Canterbury Air Regional Plan - Te mahere ā-rohe mō te hau o

Canterbury Air Regional PlanTe mahere ā-rohe mō te hau o Waitaha October 2017

Canterbury Air Regional Plan - Te mahere ā-rohe mō te hau o Waitaha 2017

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Environment Canterbury

Table of contents

Introduction - Understanding the Canterbury Air Regional Plan 1 -11

Issues of significance to Ngāi Tahu 2 -12

How the Plan Works 3 -13

Definitions and Interpretation 4 -14

Objectives 5 -15

Policies 6 -16

Rules 7 -17

Schedules 8 -18Schedule 1: Information to be provided with applications for resource consent 8 -1Schedule 2: Assessment of offensive and objectionable effects 8 -5Schedule 3: Content of smoke management plans for the outdoor burning of organic material in ruralareas 8 -14Schedule 4: Contaminants 8 -15Schedule 5: Emission Stack Heights for Large Scale Fuel Burning Devices 8 -17Schedule 6: Application of Ringelmann Scale 8 -18Schedule 7: Testing for particulate matter in exhaust gases 8 -22Schedule 8: Registration and maintenance of small-scale heating appliances burning solid fuel 8 -23Schedule 9: Small-scale heating appliance auditing process 8 -24Schedule 10: Heritage Buildings 8 -28Schedule 11: Areas affected by the Ngāi Tahu Claims Settlement Act 1998 8 -33

Clean Air Zone Map Series 9 -19

Canterbury Airsheds 10 -110

Crop Residue Burning Buffer Area Map Series 11 -111

Canterbury Air Regional Plan General Map Series 12 -112

Special Zones 13 -113






1 Introduction - Understanding the Canterbury Air RegionalPlan

Tīhei mauri ora.Pātai mai he aha te mea nui o te ao

Ka whakahoki auHe tangata, he tangata, he tangata.

Tīhei mauri ora.

(Translation)The breath of life.

Ask me what is the most important thing in the worldAnd I will reply

It is people, it is people, it is people.The breath of life.

- Whakataukī

The Purpose of this Plan

The Canterbury Region enjoys good air quality in most places and at most times. Consequently, air qualitycould be taken for granted. But in fact urban areas, both towns and cities, suffer from degraded air quality atregular intervals. Ambient air can be polluted by contaminants or localised air quality may be compromisedby dust, smoke or odour. The effects vary from pervasive and serious health impacts to nuisance effects thatdetract from the amenity values of an area.

The purpose of the Resource Management Act (RMA) is to promote the sustainable management of resourcesfor the benefit of people, including by “safeguarding the life-supporting capacity of air, water, soil andecosystems”. Previously Ngāi Tahu alone exercised rangatiratanga (guardianship) over the Canterbury Regionki uta ki tai (from the mountains to the sea). They regarded air as mauri (a life force) and therefore as a taonga(treasure) to be protected for the benefit of future generations. This heritage, recognised in the RMA, gave riseto the duty upon councils to consult tangata whenua to ensure that their culture and traditions are suitablyaccommodated in air and other resource management plans.

The Air Plan seeks to manage discharges to air in the best practicable manner. Its principal purpose is tomaintain air quality where it provides for people’s health and cultural wellbeing, or to improve it if it does not,whilst recognising the investment in, and significant contribution to the economy and social wellbeing ofCanterbury of industrial and trade activities that discharge into air.

Air Quality in Canterbury

Some parts of the world confront constant serious pollution from an urban concentration of heavy industry,coal-fired power stations and vehicle emissions, while in other parts smoke from large scale outdoor burningor major dust storms are the predominant issues. In comparison, most of Canterbury enjoys air quality thatranges from good to pristine. The clear air and lack of light pollution in the Mackenzie Basin provides forexcellent visibility of the night sky that has received international recognition. Our rural areas have good airquality most of the time but can be affected by burn-offs and other rural practices. Our towns and citiesexperience poorer air quality, particularly in winter, both from the burning of coal or wood to produce heatfor industry or home heating, and the burning of petrol or diesel in vehicles.

Meteorological conditions and the lie of the land may alleviate or exacerbate air pollution. For example,temperature inversions are a Christchurch characteristic. These typically occur in winter when cold air istrapped beneath a layer of warm air and pollutants cannot rise and disperse.

1 – 1Environment Canterbury


Types of Contaminants

Air contaminants come from a variety of sources and have varying physical and chemical characteristics. Suchsources are both natural and man-made (anthropogenic). The air contaminant of most concern in Canterburyand most of New Zealand is particulate matter (PM). The natural sources of PM include pollen, sea spray, andwindborne dust (soil). The Air Plan cannot control or even influence these natural sources. Fortunately, theparticles are comparatively large and are possibly less of a threat to human health.

PM is identified by reference to size, as eitherSARAH PM10 or PM2.5. PM10 comprises particles less than 10 micronswhile PM2.5 particles have a diameter less than 2.5 microns. PM can penetrate deep into the lungs and even intothe bloodstream if the particles are ultrafine. Damage to the respiratory and circulatory systems results. Thosemost at risk are young children, the elderly and people suffering from respiratory and cardiovascular disease.Air quality standards and guidelines have been established for PM10 at a national level, however there is currentlyno New Zealand guideline for PM2.5.

Health impact assessments (such as the HAPINZ study, updated 2012(1)) have been undertaken to assist inunderstanding the extent of the harm caused to human health from PM exposure. These indicate that eachyear in Canterbury more than 400 adults over 30 years of age die prematurely because of their exposure topoor air quality, while many others require admission to hospital or are rendered unwell and miss work days.

Towards the middle of the spectrum there are a number of harmful chemicals discharged from industrialactivities, vehicles and home heating, which are generally present as gases. Those include carbon monoxide,nitrogen dioxide, sulphur dioxide, benzene, benzo(a)pyrene and polycyclic aromatic hydrocarbons (PAHs).Exposure to these contaminants can cause health effects, some similar to those occasioned by exposure toPM. This group is subject to air quality standards, or guidelines, promulgated by central government. The AirPlan imposes controls upon their discharge on an activity basis and in an endeavour to ensure that the prescribedmaximum levels are not exceeded. Although localised exceedances occur occasionally in the CanterburyRegion, the risk posed by these contaminants remains secondary to that from exposure to PM.

At the other end of the spectrum are contaminants that predominantly affect wellbeing rather than physicalhealth. The main ones are smoke and dust discharges. The Air Plan imposes controls upon these dischargesby reference to the so-called FIDOL factors: the frequency, intensity, duration, offensiveness and location ofthe discharge.

Sources of Contaminants

The Canterbury Regional Council (CRC) maintains emission inventories relating to the principal locations, wherea pollution problem exists. These have a main focus on PM10 as this is the primary pollutant affecting theseurban areas. The most recent PM10 source emission figures at the time the Air Plan was prepared are:

Contribution to man-made PM10 emissionsSource

57% - 93%Home heating

5% - 27%Industrial

2% - 23%Vehicles

The width of the range attributed to each source reflects the diversity of the urban locations. One location isdominated by the home heating contribution (93%), meaning that the other sources are insignificant. InChristchurch, however, home heating remains predominant (57%), but industry (27%) and motor vehicles(23%) are also significant contributors.

The Air Plan imposes controls on home heating and industrial discharges, but not on motor vehicle emissions.Vehicles, being mobile, are beyond the reach of regional councils. Instead vehicle emission standards and fuelspecification are the province of central government.

1 HAPINZ health effects model: http://www.hapinz.org.nz

Environment Canterbury1 - 2


http://www.hapinz.org.nz

The Understanding of Air Quality

The science of air quality is complex and the state of knowledge continues to evolve. A current and pertinentexample of this concerns air quality guidelines for PM10, and its subset PM2.5. Under the Resource Management(National Environmental Standards for Air Quality) Regulations 2004 (the NESAQ), regional councils are requiredto monitor PM10 and publicly report where the average 24 hour levels exceed 50 micrograms per cubic metreof air (50 µg/m3) on more than one day per annum. This level was derived from a World Health Organisation(WHO) guideline.

But WHO now recommends guidelines for both PM10 and PM2.5:

Guideline Concentration (µg/m3)Averaging period

PM2.5PM10

255024-hour average

1020Annual average

The international consensus is that PM2.5, a component of PM10, is the more insidious of the two and that longterm exposure is more harmful to health than is short term exposure. The implications of this shift are underconsideration in New Zealand at present, but in the meantime we remain subject to a short term PM10 basedexposure limit. This is significant because exceedances in New Zealand are characterised by spikes in the wintermonths on cold days when meteorological conditions are adverse.

Nonetheless, the monitoring data shows that while the long term exposure profile in Canterbury is largelycompliant for PM10, improvements are required in long term PM2.5 air quality:

Annual PM2.5 Concentration (µg/m3)Annual PM10 Concentration (µg/m3)Location/Airshed

Guideline = 10 µg/m3Guideline = 20 µg/m3

2013201220132012

--20.421.2Ashburton

11.19.819.719Christchurch –St Albans

11.110.424.422.7Christchurch - Woolston

--1820.1Geraldine

--18.218.4Kaiapoi

--16.217.2Rangiora

141526.927.6Timaru

--17.417.9Waimate

--18.416.5Washdyke

Source: Statistics New Zealand Environmental Indicators Reporting (http://www.stats.govt.nz/)

When Will Good Air Quality be Assured?

This is an unknown, or more likely the correct answer is never. Attaining a state of stable good air quality ismost unlikely because change is a fact of life and many sources of air pollution are naturally occurring. Change,whether in relation to the population demographic of a region, new industrial activity, changed housing location,improved scientific understanding, climate change, new rural activities or a myriad of other possibilities willthrow up new challenges. Good air quality, therefore, will remain a work in progress.



Once this is recognised it also becomes apparent that the goal of improving ambient air quality is necessarilya long term objective. Substantial gains have already been made and improvement in air quality has beenachieved in many of the polluted urban areas within the Canterbury Region. Further improvement will be moredifficult. It will take time. Progressive improvement must be the goal. The Air Plan is crafted to incentiviseimprovement over time.

A Balanced Approach

As is aptly recognised in the RMA the sustainable management of resources, air included, may require abalancing exercise. There is often a tension between promoting people’s social, economic and cultural wellbeingand their health and safety, on the one hand; and safeguarding the life-supporting capacity of air on the other.

In this Plan the tension is most acute in relation to the need to improve air quality in areas where it is degraded,while at the same time ensuring that vulnerable households are not exposed to fuel poverty and to living incold damp houses. The strategy designed to further improve the particulate discharge levels from home heatingappliances involves requirements to decommission the existing stock of wood burners over time and replacethem with ultra-low emitting enclosed burners (ULEBs) or other clean technology. Ironically these initiatives,intended to improve health outcomes by providing improved ambient air quality, have the potential to exposepeople to adverse health impacts if the correct balance is not struck. The Air Plan seeks to avoid this perverseoutcome by ensuring that existing technology is phased out over a timeframe sufficient to enable householdersto plan for change, with assistance provided where genuine need exists.

Key Management Response for Air Quality

The management of air quality is complex. Ensuring access to good quality air while balancing the social andeconomic costs of achieving this requires a multi-pronged approach. The approach the CRC has adopted hasthe following components:

a statutory planning framework that supports the non-regulatory programmes;

non-regulatory education, advocacy and support programmes, particularly for PM10 and PM2.5 reduction;

working co-operatively with key partners.

The NESAQ sets targets for air quality improvement in polluted airsheds. It is the responsibility of the CRC tomonitor and enforce observance of these targets. This will occur through a combination of both thenon-regulatory work programme and statutory requirements.

The Statutory Planning Framework

The primary legislation for managing natural resources in New Zealand, including air quality, is the ResourceManagement Act 1991 (RMA). The single purpose of the RMA is the promotion of the sustainable managementof natural and physical resources. This involves managing the resources of the Canterbury Region in ways thatprovide for the needs of current and future generations, and ensures that adverse effects on the environmentare avoided, remedied or mitigated.

The content of an air plan is dictated to a significant extent by requirements of the RMA. Public consultationis a first requirement that precedes, and influences, the content of a plan. In achieving the purpose of the RMA,regional councils are required to give effect to higher order documents, including National Policy Statementsand National Environmental Standards.

