council's decision on whether the land is sufficiently protected and suitable for subdivision will be a matter of degree. Total or absolute protection is not required.

This case was discussed and applied in Resource Planning & Management Ltd v Marlborough DC 10/10/03, France J, HC Wellington CIV-2001-485-814. The High Court summarised the test set out in Maruia as: the Council "does not have to ensure that the whole of the land is free from the risk of inundation but does have to ensure that 'in its judgement ' the land is 'sufficiently ' protected to be suitable for subdivision". In this case, the High Court decided that the council decision-maker had followed this approach to s106.

When making decisions under s106, councils therefore have to come to a decision on whether the land is suitable for subdivision, taking into account any measures proposed by the applicant to protect the land from the effects of natural hazards.

d. Vesting land as reserve under s106

Vesting land in the council as reserve may be a way to avoid, remedy or mitigate the potential hazard effects to the land (for example from coastal erosion), and therefore a way to meet the requirements of s106.

Because the onus is on the applicant to propose measures to meet s106, the Court in Foreworld Developments Ltd v Napier CC W089/98, 4 NZED 24 stated that the financial burden of any such measures also lies with the applicant. Therefore, there would be a substantial cost to an applicant if a reserve was to be vested in the council as a means of satisfying s106. As such, the Court ruled that consideration of other viable options must be available to the applicant before vesting land as reserve is imposed by the council as a condition of consent.

Functions common to Regional Councils and Territorial Authorities

Section 35 RMA imposes a general duty on regional councils and territorial authorities to gather information and undertake monitoring to effectively carry out their functions under the RMA. Subsection (5)(j) specifically requires regional councils and territorial authorities to keep records of natural hazards.

Section 67 (contents of regional plans) and s75 (contents of district plans) allow regional and district plans to include procedures for monitoring the efficiency and effectiveness of policies and methods contained in the plans.

Gathering information and keeping records of natural hazards provides regional councils and territorial authorities with a body of information that can be used for more effective natural hazard planning. Monitoring the effectiveness of policies and rules and the exercise of resource consents also provides information for more effective natural hazard planning.

Section 67 (contents of regional plans) and s75 (contents of district plans) allow regional and district plans to include methods (other than rules) to be used to give effect to the policies contained in regional and district plans.  As well as rules, non-regulatory methods of implementing natural hazard related policies can be used.  For example, an education programmes used to raise levels of awareness and enhance readiness.

Case law relating to functions of regional and district councils

a. Difference between occurrence of and effects of natural hazards

The Court of Appeal has noted that the reference in sections 30 and 31 of the RMA to the avoidance or mitigation of natural hazards refers to the avoidance or mitigation of the effects of the occurrence of a natural hazard, rather than avoidance or mitigation of the occurrence itself. Canterbury RC v Banks Peninsula DC [1995] 3 NZLR 189; [1995] NZRMA 452, also reported as Canterbury RC v Christchurch CC (1995) 1B ELRNZ 415 (CA), noted [1995] BRM Gazette 97; NZCLD, 5th Series, R—218.

Relating this back to the section of this report that discusses management options, this suggests that under the RMA, regional councils and territorial authorities are only required to use methods that modify behaviour, i.e. elements at risk and vulnerability, and are not required to use methods that modify the hazard itself.

b. Exercising control

The case of McKinlay v Timaru DC C024/01, 6 NZED 308 discusses what constitutes exercising control of the use of land for the purposes of avoiding or mitigating natural hazards, in the context of regional councils (s30). The Court states that it is not enough to set out in a regional policy statement which authority shall take responsibility for developing objectives, policies and rules relating to the control of land for the avoidance of natural hazards. A regional council has to actually implement regional rules to control natural hazards.

c. Overlapping jurisdiction of regional and district councils (s30 and s31)

The courts have considered the matter of the overlapping jurisdiction of regional councils and territorial authorities regarding controlling the use of the land for the avoidance or mitigation of the effects of natural hazards.

The Court of Appeal outlined the limits on functions of regional councils and territorial authorities in Canterbury RC v Banks Peninsula DC [1995] 3 NZLR 189; [1995] NZRMA 452 (CA), noted [1995] BRM Gazette 97; NZCLD, 4th Series, R—218. The Court emphasised that "it is not so much what can be controlled, but the purpose for which it can be controlled". Regional councils and territorial authorities can make rules which prohibit, regulate or allow activities for the purpose of carrying out their functions under s30 or 31. Neither a regional council nor a territorial authority can make rules for purposes falling outside of its functions. To this extent, regional councils and territorial authorities have overlapping rule-making powers and both are able to control the use of land for the avoidance or mitigation of the effects of natural hazards. However, the rule-making powers of a territorial authority are limited by s75, which required, at the time the case was decided, that district plans must not be inconsistent with regional policy statements and plans.

Section 75 now states that district plans must give effect to regional policy statements and must not be inconsistent with regional plans. However this change does not alter the application of this case.

In this case, the Court of Appeal decided that "the Canterbury Regional Council has the power to prohibit or restrict activities such as residential occupation and the erection of buildings in the Waimakariri Flood Plain, for the purpose of avoiding or mitigating natural hazards". This shows a clear overlap of functions as the regional council is able to impose land use controls that would normally be imposed by the district council. However, because the purpose of the control is avoiding or mitigating natural hazards, which is a function of the regional council, the regional council is able to impose such controls.