The Canterbury Regional Policy Statement sets the overarching policy for the Region and must be given effectthrough Regional and District Plans. Chapter 14 of the Canterbury Regional Policy Statement is devoted to airquality. It identifies the key issues and also prescribes two overarching objectives and five policies to guidethe management of air quality in the Canterbury Region. The Air Plan gives effect to the Policy Statement by:

setting out objectives, policies and methods that provide a framework to reduce PM10 concentrations,including by controlling discharges of contaminants into air from home heating, industry and othersources and encouraging the uptake of cleaner technology, in polluted airsheds so that the targets setby the NESAQ can be achieved; and



providing a framework that enables consideration of industry offsets in accordance with Regulation 17of the Resource Management (National Environmental Standards for Air Quality) Regulations 2004, andwhich provides opportunity for industry to access offsetting opportunities in the domestic market; and

setting a framework for the management of PM10 and other contaminants discharged into air that ensuresair quality is maintained or improved across the Region, and sensitive and discharging activities areprotected from each other.

In preparing an air plan, regional councils must also have regard to other regional planning documents thatare in the course of development, including the planning initiatives of adjacent regional councils. Iwi managementplans lodged with the council must be taken into account where relevant.

Section 15 of the Resource Management Act

Section 15 of the RMA is pivotal to the preparation of air plans. It prohibits all industrial discharges ofcontaminants except those expressly allowed by a national environmental standard, a national regulation ora rule in a regional plan. On the other hand, discharges from all other sources are allowed except if theycontravene a standard, a regulation or an air plan rule. In practice this means that air plans need to containexpress provisions to accommodate industrial activity in the region; while discharges from all other sources(whether from domestic, outdoor burning or farming activities) need only be regulated where some level ofcontrol is considered necessary.

Resource Management (National Environmental Standards for Air Quality) Regulations 2004

In addition to setting targets for air quality, the NESAQ includes regulations that must be given effect throughthe regional planning framework. These important regulations impose a number of national controls, including:

prohibitions on the outdoor burning of various forms of waste;

ambient air quality standards (limits) for various contaminants in polluted urban areas gazetted asairsheds;

requirements upon regional councils to monitor PM10 levels in airsheds and decline resource consentswhere PM10 limits will be exceeded;

prohibitions on granting resource consents for the discharge of various chemical contaminants in airsheds;

design and thermal efficiency standards for domestic woodburners;

a prohibition upon domestic open fires in airsheds.

The Air Plan in many respects reflects and builds upon these national standards. It also imposes some controlsthat are more stringent than those applicable nationally, particularly through the use of the Clean Air Zoneconcept.

National guidance is also provided in the Ambient Air Quality Guidelines 2002, an update of the 1994 version.They identify limits at which a wide range of contaminants will degrade ambient air, as opposed to a safe limitto pollute up to. The document advises readers how to apply the guideline values and also initiate emissionreduction strategies. Although not legislative requirements, the guidelines have informed the approach to,and content of, some rules in the Air Plan, particularly those that govern industrial discharges.

Working with Key Partners

Ngāi Tahu, as Kaitiaki, are key partners in air quality management. The relationship of Ngāi Tahu with naturalresources and the environment in Canterbury is set out in section 3 of the Air Plan.

District Health Boards have a particular interest in improving health outcomes for Cantabrians, and inrecognition of the health effects of poor air quality, the Canterbury and the South Canterbury District HealthBoards and Community Public Health have partnered with the CRC through the development of the Air Plan.In particular, the health boards have a role in the non-regulatory aspects of improving air quality, assistingthe CRC in ensuring we deliver both clean air and warm homes. The CRC and the Canterbury District HealthBoard and its statutory body work collaboratively in relation to nuisances under Section 29 of the Health Act1956.



Territorial Authority partnerships are essential to managing air quality. Managing air quality requires anintegrated approach across local government. CRC’s ability to manage discharges to air, and to ensure thatthe adverse effects on surrounding communities are mitigated, is assisted where district plans provide fordischarging activities to be located in appropriate areas. Where activities that discharge contaminants into airare provided for, they must be protected from reverse sensitivity effects through provisions that ensureavoidance of the encroachment of sensitive activities into areas where discharging activities are located.

Industry can provide solutions to air quality issues through the development and adoption of cleaner technology.The Air Plan has been prepared to support and enable innovation across all sectors, and encourage uptake ofthe cleanest technology. The CRC has, through the Air Plan, encouraged the development of cleaner domesticsolid fuel burning technology, so that a range of heating options are available for the community.

Non-regulatory Programmes

The non-regulatory programmes are essential to achieving good air quality across the Region. These programmeshelp to ensure that reducing emissions of particulate, particularly from home heating, does not result in theperverse outcomes of replacing poor air quality related health impacts with cold home related health impacts.CRC recognises that implementation of the Air Plan will come at some social cost and the non-regulatory workprogramme is designed to ensure that these costs are minimised while the health benefits of improved airquality are maximised, so that the community experiences an overall benefit. These programmes are tailoredannually to suit the needs of each community in Canterbury and include the following work streams:

supporting both warm homes and clean air through heating help and assistance programmes;

education and awareness campaigns;

working with wood merchants to ensure the supply of properly seasoned wood;

encouraging development of new technology;

working closely with territorial authorities, health boards, industry and communities in order to identifyand implement solutions.

Two Factors That Have Shaped the Air Plan

The first concerns change that has affected the Region during the lifetime of the previous air plan, containedin Chapter 3 of the Canterbury Natural Resources Regional Plan. The sequence of earthquakes that commencedin late 2010 has had an influence on the Air Plan provisions. The earthquakes caused a substantial loss of theprevious housing stock, the relocation of thousands of people, dust problems from demolition work, the needfor the urgent construction of new housing and other buildings, and the use of emergency powers by theMinister for Earthquake Recovery. Innovative solutions were required, and the lessons learnt have had aninfluence in the preparation of the Air Plan.

Over a longer timeframe the Region has experienced an unprecedented growth in rural farming activity. Thistoo required accommodation in the Air Plan. The location of large scale processing infrastructure in rural areasposed new issues that required consideration; as did the scale of development of stock housing structuresand associated effluent storage and discharge facilities.

Structure of the Air Plan

The style of this plan is different to that employed in the previous Air Plan. While the coverage and subjectmatter is necessarily similar, this plan is more succinct. The provisions are not accompanied by explanationsconcerning the reasons for and results anticipated from them. In this regard the new Air Plan builds on theold, so that less is more. In addition, the Air Plan is now a stand-alone document.



Strategic Concepts That Underpin the Plan

A key spatial, or area–based, concept that underpins the Air Plan is a division of the Canterbury Region intothree distinct geographical areas.

These are:

Airsheds

Clean Air Zones (CAZs); and

Areas outside the CAZs.

Airsheds are a creature of the NESAQ. They are urban areas that have a PM10 exceedance history. This resultsin their being classified as an airshed with closely defined boundaries by virtue of a Ministerial Notice in theNew Zealand Gazette. This process is under the control of central government, although the PM10 monitoringthat results in this outcome is undertaken by regional councils. The NESAQ prescribes various requirementsapplicable to monitoring, exceedance levels and resource consents in polluted airsheds.

Canterbury has eight airsheds. They are in Christchurch, Rangiora, Kaiapoi, Ashburton, Timaru, Geraldine,Waimate and Washdyke. Situated on the outskirts of Timaru, Washdyke was split off from the Timaru airshedand gazetted in July 2015 some months after the Air Plan was notified. It is unique in that its pollution problemis attributable to industrial discharges, whereas in the other airsheds industry is a less significant or minorplayer.

Clean Air Zones are areas identified in Section 9 of the Air Plan, the Clean Air Zone Map Series. In general termsthe CAZs surround, and include the particular airshed, and are identified as such because discharges into theair from anywhere within the zone may impact on air quality within the polluted airshed, so there is a need formore stringent controls. A number of industrial and space heating rules are specific to the CAZs, or even to aparticular zone.

All areas outside the CAZs comprise the third spatial area. This is most of the land area within the CanterburyRegion, comprising predominantly farm land but also a large number of smaller towns. Some of these townshave pollution issues that may require regulatory control when better monitoring data is available. For now,the rules applicable to the outside area are less onerous than those tailored for application within the CAZs.

Another spatial concept is used in the Plan to complement the CAZ framework. A number of rules, applicableboth within and outside the CAZs, differentiate between properties that are 2ha or greater and propertiesunder this size limit. The larger properties have special needs in relation to disposal of organic waste (fromtrees and hedges) and also a greater capacity to internalise harmful or nuisance effects beyond their boundaries.

Crop Residue Burning Buffer Area

Section 11 to the Plan is a Crop Residue Burning Buffer Area Map Series. Two maps identify buffer areas aroundAshburton and Timaru. Some rules regulate crop residue burning by drawing a distinction between rural areas“outside”, and “inside”, the buffer areas.






2 Issues of significance to Ngāi Tahu

Ngāi Tahu

This section explains Ngāi Tahu’s traditional relationship with the natural environment, defines various tenetsthat are fundamental to that relationship and records some statutory rights and requirements framed inrecognition of Ngāi Tahu’s generational guardianship of the area that now comprises the Canterbury Region.

At a more practical level the section also sets out the information required to enable people to understandand meet their obligations under various provisions in the Air Plan that afford protection to values, and areas,of special significance to Ngāi Tahu.

The Ngāi Tahu view of the Natural World

Whakapapa

Whakapapa, although commonly defined as meaning ‘genealogy’, explains the origins of everything, past andpresent, within the Māori world. It is the central pillar of the framework, setting out and effectively explainingthe inter-relationships between the land, sky, oceans, rivers, elements, minerals, plants, animals and people,and how each was created. It is through whakapapa that all things are intricately linked, as well as having theirindividual place in the world. Ultimately it is whakapapa that connects people to each other, to their ancestors,to the land and to natural resources.

All these elements lie at the root of Ngāi Tahu existence and meaning, while values, resources, and age-oldcustoms distinguish Ngāi Tahu from other iwi and also identify hapū and iwi as mana whenua within the rohe(boundaries) of the Canterbury Region.

Taonga

It is through Ngāi Tahu genealogical ties that all natural resources - air, land, water, and indigenous biodiversity- are considered taonga, and are valued or treasured. Taonga are passed on by the ancestors to be protected,and to provide for and sustain life.

Taonga includes both tangible and intangible things. Tangible taonga includes all natural resources, importantspecies, sites where food and cultural resouces are gathered, significant landforms and special culturallandscapes. Intangible taonga includes Te Reo, and tikanga (customs). All taonga comprise part of the culturaland tribal identity of an iwi.

Wāhi taonga

Wāhi taonga are “places treasured” due to their high intrinsic values and their capacity to shape and sustainthe quality of life experience and provide for the needs of present and future generations. The ability to viewcertain wāhi taonga from a distance is important to people’s spiritural wellbeing. Poor air quality can affectpeople’s experience of wāhi taonga and their visibility; therefore, continued maintenance and protection ofair quality surrounding wāhi taonga is important to provide for people’s phsyical and cultural wellbeing.

Wāhi tapu

Wāhi tapu are places of particular significance that have been imbued with an element of sacredness orrestriction (tapu) following a certain event or circumstance (e.g. death). Wāhi tapu sites are treated accordingto local customs (tikanga and kawa) whereby the tapu nature of those sites is respected. Of all wāhi tapu,urupā (burial sites) are considered to be the most significant.



Kaitiaki

Kaitiaki is the exercise of guardianship over the air, sky, sea and land. Ngāi Tahu preservation of their culture,traditions and taonga is equally reflected through the system of kaitiaki.

Traditionally, kaitiaki were the non-human guardians of the environment (e.g. birds, animals, fish and reptiles)which, in effect, communicated the relative health and vitality of their respective environments to local tohunga(experts) and rangatira (leaders) who were responsible for interpreting the ‘signs’ and making decisionsaccordingly. In essence, there is no real difference to scientific practices of today, which continue to use specificindicator species and observe their behaviours to measure the state of the environment.

Kaitiakitanga

Kaitiakitanga is defined in the RMA as “the exercise of guardianship by tangata whenua of an area in accordancewith tikanga Māori in relation to natural and physical resources; and includes the ethic of stewardship.”

The Ngāi Tahu framework for managing natural resources has evolved from a distinct Polynesian world viewwhich acknowledges that people are part of the world around them and not masters of it. It then developedthrough more than 40 generations of collective experience in Te Waipounamu.

Kaitiakitanga is fundamental to the Ngāi Tahu relationship with the environment. It entails the active protectionof natural resources - air, land, water and indigenous biodiversity - to maintain and protect the mauri (lifeforce) of all taonga. Kaitiakitanga is more than guardianship. It is an inter-generational responsibility inheritedat birth to care for the environment, which is passed down from generation to generation.

Mauri

Mauri is the most important factor in relation to air quality. It is the health and spirit often described as the‘life force’ or ‘life principle’ of any given place of being, or of the air that provides life. It can also be understoodas a measure or an expression of the health and vitality of that place or being. The notion embodies the NgāiTahu understanding that there are both physical and metaphysical elements to life and that both are essentialto overall wellbeing.

It also associates the human condition with the state of the world around us. Mauri, therefore, is central tokaitiakitanga; that is, the processes and practices of active protection and responsibility by mana whenua forthe natural and physical resources of the takiwā.

Mauri can change either naturally or through intervention and Ngāi Tahu use both physical and spiritualindicators to assess its relative strength. Physical indicators include, but are not limited to, the presence andabundance of mahinga kai fit for consumption or cultural purpose. Spiritual indicators are the Kaitiaki referredto previously. They are often recalled in kōrero pūr`ākau (oral traditions) to explain the intrinsic connectionbetween the physical and metaphysical realms within each takiwā held by mana whenua.

Mauri Oho! Mauri Tū! Mauri Ora!(If the mauri or life force is awakened, and upheld, then all living things shall be sustained)

Mahinga Kai

The Ngāi Tahu Claims Settlement Act 1998 describes mahinga kai as “the customary gathering of food andnatural materials and the places where those resources are gathered.” Mahinga kai is a corner stone of theNgāi Tahu cultural identity and relationship with landscapes and waterways of Te Waipounamu.

The ability to continue to gather natural resources and to pass on these cultural values to the next generationis paramount to Ngāi Tahu whānui. This is encompassed in the natural resource philosophy of “ki uta ki tai”,from the mountains, to the sea. This reflects the holistic nature of traditional resource management, particularlythe inter-dependent nature and function of the various elements of the environment. Through the principlesof kaitiaki, Ngāi Tahu assumes a responsibility to sustainably manage mahinga kai resources for the needs offuture generations.



Rohe of the Canterbury Region

The entire Canterbury Region lies within the traditional takiwā of Ngāi Tahu which runs from the Sub Antarcticislands in the south to Te Pari-nui-o-Whiti (White Bluffs) in the north and to Kahurangi Point (between Karameaand Farewell Spit) on Te Tai Poutini (West Coast). Ngāi Tahu is the largest iwi (tribe) in the South Island,comprising of hapū (sub-tribes) and whānau (extended families) who continue to express their mana whenuawithin their respective areas (takiwā) through the following key precepts:

protection and perpetuation of their whakapapa

continued occupation of their ancestral lands (ahi-kā-roa)

continual use of traditional and contemporary natural resources (mahinga kai)

taking responsibility to protect and maintain the mauri (vitality) of their environment for the benefit andenjoyment of future generations.

The CRC recognises Ngāi Tahu mana whenua through its relationship and consultation with Nga Rūnanga ofthe Canterbury Region and Te Rūnanga o Ngāi Tahu.

Mana whenua

Mana whenua is the right to exercise authority over a particular area (takiwā), its resources and its people.Mana (respect, standing, authority) is passed on via whakapapa and is protected and secured through theon-going exercise of rights to resources in a manner consistent with tikanga. Inevitably with mana comesresponsibility.

Following the confinement of Ngāi Tahu property rights to native reserves, local Ngāi Tahu communities beganto establish ‘Rūnanga’ (i.e. an assembly or council) to facilitate the representation of their rights and interestsin the evolving new system of local governance and resource management.

Marae were built at the heart of these communities. They were bastions of Ngāi Tahu tikanga and kawa (customs,laws, protocols) and came to be known as “papatipu marae”; that is, the marae based communities in whichflax roots Ngāi Tahu are nurtured and raised.

With settlement of the Ngāi Tahu historic Treaty grievances in 1998 and the enactment of the Te Rūnanga oNgāi Tahu Act 1996, the tribe re-structured itself again under the auspices of one tribal rūnanga (Te Rūnangao Ngāi Tahu) with 18 regional rūnanga (Nga Rūnanga o Ngāi Tahu).

Te Rūnanga o Ngāi Tahu was established to give the tribe a legal identity and, where prudent, represent theentire tribal collective of Ngāi Tahu whānui. It has also become the ‘iwi authority’ for Ngāi Tahu for the purposesof the RMA.

Nga Rūnanga were established to represent the rights and interests of local whānau and hapū internally withinthe new tribal structure and externally with the likes of local and regional government agencies within theirrespective takiwā.

Papatipu Rūnanga

Nga Rūnanga have come to be known as ‘Papatipu Rūnanga’, but only because of their relationship to thepapatipu marae communities they represent.

The mandated representatives of Ngāi Tahu who have customary authority over air, the land, waterways andsea of their respective takiwā and responsibility for environmental issues are the Papatipu Rūnanga. Wheneverinformation or discussion is required with respect to resource consent and environmental issues it is importantto identify and contact the mandated Rūnanga responsible for the particular area.

The 10 Papatipu Rūnanga within the Canterbury Regional Council rohe are:

Te Ngāi Tūāhuriri RūnangaTe Rūnanga o Kaikōura

Te Rūnanga o KoukourārataTe hapū o Ngāi Wheke (Rāpaki)



Ōnuku RūnangaWairewa Rūnanga

Te Rūnanga o ArowhenuaTe Taumutu Rūnanga

Te Rūnanga o MoerakiTe Rūnanga o Waihao

The below figure shows the names and location of the 10 Papatipu marae within the Canterbury Region as wellas their primary hapū and representative Rūnanga.

Contact details for each Rūnanga can be found at http://www.Ngāi tahu.iwi.nz/

The Ngāi Tahu Claims Settlement Act 1998

Together Te Tiriti o Waitangi and the RMA promote sustainable management of natural and physical resources.In relation to Ngāi Tahu, this can be interpreted as enabling iwi/hapū to provide for their cultural wellbeingthrough their world view.

Te Tiriti o Waitangi, contained the Crown’s agreement “to protect the Chiefs, the sub-tribes and all the peopleof New Zealand in the unqualified exercise of their chieftainship over their lands, villages and all their treasures.”Thereby mana whenua was recognised.

But this agreement was not honoured and, eventually, the Crown and Ngāi Tahu concluded a Deed of Settlement,and the Ngāi Tahu Claims Settlement Act was enacted to redress, where possible, serious breaches of theTreaty. The Act includes a number of mechanisms to recognise and meet concerns of particular importanceto Ngāi Tahu including the creation of statutory acknowledgement areas, declarations of tōpuni, and nohoangaentitlements.

Statutory acknowledgement areas are recognised in the Ngāi Tahu Claims Settlement Act as areas in relationto which Ngāi Tahu has “a particular cultural, spiritual, historic and traditional association.” Recognition meansthat the areas must be shown on council maps and referenced in regional plans, so that Ngāi Tahu can havean input into resource consent applications and be heard in Court when issues relating to a statutoryacknowledgement area arises. The areas include mountains, lakes, rivers and various land features.

Declarations of Tōpuni The concept of tōpuni derives from the tikanga (customs) of rangatira (Chiefs) extendingtheir mana and protection over people or areas by placing their cloak over them. A declaration of Tōpuni madeunder the Ngāi Tahu Claims Settlement Act similarly places an overlay of Ngāi Tahu values over Crown landusually managed by the Department of Conservation (DoC). The declaration requires that DoC or the managementboard consult and listen to Ngāi Tahu in relation to plans and strategies for Tōpuni areas.

Nohoanga Entitlements granted under the Ngāi Tahu Claims Settlement Act permit Ngāi Tahu to have seasonalcamp sites on Crown land close to waterways to access fish and natural resources. Nohoanga entitlements,declarations of Tōpuni and statutory acknowledgement areas within the Canterbury Region are shown below.



http://www.ngaitahu.iwi.nz/

Statutory Acknowledgement Areas, Declarations of Tōpuni and Nohoanga Entitlements



Information available from the Canterbury Regional Council

The RMA contains information requirements relating to the iwi and hapū that exercise kaitiakitanga within anyparticular region. These requirements are of assistance to users of the Air Plan, in particular those who requirea resource consent for an activity that may cause effects adverse to the interests or values of Ngāi Tahu.

The Crown must provide to the Council details of the iwi and hapū who exercise kaitiakitanga within the region,including the particular areas over which the iwi and hapū provide stewardship. The Council must in turnmaintain an accessible record of the information provided to it.

That record must contain:

contact details for both the iwi and the hapū;

maps, or their equivalent, that show the areas over which iwi and hapū exercise kaitiakitanga;

any planning document recognised by an iwi authority provided it has been lodged with the Council.

Where, as in the Canterbury Region, there are multiple hapū represented by separate Papatipu Rūnanga,details for each hapū will be recorded.

The relevant planning documents in the present context are iwi management plans. Ngāi Tahu has set out itsresource management values, issues, objectives and policies in a number of iwi management plans throughoutthe Canterbury Region. These have been prepared in order to facilitate the exercise of Ngāi Tahu Rangatiratanga(chieftainship) over their lands, villages and all their treasures as per Article II of the Treaty / Te Tiriti, includingthe exercise of their kaitiaki responsibilities as Mana Whenua.

Iwi Planning documents provide information for assessing potential impacts on cultural values and interests.While they are not statutory instruments iwi management plans have weight under the RMA. Assuming theirrecognition by an iwi authority and lodgement with the Canterbury Regional Council, iwi management plansmust be “taken into account” if their contents are relevant to the resource management issues of the region.Local authorities must also take such plans into account when preparing regional or district plans under theRMA. In the preparation of this Plan an analysis of the iwi management plans was conducted. The CRC maintainsa relationship with Ngāi Tahu through both the Te Rūnanga and Nga Rūnanga in the Canterbury Region. TheCRC also has a joint work programme with Ngāi Tahu called “Tuia”.

Consultation with Ngāi Tahu

In the first instance Plan users should inspect the records held by the CRC to obtain information relating tosites and matters in which Ngāi Tahu have a cultural or other special interest.

Should the Council not have relevant materials on Ngāi Tahu values, then consultation with hapū is the onlymeans by which information can be obtained and it is good practice to do so. The level of consultation willvary depending on the nature of the issues and what is required to assess adverse effects on sites of culturalsignificance. In matters to do with the management of natural resources within individual takiwā, a particularRūnanga will have responsibility for management as kaitiaki and it alone should be consulted.

The need for consultation is most likely to arise in relation to rules which include a condition that a dischargemust not occur within a specified distance of “a sensitive activity, wāhi tapu, wāhi taonga or place of significanceto Ngāi Tahu”. Permitted activity rules with such a condition have an addition to the above formulation, namely“that is identified in an Iwi Management Plan”. But in relation to non-permitted activity rules where a resourceconsent application is required these additional words are not included in the condition. Accordingly, Planusers in the former category need only inspect the relevant Iwi Management Plan, while those who require aconsent will need to talk to CRC staff and in some instances consult the affected hapū as well.

The RMA and the Local Government Act 2002, require the CRC to consult with Ngāi Tahu in respect of themanagement of natural and physical resources of the Canterbury Region, including the preparation or changingof regional plans. If a resource consent application is not publicly notified, consenting authorities must decidewhether “affected person” status should be accorded to anyone. In relation to Ngāi Tahu this may mean thatTe Rūnanga or a Nga Rūnanga are to be notified depending on the area to which the application relates.