Another justification for the overlap of functions between regional councils and territorial authorities is the requirement in s30 for regional councils to achieve integrated management of resources in the region. The Court stated in North Shore CC (Re an application) A087/94, [1995] NZRMA 74, 4 NZPTD 90 that in order to achieve this goal, a regional council must be able to impose some measure of restraint on management decisions made by territorial authorities. The Court decided that this could include policies and methods establishing metropolitan limits.

d. Coordination of management between regional councils and territorial authorities

The decisions in the cases discussed above dealing with sections 30 and 31 suggest that coordination between regional councils and territorial authorities is required to effectively manage the effects of natural hazards under the RMA.

The Court has made this suggestion in Re the Tauranga District Council 1 July 2003 EnvC A111/2003. In this case Bollard J acknowledged that the district council shares responsibility for natural hazard management with the Bay of Plenty Regional Council, and stated that "establishment of an integrated approach in terms of methods, which can effectively and fairly address the avoidance and mitigation of particular natural hazards, is essential".

The implication of the decision in McKinlay v Timaru District Council C24/2001 EnvC Jackson J, 6 NZED 308, highlights another reason for coordination between regional councils and territorial authorities. In this case, the Court decided that a dwelling could be rebuilt after being destroyed by a natural hazard, even if the district plan rules prohibited dwellings being built in that location, provided the rebuilt dwelling was the same or similar in character, intensity and scale as the present dwelling, in accordance with s10. This means that s10 existing use rights 'override ' district plan rules.

However, the Court noted the different application of existing use right under s20 (now s20A). The implication is that if there were regional rules in place that prohibited building, the existing use rights would not apply in the same way because the test under s20A is much stricter.

This implies that regional councils and territorial authorities have to work cooperatively when formulating regional and district plan rules in order to avoid a situation where a lack of regional rules allows existing uses to continue after a building has been destroyed by a natural hazard event.

Case law relating to planning horizons

A number of cases have discussed the appropriate risk period to plan for when preparing regional and district planning documents.

Regional plan provisions were discussed in Save the Bay v Canterbury Regional Council C6/2001 EnvC, Jackson J. In this case, the Court considered that there needed to be greater recognition of catastrophic natural events, quoting a statement that 90% of damage to the environment caused by natural hazards occurs in 10% or less of events. The Court suggested that "authorities should recognise this inverse relationship in the preparation and wording of their plans".

District plan provisions regarding coastal development were discussed in Bay of Plenty Regional Council v Western Bay of Plenty District Council A27/02 EnvC Bollard J. In this case potential adverse effects through changed climate conditions and sea level rise were accepted by the Court as existing. The Court also acknowledged the inherent uncertainly in the area of coastal planning. The Court concluded that these factors, together with the principles of the NZCPS pointed to a precautionary approach to planning. As such, in this case the Court stated that it was sound to plan for the 100-year predicted risk period.

District plan provisions regarding coastal development were again discussed by Bollard J in Skinner v Tauranga District Council A 163/02EnvC. Bollard J again stated that a 100-year predicted risk period is reasonable for coastal planning. Factors considered by Bollard J included a lack of field data, the lack of certainly as to the impact of future climate change on various drivers of shoreline movement, and the precautionary element in the NZCPS.

A precautionary approach does not mean a council has to be ultra cautious. In this case, Bollard J removed a safety buffer zone because the effect of the zone would have gone "beyond the extent necessary to ensure sufficient and appropriate recognition of coastal hazard risk to those properties during the 100-year forecasting period".

The case law therefore points to a 100-year planning horizon, particularly for coastal hazard planning. Consideration also needs to be given to events of low frequency that have the potential to cause catastrophic effects.

Case law relating to integrated hazard management

In Save the Bay v Canterbury Regional Council C6/2001EnvC, Jackson J, the Court favoured integrated management of coastal hazards. The Court was concerned that the proposed regional coastal environmental plan addressed only coastal erosion and inundation and no other natural hazards. There were also insufficient rules following on from the stated objectives and policies. Failing to cover all coastal hazards was not an integrated management approach.

Case law relating to the relationship between RMA and Building Act

It is appropriate for councils to consider the potential for a building to be affected by sever storms, salt deposits and spray drift, regardless of the fact that the design and construction of the building is considered under the Building Act, Lowry Bay Residents Association v Eastern Bays Little Blue Penguin Foundation Inc W45/01 EnvC, Kenderdine J.

The Court discussed the relationship between the RMA and the Building Act in Bay of Plenty Regional Council v Western Bay of Plenty District Council A27/02 EnvC Bollard J. In this case the Court outlined the different purpose of each act as follows: "that under the RMA of promoting the sustainable management of resources in the context of the wide environmental perspective that the Act embraces; and that under the Building Act by focussing on the integrity and safety of buildings wherever they are located".

This relationship was again discussed in Re the Tauranga District Council 1 July 2003 EnvC A111/2003. Bollard J summarised the roles of each act as follows: "Under the Resource Management Act 1991 use of land and subdivision should avoid or mitigate natural hazards. The Building Act gives responsibility for granting building consent on land subject to specific natural hazards, with certain exceptions".

Emergency Management under the RMA