How the Air Plan Addresses Issues of Significance to Ngāi Tahu

To inform the development of the Air Plan a report was prepared in 2013 outlining issues of significance to NgāiTahu regarding air quality. A recommendation of the report was that the extent to which the Air Planaccommodated issues of significance to Ngāi Tahu would be shown by how well the policies and rules in thePlan achieved outcomes desired by Ngāi Tahu:

the life supporting capacity and mauri of air is maintained for future generations.

Ngāi Tahu are involved in regional decision-making on air quality issues.

sites of cultural significance, including wāhi tapu, wāhi taonga, marae, and mahinga kai are protectedfrom the adverse effects associated with the discharge of contaminants to air.

cultural amenity values are recognised in regional planning documents, and are protected from activitiesthat result in the discharge of contaminants to air.

An assessment of the provisions was undertaken to determine how well the Air Plan gave effect to the fouroutcomes desired by Ngāi Tahu. This exercise served to demonstrate that the Plan, through a mix of objectivesand central or specific policies, responded to and met each of the desired outcomes.

SUMMARY

The above has introduced the central tenets and some of the principal processes and mechanisms by whichNgāi Tahu came to manage the natural resources of Te Waipounamu. While the nature of this approach isdistinctly Māori, the intent – sustainable management – is clearly shared with wider New Zealand culture andhas been reflected in Part II of the RMA. In order to bring both cultural perspectives together in the overallmanagement of Canterbury’s air resources, this Plan has sought to integrate and weave Ngāi Tahu valuesthroughout. The result will be a region so much richer for its inclusiveness.






3 How the Plan Works

As required by section 67(1) of the Resource Management Act a regional plan must contain:

the objectives for the region

the policies to implement the objectives

the methods to implement the policies.

Otherwise the content of an Air Plan is at the discretion of the responsible regional council.

This Plan commences with three sections containing information intended to assist users of the Plan tounderstand, and apply, the plan provisions. The statutory sections containing the objectives, policies and rulesthen follow. Section 8 contains schedules that provide information and technical details and sections 9 – 13contain maps that support and amplify the rule framework.

Objectives and policies

The objectives in this Plan identify the resource management outcomes or goals for air quality in the CanterburyRegion.

The policies implement the Air Plan’s objectives, as required under section 67(1)(b) of the RMA. The Plancontains central and specific policies. Central policies apply to all activities. These policies provide an overalldirection for the management of air quality in the Region. The specific policies identify the outcomes soughtfrom the management of air quality for particular groups of activities. The policies guide decision-making onresource consent applications, and provide the rationale for the rules and the status which is given to activities.

The objectives and the policies each apply as a comprehensive suite, and must each be read and consideredtogether.

Rules

The rules in the Plan implement the policies, as required under section 67(1)(c) of the RMA. The rules have theforce and effect of regulations in statute, which means they are legally binding.

The rules determine whether a person needs to apply for a resource consent or whether the proposed activitycan be undertaken without one (known as permitted activities). The rules may also make some activitiesprohibited, which means no resource consent application can be made for that activity. An activity needs tocomply with all relevant rules in the Plan in order to be permitted.

The Plan contains general rules that apply anywhere in the Region. It also contains rules which are specific toareas within the Region, or specific to certain discharges of contaminants into air. If the discharge is notcontrolled by a general or specific rule, there will be a ‘catch all’ or ‘default’ rule that will apply, and this willspecify the status of the discharge. In accordance with section 15 of the RMA, the Air Plan has two principlesfor determining whether or not a resource consent is required for a discharge of contaminants into air:

1. A discharge of contaminants into air, which is not from an industrial or trade premise, is permittedunless it contravenes a rule in the Air Plan.

2. A discharge of contaminants into air from an industrial or trade premise is not permitted unlessexpressly allowed by a rule in the Air Plan.

There is an inter-relationship between the status an activity is given in a rule in this Plan, the effects sought tobe managed by the policies, and the environmental outcomes sought to be attained by the objectives. Therules authorise discharges by reference to what the RMA calls “classes of activities”; more simply a consenthierarchy comprises these activities:



Permitted activity: - A resource consent is not required. The discharging activity must, however, complywith the terms and conditions of the applicable rule, it being for the intending discharger to satisfyhimself/herself of this.

Controlled activity: - A resource consent is required, but must be granted if the terms of the rule aremet and subject to any conditions imposed on matters over which control has been reserved.

Restricted discretionary activity: - A resource consent is required, which may or may not be granted.If granted, the consent may include conditions but only related to matters of discretion stated in therule.

Discretionary activity: - As for a restricted discretionary activity, except that conditions are at large(i.e. are not restricted to matters over which discretion has been reserved).

Non-complying activity: - A resource consent is required, and may only be granted if the adverse effectsof the activity are minor or the activity is not contrary to the objectives and policies of the Plan.

Prohibited activity: - A resource consent may neither be applied for, nor granted.

When do Rules Have Legal Effect and Become Operative?

All rules in the Canterbury Air Regional Plan had immediate legal effect under section 86B(3) of the RMA fromthe date of notification (28 February 2015).

This means that from this date account must be taken of the Plan provisions in relation to any relevant resourcemanagement processes. The weight given to the provisions will increase as each step towards the Plan becomingoperative is completed.

The Plan provisions become operative when all submissions on the Plan have been considered or withdrawn,and any appeals against the provisions of the Plan have been determined. At this point the regional councilapproves the Plan and it becomes operative on a date that is to be publicly notified.

Where an activity requires a resource consent as a result of:

a rule in a proposed plan taking legal effect, or

a rule in a plan becoming operative

the activity may continue in the short term if it was previously lawful, the effects of the activity have notmaterially changed and the activity has not been discontinued. However, this description is a paraphrase ofsubsections (1) and (2) of section 20A of the RMA. Anyone who requires a resource consent in either of theabove situations should consult and solely rely on the terms of the section itself.

Resource consents

When applying for resource consent, applicants should refer to Schedule 1 of the Air Plan which sets out theminimum information requirements.



4 Definitions and Interpretation

The definitions are an essential part of the Air Plan, being integral and fundamental to understanding andapplying the Plan provisions. The rules in particular rely upon various definitions that define terms rangingfrom “ambient air” to “ultra-low emitting enclosed burner”, and many other concepts in between. Wheneveran objective, policy or rule uses a term that is defined in this section (except for those definitions taken directlyfrom the RMA), the defined term is shown in italics to alert plan users of the need to consult the definition.

Some of the definitions are taken directly from the RMA or other legislation. Where this is the case the sourceis identified by (RMA), or another relevant abbreviation, appearing in the left hand column underneath thewords comprising the defined term.

The table that follows comprises three parts:

general definitions

small-scale heating appliance definitions

abbreviations.

Table 2.1 General Definitions

DefinitionTerm

means properties which share a boundary with the subject property.Adjoiningproperties

means any substance, whether inorganic or organic, man-made or naturally occurring,modified or in its original state, that is used in any agriculture, horticulture or relatedactivity to eradicate, modify or control flora or fauna. For the purposes of this Plan itincludes agricultural compounds and animal remedies but excludes fertilisers, vertebratetoxic agents and oral nutrition compounds.

Agrichemical

means the air outside buildings and structures. This does not include indoor air, air in theworkplace, or contaminated air discharged from a source.

Ambient air

means those natural and physical qualities and characteristics of an area that contributeto people's appreciation of its pleasantness, aesthetic coherence, and cultural andrecreational attributes.

Amenity values(RMA)

means the best method for preventing or minimising the adverse effects on theenvironment, having regard, among other things, to:

Best practicableoption(RMA)

a. the nature of the discharge or emission and the sensitivity of the receivingenvironment to adverse effects; and

b. the financial implications, and the effects on the environment, of that optioncompared to other options; and

c. the current state of technical knowledge and the likelihood that the option can besuccessfully applied.

means materials consisting of, or including, fragments that could be discharged as dustor particulate. These materials include but are not limited to: gravel, quarried rock,fertiliser, coal, cement, flour, rock aggregate, grains, compost and woodchip.

Bulk solidmaterials

means a designated geographical area identified on the maps in Section 9.Clean Air Zone

means material that, when buried, will have no adverse effects on people or theenvironment. Cleanfill material includes virgin natural materials such as clay, soil androck, and other inert materials such as concrete or brick that are free of:

Cleanfill

a. combustible, putrescible, degradable or leachable components;

b. hazardous substances;



DefinitionTerm

c. products or materials derived from hazardous waste treatment, hazardous wastestabilisation, or hazardous waste disposal practices;

d. materials that may present a risk to human or animal health, such as medical andveterinary waste, asbestos, or radioactive substances; or

e. liquid waste.

means the maximum rated energy output of all large scale fuel burning devices that maybe operated within a property simultaneously at any time, where the rated energy outputfor internal combustion equipment is the useful or delivered energy output at maximumcontinuous rating, often indicated (in kilowatts or megawatts) on the nameplate of a unit.For generators, the kW output is approximately 80% of the kVA rating.

Combined netelectrical outputcapacity

means the maximum rated energy output of all large scale fuel burning devices that maybe operated within a property simultaneously at any time where the rated energy outputfor external combustion equipment is the useful or delivered heat output at maximumcontinuous rating, often indicated (in kilowatts or megawatts) on the nameplate of a unit.

Combined netenergy outputcapacity

means an event held for the benefit of the community or for members or associates of acommunity group or organisation.

Community orcultural event

includes any substance (including gases, odorous compounds, liquids, solids, andmicro-organisms) or energy (excluding noise) or heat, that either by itself or in combinationwith the same, similar, or other substances, energy, or heat:

Contaminant(RMA)

a. when discharged into water, changes or is likely to change the physical, chemical,or biological condition of water; or

b. when discharged onto or into land or into air, changes or is likely to change thephysical, chemical, or biological condition of the land or air onto or into which it isdischarged.

means the standing organic matter left behind after a cultivated crop is harvested. Thisexcludes the residue of woody crops such as plantation forests.

Crop residue

means the use of internal combustion generators to generate electricity at times whennational grid electricity supply is not available due to a failure of either the national gridor the local distribution network.

EmergencyElectricityGeneration

means the keeping of pigs outdoors on land at a stock density which ensures permanentvegetation cover is maintained and in accordance with any relevant industry codes ofpractice, and where no fixed buildings are used for the continuous housing of animals.

Extensive pigfarming

means a substance or biological compound or mix of substances or biological compoundsthat is described as or held out to be for, or suitable for, sustaining or increasing thegrowth, productivity, or quality of plants or, indirectly, animals through the applicationto plants or soil of:

Fertiliser

a. nitrogen, phosphorous, potassium, sulphur, magnesium, calcium, chlorine or sodiumas major nutrients; or

b. manganese, iron, zinc, copper, boron, cobalt, molybdenum, iodine or selenium asminor nutrients; or

c. fertiliser additives; and

includes non-nutrient attributes of materials used in fertiliser, but does not includesubstances that are plant growth regulators that modify the physiological functions ofplants.

means the keeping, rearing or breeding of poultry, whether for the purpose of productionof poultry for human consumption or for the purpose of egg production, where:

Free range poultryfarming

a. all of the birds farmed have access to open air runs; and



DefinitionTerm

b. permanent vegetation ground cover exists on the land where birds are permittedto range; and

c. the stocking rate of the runs and weatherproof shelter to which the birds have accessdoes not exceed the industry standard for the relevant bird type.

means extraction, quarrying, mining, processing, screening, conveying, blasting, orcrushing of any material.

Handling

has the same meaning as that set out in section 2 of the Hazardous Substances and NewOrganisms Act 1996.

Hazardoussubstance

meansIndustrial or tradepremises (RMA) a. any premises used for any industrial or trade purposes; or

b. any premises used for the storage, transfer, treatment, or disposal of waste materialsor for other waste-management purposes, or used for composting organic materials;or

c. any other premises from which a contaminant is discharged in connection with anyindustrial or trade process;

but does not include any production land.

includes every part of a process from the receipt of raw material to the dispatch or usein another process or disposal of any product or waste material, and any interveningstorage of the raw material, partly processed matter, or product.

Industrial or tradeprocess (RMA)

means the keeping, rearing or breeding for any purpose of more than 25 pigs that havebeen weaned, or more than six sows, where the predominant productive processes arecarried out within buildings or closely fenced outdoor runs or where the stocking densityprecludes the permanent maintenance of vegetation cover but excludes extensive pigfarming.

Intensive pigfarming

means the keeping, rearing or breeding of 10,000 or more birds, whether for the purposeof the production of poultry for human consumption or for the purpose of egg production,where the predominant productive processes are carried out primarily within buildings,

Intensive poultryfarming

and includes (but is not limited to) intensive breeder poultry farming, intensive rearerpoultry farming, intensive broiler poultry farming and intensive layer poultry farming, butexcludes free range poultry farming and hatcheries.

means any boiler, furnace, engine or other internal or external combustion device that isdesigned to burn fuel for the primary purpose of energy production and that has a netheat or electrical energy output of 40kW or more but excludes:

Large scale fuelburning device

a. waste incineration devices and crematoria;

b. motor vehicles;

c. boats;

d. aircraft;

e. trains;

f. stationary and mobile engines in a heritage park.

means an effect that is materially harmful to people or the environment.Noxious ordangerous effect

means the burning of materials in the open air, excluding that which occurs within anenclosed device that discharges into air through a flue or chimney.

Outdoor burning

means the use of a large scale fuel burning device to generate electricity for the purposeof supplementing electricity supply at times of peak loading.

Peak electricitynetwork loadmanagement

means a chemical that is produced as a result of refining or physical treatment ofpetroleum, or as a result of a chemical process in which petroleum is a reagent.

Petroleum product



DefinitionTerm

means any contiguous area of land, including land separated by a road or river, held inone or more than one ownership, that is utilised as a single operating unit, and may includeone or more certificates of title.

Property

means those areas to which the public have right of access under any statute, regulation,law or by-law, and are limited to:

Public amenityarea

a. Crown and Local Authority properties, reserves, gardens, and parks;

b. sports grounds;

c. forest and bush areas;

d. pedestrian walkways, malls and precincts;

e. beaches, beach reserves, and adjacent foreshore areas;

but shall exclude roadways.Note: an area where the public is provided access at the discretion of a landowner and/oroccupier is not a public amenity area.

has the same meaning as that set out in the Canterbury Regional Policy Statement.Regionallysignificantinfrastructure

means used oil that has been processed to remove impurities such as particulate, metals,solvents, volatiles, sulphur and chlorine.

Re-refined oil

means an activity undertaken in:Sensitive activity

a. the area within 20m of the façade of an occupied dwelling; or

b. a residential area or zone as defined in a district plan; or

c. a public amenity area, including those parts of any building and associated outdoorareas normally available for use by the general public, excluding any areas used forservices or access areas; or

d. a place, outside of the Coastal Marine Area, of public assembly for recreation,education, worship, culture or deliberation purposes.

means:Site

a. an area of land or volume of space with defined boundaries, whether legally orotherwise described, comprised in a single allotment or any other legally definedparcel of land:

(i) held in a single certificate of title; or

(ii) for which a separate certificate of title could be issued without further consent.

b. in the case of land subdivided under the cross lease or company lease systems, siteshall mean an area of land exclusively restricted to the control of users of that land.

c. in the case of land subdivided under the Unit Titles Act 2010, site shall mean an areaof land or volume of space containing a principal unit or a proposed unit in a unitplan, together with its accessory units.

“Site” also includes the access to the site.

means the date on which a change of ownership of a property from one legal person toanother is registered with Land Information New Zealand or, if the registration of anownership change needs to be lodged with Land Information New Zealand for processing,the date that the dealing is lodged for registration.

Sold

This does not include:

a. a transaction in which a person who was a registered proprietor of the land at thedate of notification of this Plan, remains or becomes a registered proprietor (whetheror not the only registered proprietor) of that property after the transfer;



DefinitionTerm

b. a transaction in which the transferee is a trustee of a trust, and one or more of thetransferors is a beneficiary of that same trust;

c. a transaction which takes place before 1 March 2016.

means any building, equipment, device, or other facility made by people and which isfixed to land; and includes any raft.

Structure (RMA)

means a town or community located in an area of rural character.Township



The following terms are used in the Canterbury Air Regional Plan to describe small-scale heating appliances.

Table 2.2 Small-scale Heating Appliance Definitions

DefinitionDevice type

meansSmall-scale heatingappliance a. an open fire, older-style enclosed burner, low-emitting enclosed burner or ultra-low

emitting enclosed burner; or

b. a stationary petrol, diesel or gas burning device with a net energy output of 40kW or less used for the purpose of heating space, or heating liquid for the purpose of heating space.

means a fire place that is not enclosed and is located inside a building.Open fire

means an enclosed solid fuel burning device that is not a low emitting enclosed burneror an ultra-low emitting enclosed burner.

Older-style enclosedburner

meansLow emittingenclosed burner a. an enclosed solid fuel burning device that has been certified by the CRC in

accordance with Schedule 9 as achieving an emission standard of 1g or less of totalsuspended particulate output per 1kg of fuel burnt and a design standard of 65%efficiency when tested in accordance with Schedule 9; or

b. an enclosed solid fuel burning device that is not an ultra-low emitting enclosedburner and was certified before 28 February 2015 as meeting the standards requiredby rules AQL2 or AQL2A of the Canterbury Natural Resources Regional Plan.

meansUltra-low emittingenclosed burner a. an enclosed solid fuel burning device that has been certified by the CRC in

accordance with Schedule 9 as achieving an emission and efficiency standard of38mg/MJ of useful energy when tested to simulate real life conditions as set outin Schedule 9; or

b. an enclosed solid fuel burning device approved by CRC before 28 February 2015as achieving the following standards:

(i) the emissions result in no more than 0.5 grams of total suspended particulateemissions per kilogram of fuel burned; and

(ii) thermal efficiency of 65% or greater.

means a secondary air emission treatment device that reduces the particulate from asmall-scale heating appliance.

Secondary emissionreduction device



Table 2.3 Abbreviations

DefinitionAbbreviation

Canterbury Regional CouncilCRC

Hectaresha

Kilogramskg

KilowattkW

Litresl

Litres per secondl/s

Metresm

Square metresm2

Cubic metresm3

Cubic metres per daym3/day

Milligrams per cubic metremg/m3

Milligrams per megajoulemg/MJ

Millimetresmm

MegawattMW

Micrograms per cubic metreμg/m3

Resource Management (National Environmental Standards for Air Quality) Regulations2004

NESAQ

Particulate matter less than 10 micrometres in aerodynamic diameterPM10

Particulate matter less than 2.5 micrometres in aerodynamic diameterPM2.5

Resource Management Act 1991RMA

Tonne (metric - 1000kg)t






5 Objectives

5.1 Air quality protects the mauri and life supporting capacity of the environment.

5.2 Ambient air quality provides for the health and wellbeing of the people of Canterbury.

5.3 Competing demands for the use of the air resource of Canterbury are accommodated while unacceptabledegradation of ambient air quality is avoided.

5.4 Degraded ambient air quality is improved over time and where ambient air quality is acceptable it ismaintained.

5.5 Air quality is managed in a way that provides for the cultural values and traditions of Ngāi Tahu.

5.6 Amenity values of the receiving environment are maintained.

5.7 Discharges from new activities are appropriately located to take account of adjacent land uses andsensitive activities.

5.8 Discharges from existing activities are managed in response to evolving characteristics of the receivingenvironment.

5.9 Offensive and objectionable effects and noxious or dangerous effects on the environment are generallyavoided.

5.10 Developments and innovation in technology that have the potential to improve air quality are enabled.






6 Policies

Central policies applying to all activities

6.1 Discharges of contaminants into air, either individually or in combination with other discharges, do notcause:

a. diverse effects on human health and wellbeing; or

b. adverse effects on the mauri and life supporting capacity of ecosystems, plants or animals; or

c. significantly diminished visibility; or

d. significant soiling or corrosion of structures or property.

6.2 Recognise the value of air quality as a taonga to Tangata Whenua and manage adverse effects ofdischarges into air on wāhi tapu, wāhi taonga, and places of significance to Ngāi Tahu.

6.3 Manage the effects of discharges into air on ambient air quality by:

a. the spatial division of the Canterbury Region into areas inside and outside Clean Air Zones;

b. setting a 2ha property area threshold; and

c. setting thresholds for effects above which resource consents are required.

6.4 Reduce adverse effects of discharges on people where ambient air quality does not meet the value setin a national ambient air quality standard or guideline.

6.5 Minimise adverse effects on people where ambient air quality is degraded when assessed against anational ambient air quality standard or guideline.

6.6 Maintain ambient air quality in locations where the quality is acceptable when assessed against anambient air quality standard set in a national ambient air quality standard or guideline.

6.7 In Clean Air Zones, reduce overall concentrations of PM2.5 so that by 2030 those concentrations do notexceed 25μg/m3 (24 hour average) and 10μg/m3 (annual average).

6.8 Offensive and objectionable effects are unacceptable and actively managed by plan provisions and theimplementation of management plans.

6.9 Discharges into air from new activities are appropriately located and adequately separated from sensitiveactivities, taking into account land use anticipated by a proposed or operative district plan and thesensitivity of the receiving environment.

6.10 If the sensitivity of the receiving environment is altered by authorised land use change so that an existingdischarge results in significant adverse effects on the receiving environment, require the effects of thatdischarge to be reduced and provide a reasonable timeframe for achieving that reduction.

6.11 When evaluating resource consent applications recognise locational constraints on activities, whenimposing terms and conditions.

6.12 Where activities locate appropriately to mitigate adverse effects on air quality a longer consent durationmay be available to provide on-going operational certainty.

6.13 Minimise the cumulative effects of discharges of contaminants into air by requiring:

a. permitted discharges to apply good environmental practices; and

b. discharges allowed by a resource consent to apply the best practicable option.



6.14 Recognise the contribution of nationally and regionally significant infrastructure to people’s social andeconomic wellbeing and provide for discharges associated with the development, operation, andmaintenance of that infrastructure.

6.15 Recognise that changes in technology may allow for improvements in the quality of a discharge overthe term of the consent and acknowledge this by imposing management and review conditions on newand replacement resource consents.

6.16 Provide for discharges of contaminants into air necessary for the protection of production species andother biodiversity from biosecurity risks.

6.17 Where a discharge causes effects that are unpredictable because of scientific uncertainty or an absenceof information adopt a precautionary approach to assessing the effects if there is a risk of high probabilityor high potential impact.

Outdoor burning

6.18 Minimise adverse effects of discharges into air from outdoor burning of organic material by establishingstandards for this activity, including when burns are allowed and requirements for the preparation andimplementation of a smoke management plan.

6.19 Avoid outdoor burning of non-organic material (other than incidental amounts) except where the burningis for fire fighting research and training, munitions, ammunition and pyrotechnic disposal or occurs inaccordance with tikanga Māori.

6.20 Minimise adverse effects on townships of discharges into air from outdoor burning of organic material,particularly where Crop Residue Burning Buffer Areas have been identified on the Planning Maps.

6.21 Allow discharges into air from outdoor cooking and outdoor burning of organic material for communityand cultural events.

Industrial and trade activities and large scale fuel burning devices

6.22 Applications for resource consent for discharges of contaminants into air from large scale fuel burningdevices and industrial or trade activities shall identify the best practicable option to be adopted tominimise effects.

6.23 Avoid significant increases in the concentration of PM10 in ambient air within a gazetted airshed byestablishing thresholds and performance standards for the discharge of PM10 within the associated CleanAir Zone.

6.24 Within Clean Air Zones, generally avoid granting resource consents to discharge PM10 whereconcentrations in the discharge exceed 250mg/m3.

6.25 Applications for resource consent for discharges into air from industrial or trade activities or large scalefuel burning devices classified as discretionary shall address:

a. where the discharge includes PM10, the mass emission rate of the proposed discharge relative tothe total emission rate of all discharges within the Clean Air Zone; and the degree to which theproposed discharge exacerbates cumulative effects within the Clean Air Zone; and

b. localised effects of the proposed discharge and the location of sensitive receptors; and

c. available mitigation and emission control options; and

d. the duration of consent being sought and the practicability for the effects of the discharge to bereduced over time.

6.26 When considering applications for resource consent for the discharge of contaminants into air fromlarge scale fuel burning devices or from industrial, trade or commercial activities, the CRC will considerthe combined effect of all consented discharges into air occurring on the property.



6.27 Enable discharges into air from large scale fuel burning devices for the purpose of:

a. emergency electricity generation; or

b. strategic management of electricity supply by network suppliers,

while limiting discharges to the duration of the emergency, supply crisis or excess network loading and givingpreference to the use of generators located outside Clean Air Zones.

6.28 Manage discharges of odour and dust from the storage, transfer, handling, treatment or disposal ofliquid or solid waste, by ensuring that any discharges from those activities are appropriately located.

6.29 The recovery of Lyttelton Port is provided for by expediting activities associated with the repair, rebuildand reconfiguration of the Port, while managing the effects on the environment.

Rural discharges into air

6.30 The discharge of agrichemicals and fertilisers into air is undertaken using best management practicesto minimise the risk of adversely affecting non-target locations.

6.31 Adverse effects of discharges of odour into air from farming activities are managed through performancestandards or conditions on resource consents that ensure the amenity values of the area in which thedischarge occurs are maintained and effects on sensitive activities are minimised.

6.32 Discharges of contaminants into air associated with farming activities do not cause offensive orobjectionable effects beyond the boundary of the property of origin.

Small-scale heating appliances

6.33 Improve air quality where it is degraded and maintain air quality where it is acceptable by managingdischarges from small-scale heating appliances through:

a. establishing plan provisions that stimulate the development of new technology, including thedevelopment of secondary emission reduction devices; and

b. specifying appropriate appliance performance standards and operational requirements; and

c. requiring upgrades in technology in Clean Air Zones within a specified time frame; and

d. establishing limits on visible smoke discharges and specifying fuel standards.

6.34 Enable the use of small-scale heating appliances in particular heritage buildings where those appliancesare integral to the heritage fabric of the building, including by undertaking regular review of Schedule10.

6.35 Enable the use of ultra-low emitting enclosed burners in new situations and as replacements for existingsmall-scale heating appliances.

6.36 According to the maturity of the previous controls in each Clean Air Zone, allow discharges fromlow-emitting enclosed burners in specified circumstances and timeframes.

6.37 Phase out discharges of contaminants into air from the use of open fires on properties less than 2 hectaresin Clean Air Zones.

6.38 Phase out discharges of contaminants into air from the use of older-style enclosed burners in Clean AirZones.






7 Rules

Rule Index

Rule NumberActivity

7.1 – 7.9Rules applying to all activities

7.1Must comply with all applicable rules

7.2Universal matters for control or discretion

7.3 – 7.5Odour, dust and smoke effects

7.6Noxious and dangerous effects

7.7 – 7.9Hazardous air pollutants

7.10 – 7.19Outdoor burning

7.10Burning for fire-fighting training or deflagration

7.11 – 7.13Burning of crop residue

7.14Burning vegetation, paper, cardboard or untreated wood

7.15Burning for community or cultural events

7.16Domestic cooking (including hangis, barbeques and pizza ovens)

7.17Burning for biosecurity reasons

7.18Burning animal carcasses and offal

7.19Other

7.20 – 7.30Large scale fuel burning devices

7.20 – 7.25External combustion

7.26 – 7.30Internal combustion including electricity generation

7.31 – 7.64Industrial, trade or commercial activities

7.31Lyttelton Port Recovery

7.32 – 7.40Dust generating activities

7.32 – 7.34Land development

7.35 – 7.36Bulk solid materials

7.37Seed processing

7.38Wood waste

7.39 – 7.40Abrasive blasting

7.41 – 7.44Surface coating and printing

7.41 – 7.43Spray application of paint

7.44Printing processes

7.45 – 7.51Waste management

7.45 – 7.49Landfills, cleanfills and waste transfer sites

7.50 – 7.52Human effluent treatment and disposal

7.53 – 7.62Other

7.53Petroleum products

7.54 – 7.55Drycleaning and laundries

7.56Metal working

7.57Clay firing

7.58Cooling towers and heat exchangers

7.59Cooking of animal and plant matter

7.60 – 7.62Laboratory fume cupboards, fumigation and ventilation

7.63Activities not otherwise provided for

7.64Activities giving rise to offensive and objectionable effects

7.65 – 7.80Farming

7.65 – 7.72Intensive farming

7.65 -7.66All intensive farming established prior to 1 June 2002

7.67 – 7.68Intensive poultry farming established after 1 June 2002



Rule NumberActivity

7.69Intensive pig farming established after 1 June 2002

7.70 – 7.71Accommodation of cattle

7.72Mushroom farming established after 1 June 2002

7.73 – 7.74Animal effluent and solid animal waste

7.75 – 7.76Offal pits

7.77 – 7.79Agrichemicals and fertilisers

7.80Activities giving rise to offensive and objectionable effects

7.81 – 7.108Small-scale heating appliances

7.81Small-scale heating appliances on industrial or trade premises

7.82 – 7.83Outside Clean Air Zones

7.84 – 7.88Within All Clean Air Zones

7.84General prohibitions

7.85Ultra-low emitting enclosed burners and small-scale heatingappliances burning liquid or gas fuel

7.86 – 7.87Small-scale heating appliances located in heritage buildings

7.88 – 7.89Small-scale heating appliances fitted with secondary emissionreduction devices

7.90 – 7.94Rangiora, Kaiapoi and Ashburton Clean Air Zones

7.95 – 7.99Christchurch Clean Air Zone

7.100 – 7.104Timaru Clean Air Zone

7.105 – 7.108Geraldine and Waimate Clean Air Zones



Rules applying to all activities

Notes and cross-references are included for information purposes only and do not form part of the rules andnor should they be considered a complete list.

7.1 Any activity must comply with all applicable rules in Section 7 of this Plan, except where explicitlystated to the contrary in any other applicable rule in this Plan.

7.2 In considering applications for controlled activities or restricted discretionary activities, thematters on which:

1. control is reserved;

2. or exercise of discretion is restricted;

include the lapsing period, the term of the resource consent, the review of the conditions of aresource consent, the need for a bond or financial contributions, any actual or potential adverseeffects on places of significance to Ngāi Tahu and the collecting, recording, monitoring andprovision of information concerning the exercise of a resource consent. These matters are inaddition to those listed in the applicable rule for the activity.

7.3 The discharge of odour, dust or smoke into air that is not managed by any other rule in this Planis a permitted activity provided the following conditions are met:

1. The discharge does not cause or is not likely to cause an adverse effect beyond the boundary ofthe property of origin; and

2. The discharge does not cause an offensive or objectionable effect beyond the boundary of theproperty of origin when assessed in accordance with Schedule 2.

7.4 The discharge of odour, dust or smoke into air that is not managed by any other rule in this Planand that does not meet condition 1 of Rule 7.3 is a restricted discretionary activity.

The exercise of discretion is restricted to the following matters:

1. The content of the management plan to be implemented; and

2. The frequency of the effects of the discharge; and

3. The intensity of the effects of the discharge; and

4. The duration of the effects of the discharge; and

5. The offensiveness of the discharge; and

6. The location of the effects of the discharge; and

7. The matters set out in Rule 7.2; and

8. Mitigation methods available to minimise any actual or potential environmental effects on theefficacy of the package of conditions.

7.5 The discharge of odour, dust or smoke into air that does not meet condition 2 of Rule 7.3 is anon-complying activity.

7.6 The discharge of any contaminant into air that causes a noxious or dangerous effect and that isnot otherwise classified by a rule in this Plan is a prohibited activity.

7.7 Except where provided for by Rule 7.10, the discharge of contaminants into air from outdoorburning or burning in a small-scale heating appliance of:

a. any quantity of a material listed in Part A below; or

b. a material listed in Part B below, except:

(i) where that material is present in minor quantities and cannot be readily separatedfrom the principal material being burnt; or

(ii) where the burning is on a marae and in accordance with tikanga Māori;



is a prohibited activity.

Part A

1. Wood painted with lead-based paint or treated with CCA timber preservative;

2. Wire that is coated with any material;

3. Materials containing asbestos;

4. All rubber;

5. Medical waste, pathological wastes, quarantine waste;

6. Batteries, chemicals, paint and other surface coating materials;

7. Tar or bitumen;

8. Used and waste oil, excluding re-refined oil;

9. Sludge from industrial processes;

10. Any container that has been used for the purpose of storing hazardous substances.

Part B

1. Wood treated or processed with preservatives (except for wood treated with CCA timberpreservative), gluing agents, or impregnated with chemicals;

2. Wood which is painted, stained or oiled (except for wood painted with lead based paint)

3. Metals and materials containing metals;

4. All plastic;

5. Animal waste;

6. Synthetic material including, but not limited to, motor vehicle parts, foams and fibreglass.

7.8 Except where prohibited under Regulations 7 to 12 of the Resource Management (NationalEnvironmental Standards for Air Quality) Regulations 2004, the discharge of contaminants intoair from burning in a large scale fuel burning device or incinerator or as part of an industrial ortrade process of any material listed in Part A or Part B of Rule 7.7 is a discretionary activity.

7.9 The discharge of contaminants into air from the outdoor burning of any waste materials withina landfill or waste transfer station or waste recovery area, but excluding landfill gas, is a prohibitedactivity.



Outdoor burning

Anywhere in the Region

Note: The relevant district, city or Rural Fire Authority outdoor burning bylaws should be consulted prior toundertaking any outdoor burning.

Burning for fire fighting or deflagration

7.10 The discharge of contaminants into air from:

a. the outdoor burning of buildings or other materials for the purpose of fire-fighting trainingor research; or

b. the burning or deflagration, by the New Zealand Defence Force, of ammunitions, munitionsand pyrotechnics

is a permitted activity provided the following conditions are met:

1. The fire is under the control of the Rural Fire Authority, New Zealand Fire Service, Department ofConservation, New Zealand Defence Force, Christchurch International Airport Fire Service or othernationally recognised body authorised to undertake fire-fighting training or research activities;and

2. The burning does not occur within 100m of any National Grid power line or substation unlesspermission has been obtained from the owner of the infrastructure; and

3. All properties not owned by the relevant organisation identified in Condition 1 above within a 150mradius of the point of discharge are notified in writing at least 7 days prior to the training exercise;and

4. Within a Clean Air Zone, building fires do not occur during the months of April, May, June, July,August and September; and

5. Burning is undertaken in accordance with Regulations 9 and 10 of the Resource Management(National Environmental Standards for Air Quality) Regulations 2004.

Burning of crop residue

7.11 Outside Crop Residue Burning Buffer Areas identified in Section 11 Crop Residue Burning BufferArea Map Series, the discharge of contaminants into air from burning standing crop residue is apermitted activity provided the following conditions are met:

1. The discharge does not cause an offensive or objectionable effect beyond the boundary of theproperty of origin, when assessed in accordance with Schedule 2; and


3. The person responsible for the discharge holds a smoke management plan prepared in accordancewith Schedule 3; and

4. The discharge is managed in accordance with the smoke management plan; and

5. The smoke management plan is supplied to the CRC on request.

7.12 Outside Crop Residue Burning Buffer Areas identified in Section 11 Crop Residue Burning BufferArea Map Series, the discharge of contaminants into air from burning standing crop residue thatdoes not meet condition 1 of Rule 7.11 is a non-complying activity.

7.13 Within Crop Residue Burning Buffer Areas identified in Section 11 Crop Residue Burning BufferArea Map Series, the discharge of contaminants into air from burning standing crop residue is acontrolled activity provided the following condition is met:

1. The burning of standing crop residue is undertaken in accordance with Schedule 3.

The CRC reserves control over the following matters:



1. The management of the effects of the dispersal or deposition of particles beyond the boundary ofthe property of origin; and

2. The contents and application of a smoke management plan; and

3. The management of cumulative effects on the township adjacent to the buffer area; and

4. The actual and potential effects of the discharge on surrounding neighbours including any nationalgrid power line or substation; and

5. The matters set out in rule 7.2.

Burning vegetation, paper, cardboard or untreated wood

7.14 The discharge of contaminants into air from outdoor burning of vegetation (excluding standingcrop residue), paper, cardboard or untreated wood, is a permitted activity provided the followingconditions are met:

1. The discharge is on a property greater than 2ha in area; and

2. The quantity of any liquid fire accelerant used does not exceed 10 litres; and


4. The material to be burnt is located at least 100m upwind and 50m in any other direction of anysensitive activity that is not located on the property where burning occurs unless permission hasbeen obtained from the occupier of the place or area where the sensitive activity is occurring; and

5. The material to be burnt is dry and the moisture content is unlikely to exceed 25% dry weight; and

6. If within 4 km of any township or Clean Air Zone, burning only occurs when the wind direction willcause smoke to disperse away from the township or Clean Air Zone; and

7. Burning is only of material sourced from no more than 2 adjoining properties and burning isundertaken on one of those properties; and

8. If the discharge is likely to continue for 3 days or more, a smoke management plan has beenprepared in accordance with Schedule 3 and the discharge is managed in accordance with thatsmoke management plan; and

9. Any smoke management plan required under condition 8 above is supplied to the CRC on request;and

10. Within a Clean Air Zone, the burning does not take place during May, June, July or August, exceptthat in the Geraldine, Ashburton, Waimate and Rangiora Clean Air Zones, burning may take placein the month of May between the hours of 8am and 4pm.

7.15 The discharge of contaminants into air from outdoor burning of vegetation and untreated woodas a part of a community or cultural event is a permitted activity provided the following conditionsare met:

1. Within a Clean Air Zone, the discharge does not take place during May, June, July or August; and


3. The material to be burnt is dry and the moisture content is unlikely to exceed 25% dry weight.

7.16 The discharge of contaminants into air from outdoor burning for the purpose of cooking, includingin a hangi, barbeque, pizza oven or other small scale or domestic outdoor cooking device, is apermitted activity.

Burning for biosecurity reasons

7.17 The discharge of contaminants into air, from outdoor burning for the purpose of controllingunwanted organisms or disease control and that is undertaken as a requirement of the BiosecurityAct 1993, is a permitted activity.



Burning animal carcasses and offal

7.18 The discharge of contaminants into air from outdoor burning of animal carcasses and offal is apermitted activity provided the following conditions are met:

1. The discharge is on a property greater than 2ha in area; and


3. The discharge does not occur within 100m of a property boundary.

Other

7.19 The discharge of contaminants into air from outdoor burning that does not comply with one ormore of the conditions of Rule 7.11 excluding condition 1, or one or more of the conditions of Rules7.10, 7.13, 7.14, 7.15 or 7.18, is a restricted discretionary activity.


1. Any effect on the environment of not meeting the condition or conditions of the particular rulecontravened; and

2. Whether the conditions of the rule, when considered as a package, remain effective; and




Large scale fuel burning devices

Note; in accordance with Regulation 17 of the Resource Management ( National Environmental Standards forAir Quality) Regulations 2004, the CRC must decline an application for a resource consent for a new or increaseddischarge of PM10 if the discharge to be expressly allowed by the consent would be likely, at any time, to increasethe concentration of PM10 ( calculated as a 24-hour mean under Schedule 1 of the Resource Management(National Environmental Standards for Air Quality) Regulations 2004 by more than 2.5 micrograms per cubicmeter(µg/m3) in any part of a polluted airshed (see gazetted airsheds shown in the maps in Section 10) otherthan the site on which the consent would be exercised.

External combustion

7.20 The discharge of contaminants into air from the external combustion of fuel in any large scalefuel burning device is a permitted activity provided the following conditions, where applicable,are met:

All devices

1. The discharge is directed vertically into air and is not impeded by any obstruction above theemission stack which decreases the vertical efflux velocity below that which would occur in theabsence of such obstruction; and

2. Except for a period not exceeding two minutes in each hour of operation, the opacity of thedischarge is not darker than Ringelmann Shade No. 1, as described in Schedule 6; and

3. The emissions are discharged through an emission stack which meets the requirements set outin Schedule 5; and

4. The fuel burning equipment is maintained in accordance with the manufacturer’s specificationsat least once every year by a person competent in the maintenance of that equipment, a copy ofeach maintenance report is held for three years and made available to the CRC on request, andthe annual maintenance includes adjustment, as required, of the fuel to air mix and testing of theratio of combustion gases discharged to optimise efficiency; and

Gas fired

5. Where the discharge is from the combustion of liquefied petroleum gas or compressed naturalgas, the combined net energy output capacity of all gas-fired devices is less than or equal to 5MW;

Diesel fired

6. Where the discharge is from the combustion of diesel:

(a) the sulphur content of the fuel to be burnt does not exceed 0.001% by weight; and

(b) the combined net energy output capacity of all diesel-fired devices is less than or equal to:

(i) 500kW within a Clean Air Zone; or

(ii) 2MW outside a Clean Air Zone;

Solid fuel fired

7. Where the discharge is from the combustion of solid fuel:

(a) the combined net energy output capacity is less than or equal to 1MW; and

(b) if the discharge is within a Clean Air Zone, it replaces a discharge from an existing large scalefuel burning device (or devices) of the same or greater net energy output capacity, burningsolid fuel, that was legally established and operating up to the time of replacement; and

(c) the fuel to be burnt meets the following specifications prior to combustion:

(i) for wood pellet fuel: the specifications set out in AS/NZS 4014:6:2007, except thatpellets made from wood sawdust or wood shavings may contain incidental amountsof antisapstain chemicals; or

(ii) for wood chip fuel: the wood chips do not contain any treatment chemicals, and themoisture content is less than 25% dry weight; and



(d) the sulphur content of the fuel to be burnt does not exceed 1% by weight; and

(e) the concentration of PM10 in the combustion gas discharged from the emission stack(s) doesnot exceed 125mg/m3 when tested in accordance with Schedule 7 and adjusted to 0˚Celsius,dry gas basis, 101.3 kilopascals, and 8% oxygen or 12% carbon dioxide.

7.21 The discharge of contaminants into air from the external combustion of fuel in any largescale fuel burning device,that does not comply with condition 3 of Rule 7.20 is a restricteddiscretionary activity.


1. Methods to mitigate or remedy localised adverse effects on air quality of the discharge ofcontaminants into air; and

2. The emission rate of contaminants; and

3. The opacity of the discharge; and

4. The extent to which the best practicable option is adopted to prevent or minimise adverse effectson air quality; and

5. Measures to disperse contaminants, including emission stack height, emission stack design andemission velocity; and

6. Maintenance of the fuel-burning equipment; and





7.22 Outside a Clean Air Zone, the discharge of contaminants into air from the external combustionof solid fuel in any large scale fuel burning device that does not meet one or more of conditions7(c), 7(d) or 7(e) of Rule 7.20, is a restricted discretionary activity.


1. Methods to mitigate or remedy localised adverse effects on air quality of the discharge ofcontaminants into air; and


3. The opacity of the discharge; and

4. The extent to which the best practicable option is adopted to prevent or minimise adverse effectson air quality; and

5. Measures to disperse contaminants, including emission stack height, emission stack design andemission velocity; and

6. Maintenance of the fuel-burning equipment; and





7.23 Within a Clean Air Zone, the discharge of contaminants into air from the external combustion ofsolid fuel in any large scale fuel burning device that does not meet condition 7 of Rule 7.20 is adiscretionary activity provided the following condition is met:



1. The concentration of filterable PM10 in combustion gas discharged from the emission stack(s) doesnot exceed 250mg/m3 when tested in accordance with Schedule 7 and adjusted to 0° Celsius, drygas basis, 101.3 kilopascals, and 8% oxygen or 12% carbon dioxide.

7.24 The discharge of contaminants into air from the external combustion of fuel in any large scalefuel burning device that does not meet one or more of conditions 1, 2, 4, 5 or 6 of Rule 7.20, orthe discharge of contaminants from the burning of solid fuel outside a Clean Air Zone that doesnot meet condition 7(a) of Rule 7.20, is a discretionary activity.

7.25 Within a Clean Air Zone, the discharge of contaminants into air from the external combustion ofsolid fuel in any large scale fuel burning device that does meet condition 1 of Rule 7.23 is anon-complying activity.

Internal combustion including electricity generation

7.26 The discharge of contaminants into air from the internal combustion of diesel, petrol, liquefiedpetroleum gas or compressed natural gas in any moveable large scale fuel burning device with acombined net electrical output capacity of up to 500kW is a permitted activity, provided thefollowing conditions are met:

1. The discharge occurs for no more than 48 hours if within 50m of a sensitive activity; and

2. The discharge occurs for no more than 5 days if at least 50m from a sensitive activity; and

3. The sulphur content of the fuel burnt does not exceed 0.005% by weight; and

4. Except for a period not exceeding two minutes in each hour of operation, the opacity of thedischarge is not darker than Ringelmann Shade No. 1, as described in Schedule 6.

7.27 The discharge of contaminants into air from the internal combustion of diesel, petrol, liquefiedpetroleum gas or compressed natural gas in any moveable large scale fuel burning device witha combined net electrical output capacity not greater than 500kW, and that is for the purposeof emergency electricity generation by a network lines operator is a permitted activity, providedthe following conditions are met:


2. Except for a period not exceeding two minutes in each hour of operation, the opacity of thedischarge is not darker than Ringelmann Shade No. 1, as described in Schedule 6.

7.28 The discharge of contaminants into air from the internal combustion of diesel, petrol, liquefiedpetroleum gas or compressed natural gas in any stationary large scale fuel burning devicewitha combined net electrical output capacity not greater than 300kW and that is for the purposeof emergency electricity generation, maintenance and peak electricity network load management,is a permitted activity provided the following conditions are met:

1. Emergency electricity generation occurs on the same property as it is used and the electricity isnot distributed to any external network electricity grid; and

2. If the discharge occurs more than 50m from a sensitive activity, it is through an emission stackwith a height of at least 3m above ground level; and

3. If the discharge occurs within 50m of a sensitive activity, it is through an emission stack with aheight of at least 3m above ground level, and above the roof of any building,land or other structurewithin 15m of the stack, unless the building, land or structure is on a different property to the stackand was not established nor had building consent or resource consent granted at the time thestack was established; and



6. The discharge can occur for maintenance and peak electricity network load management for atotal of 500 hours per calendar year; and



7. Within the 500 hours per calendar year set out in condition 6 above, no more than 300 hours percalendar year can be for the purpose of peak electricity network load management; and


9. The fuel burning equipment is maintained in accordance with the manufacturer’s specificationsat least once every year by a person competent in the maintenance of that equipment and a copyof each maintenance report is held for three years and made available to the CRC on request.

7.29 The discharge of contaminants into air from the internal combustion of diesel, petrol, liquefiedpetroleum gas or compressed natural gas in any stationary large scale fuel burning devicewitha combined net electrical output capacity of:

a. 301kW to 1MW within a Clean Air Zone; or

b. 301kW to 2MW outside a Clean Air Zone

and that is for the purpose of emergency electricity generation, maintenance and peak electricitynetwork load management, is a controlled activity provided the following conditions are met:

1. Emergency electricity generation occurs on the same property as it is used and the electricity isnot distributed to any external network electricity grid; and

2. The discharge is from an emission stack with a height of at least 7m above ground level, and 3mabove the roof of any building, land or structure within 15m of the stack, unless the building orstructure is on a different property to the stack and was not established nor had building consentor resource consent granted at the time the stack was established; and



5. The discharge can occur for maintenance and peak electricity network load management for atotal of 500 hours per calendar year; and

6. Within the 500 hours per calendar year set out above, no more than 300 hours per calendar yearcan be for the purpose of peak electricity network load management; and


8. The fuel burning equipment is maintained in accordance with the manufacturer’s specificationsat least once every year by a person competent in the maintenance of that equipment and a copyof each maintenance report is held for three years and made available to the CRC on request.


1. Any measures necessary to prevent or minimise adverse effects on air quality; and


3. The ability of the equipment to disperse contaminants, including emission stack height and design,and emission velocity; and

4. Maintenance of the internal combustion equipment; and

5. The matters set out in Rule 7.2.

7.30 The discharge of contaminants into air from the internal combustion of fuel in any large scalefuel burning device that does not comply with one or more of the conditions of Rules 7.26 to 7.29,or that is not otherwise managed by a rule in this Plan, is a discretionary activity.



Industrial, trade or commercial activities

Lyttelton Port Recovery

7.31 The discharge of contaminants into air, beyond the boundary of the property of origin, resultingfrom the handling or storage of bulk solid materials or from unsealed or unconsolidated surfacesassociated with the rebuild, repair or reconfiguration of the Lyttelton Port within the Port LandUse Area shown on Canterbury Air Regional Plan Map Port of Lyttelton Land Use Area (Map 13.2)in section 13, that is not otherwise permitted by Rule 7.35 or Rule 7.36 is a controlled activity.


1. The contents of a dust management plan prepared in accordance with Schedule 2, which shallform part of the site-wide Construction and Environmental Management Plan; and


Dust generating activities

7.32 The discharge of dust to air beyond the boundary of the property of origin from the constructionof buildings, land development activities, unsealed surfaces or unconsolidated land, is a permittedactivity provided the following conditions, where applicable, are met:

1. The building to be constructed is less than 3 stories in height, or where the building is greater than3 stories in height, a dust management plan is prepared in accordance with Schedule 2 andimplemented by the person responsible for the discharge into air; and

2. The area of unsealed surface or unconsolidated land is less than 1000m2, or where the area ofunsealed surface or unconsolidated land is greater than 1000m2 a dust management plan isprepared in accordance with Schedule 2 and implemented by the person responsible for thedischarge into air; and

3. The discharge does not cause an offensive or objectionable effect beyond the boundary of theproperty of origin, when assessed in accordance with Schedule 2.

7.33 The discharge of dust, beyond the boundary of the property of origin, from the construction ofbuildings, land development activities, unsealed surfaces or unconsolidated land that does notmeet condition 1 or 2 of Rule 7.32 is a restricted discretionary activity.


1. The content of the management plan to be implemented; and

2. The frequency of the effects of the discharge; and

3. The intensity of the effects of the discharge; and

4. The duration of the effects of the discharge; and

5. The offensiveness of the discharge; and

6. The location of the effects of the discharge; and





7.34 The discharge of dust into air beyond the boundary of the property of origin, from the constructionof buildings, land development activities, unsealed land or unconsolidated surfaces that doesnot meet condition 3 of Rule 7.32 is a non-complying activity.



7.35 The discharge of contaminants into air from the handling of bulk solid materials is a permittedactivity provided the following conditions are met:

1. The discharge of dust does not cause an offensive or objectionable effect beyond the boundaryof theproperty of origin, when assessed in accordance with Schedule 2; and

2. The handling occurs indoors, or where the handling occurs outdoors therate of handling doesnot exceed 100t per hour; or

3. Where handling occurs outdoors on less than 21 days per calendar year, the rate of handling doesnot exceed 250t per hour; and

4. Where the handling occurs outdoors and the rate of handling exceeds 20t per hour, a dustmanagement plan is prepared in accordance with Schedule 2 and implemented by the personresponsible for the discharge into air; and

5. The dust management plan is supplied to the CRC on request; and

6. The discharge does not occur within 200m of a sensitive activity, wāhi tapu, wāhi taonga or placeof significance to Ngāi Tahu that is identified in an Iwi Management Plan; and

7. Notwithstanding condition 6, where the discharge is from production blasting at a quarry site thedischarge does not occur within 500m of a sensitive activity wāhi tapu, wāhi taonga or a place ofsignificance to Ngāi Tahu that is identified in an Iwi Management Plan.

7.36 The discharge of contaminants into air from the outdoor storage of bulk solid materials is apermitted activity provided the following conditions are met:

1. The discharge of dust does not cause an offensive or objectionable effect beyond the boundaryof the property of origin, when assessed in accordance with Schedule 2; and

2. The amount of material stored does not exceed 1000t when it has an average particle size of lessthan 3.5mm; and

3. Where the storage exceeds 200t, a dust management plan is prepared in accordance with Schedule2 and implemented by the person responsible for the discharge into air; and


5. The discharge does not occur within 100m of a sensitive activity, wāhi tapu, wāhi taonga or placeof significance to Ngāi Tahu that is identified in an Iwi Management Plan.

7.37 The discharge of contaminants into air from the cleaning, conveying, packaging, processing,handling, treatment or storage of seeds, is a permitted activity provided the following conditionsare met:


2. If there is a discharge of dust beyond the boundary of the property of origin, a dust managementplan is prepared in accordance with Schedule 2 and implemented by the person responsible forthe discharge into air; and


4. Surfaces on the property where the discharge originates, including buildings, plant/equipmentand ground surfaces, are cleaned as regularly as necessary to prevent wind-blown dispersal ordeposition of particles beyond the boundary of the property of origin.

7.38 The discharge of contaminants into air from the generation, conveyance, collection, storage orfiltration of wood waste, is a permitted activity provided the following conditions are met:






4. The storage of wood shavings and sawdust is in a covered hopper or container; and

5. Surfaces where wood waste may accumulate are cleaned at a frequency that prevents wind-blowndispersal or deposition of wood particles beyond the boundary of the property where the dischargeoriginates.

7.39 The discharge of contaminants into air from dry or wet abrasive blasting in an enclosed booth isa permitted activity provided the following conditions are met:

1. The enclosed booth is fitted with an air extraction system that discharges all contaminants andexhaust air to an emission stack or vent; and

2. The discharge from the extraction system is at least 50m from any sensitive activity; and

3. The free silica content of a representative sample of the blast material is less than 5% by weight;and

4. The discharge is via a filtered extraction system that removes at least 95% of particulate matterfrom the discharge and the filtration system is maintained to ensure that this particulate removalefficiency is achieved at all times; and

5. There is no blasting of lead-based paints.

7.40 The discharge of contaminants into air from temporary dry or wet abrasive blasting is a permittedactivity provided the following conditions are met:


2. The discharge into air is only from the operation of a mobile abrasive blasting unit used at any oneproperty for no more than 10 days in any 12 month period; and

3. Abrasive blasting is only undertaken when it is impracticable or unreasonable to remove ordismantle or transport a fixed object or structure to be cleaned in an abrasive blasting booth; and

4. The maximum quantity of dry abrasive blast media used does not exceed 60kg per hour; and

5. The free silica content of a representative sample of the blast material is less than 5% by weight;and

6. There is no blasting of lead-based paints; and

7. The discharge of particulate matter is contained within the immediate area of the abrasive blastingso that particulate does not escape into the environment; and



10. The abrasive blasting unit discharge is only from:

(a) dry abrasive blasting using: garnet; sodium bicarbonate; aluminium oxide; crushed glass;or agricultural sourced media such as crushed corn cobs, walnuts; or

(b) wet abrasive blasting using only water; and

11. Where the discharge occurs in relation to maintenance of the National Grid, the activity isundertaken in accordance with Regulation 25 of the National Environmental Standard for ElectricityTransmission Activities 2009.

Surface coating and printing

7.41 Except as provided for by Rule 7.42, the discharge of contaminants into air from spray applicationof paint, dye or adhesive coating materials outside a spray booth is a permitted activity providedthe following conditions are met:




2. Where the discharge occurs within 100m of a sensitive activity, the rate of spray application doesnot exceed:

(a) 0.5l per hour and 5l per month of solvent based coating material; or

(b) 2.5l per hour and 25l per month of water based coating material containing less than 5%organic solvents by weight; and

3. Where the discharge occurs greater than 100m from a sensitive activity, the rate of spray applicationdoes not exceed:

(a) 2l per hour and 20l per month of solvent based coating material; or

(b) 10l per hour and 100l per month of water based coating material containing less than 5%organic solvents by weight; and

4. The coating material does not contain di-isocyanates or organic plasticisers; and

5. The discharge occurs greater than 10m from any sensitive activity beyond the boundary of theproperty of origin.

7.42 The discharge of contaminants into air from spray application of paint, dye or adhesive coatingmaterials to surfaces of fixed structures that cannot practicably be dismantled and transportedto a spray booth is a permitted activity provided the following conditions are met:

1. The coating material does not contain di-isocyanates or organic plasticisers; and

2. The discharge occurs at least 10m from any sensitive activity beyond the boundary of the propertyof origin.

7.43 The discharge of contaminants into air from the spray application and baking of liquid paint, dyeor adhesive coating materials in a spray booth is a permitted activity provided the followingconditions are met:

1. The discharge does not cause an offensive or objectionable effect beyond the boundary of theproperty of origin when assessed in accordance with Schedule 2; and

2. The rate of spray application does not exceed:

(a) 2l per hour, 10l per day and 100l per month of solvent based coating material; or

(b) 10l per hour, 50l per day and 500l per month of water based coating material containingless than 5% organic solvents by weight; and

3. Contaminants and exhaust air are discharged via an air extraction and filtration system to anemission stack; and

4. The filtration system removes at least 95% of particulate matter from the discharge and thefiltration system is maintained to ensure that this particulate removal efficiency is achieved at alltimes; and

5. The emission stack(s) from both spraying and baking are of a height of at least 3m above the roofof any building, land or other substantial structure within a radius of 35m from the stack, unlessthe building, land or other structure is on a different property to the stack and was not establishedor anticipated at the time the stack was established; and

6. The discharge is directed vertically into the air and is not impeded by any obstruction above thestack which decreases the vertical efflux velocity below that which would occur in the absence ofsuch obstruction; and

7. A record is kept of the type and quantity of liquid paint, dye and coating material used each monthand this record will be held for 3 years and provided to the CRC on request.

7.44 The discharge of contaminants into air from printing processes using only water based inks, dyesand additives, is a permitted activity provided the following conditions are met:

1. The discharge of odour does not cause an offensive or objectionable effect beyond the boundaryof the property of origin when assessed in accordance with Schedule 2; and



2. The undiluted water based inks, dyes and additives used contain less than 5% volatile organiccompounds by weight; and

3. The total quantity of hydrocarbon solvents discharged does not exceed the 5kg per day or 50kgper month, calculated from the maximum quantities stated in the material safety data sheets forthe inks used; and

4. The discharge will not cause corrosion or soiling of structures or property beyond the boundaryof the property of origin; and

5. A record is kept of the quantity and type of printing ink or dye used each month and the recordand material safety data sheets for all printing inks and dyes used are to be held for 3 years andprovided to the CRC on request.

Waste management and disposal

7.45 Within the Burwood Landfill Specific Purpose Site as shown on Map 13.1 in section 13, and exceptwhere otherwise permitted, the discharge of contaminants into air from the handling and disposalof earthquake waste, liquefaction silt or infrastructure waste, and earthworks associated withlandfill construction and rehabilitation, is a controlled activity provided the following conditionsare met:

1. The discharge is not noxious or dangerous beyond the boundary of the Burwood Landfill SpecificPurpose Site; and

2. The application for resource consent includes written comments on the proposal from: Te Rūnangao Ngāi Tahu or any papatipu rūnanga identified by Te Rūnanga o Ngāi Tahu: the Canterbury DistrictHealth Board; the Burwood-Pegasus Community Board; the Parklands Residents’ AssociationIncorporated; the Queenspark Residents’ Association; and the owners and occupiers of landadjacent to Burwood Landfill Specific Purpose Site as shown on Map 13.1 in section 13; and whereno written comments are included in the application, it is demonstrated that 10 working days wasprovided to parties to make written comments.


1. The content of a dust and odour management plan prepared in accordance with Schedule 2; and

2. The extent to which matters raised in consultation are remedied or mitigated, including theproposed methods of remediation or mitigation and any effects of those proposed methods; and

3. The extent to which actual or potential adverse effects on air quality are to be mitigated, theproposed methods of mitigation, and any effects of those proposed methods; and

4. The matters set out in Rule 7.2

Notification: Pursuant to sections 95A and 95B of the RMA, an application for resource consent underthis rule will be processed and considered without public or limited notification. Note that limitednotification to affected order holders in terms of section 95F of the RMA will be necessary, where relevant,under section 95B(3) of the RMA.

7.46 Within the Burwood Landfill Specific Purpose Site as shown on Map 13.1 in section 13, and exceptwhere otherwise permitted, the discharge of contaminants into air from the handling and disposalof earthquake waste, liquefaction silt or infrastructure waste, and earthworks associated withlandfill construction and rehabilitation, that does not meet one or more of the conditions of Rule7.45 is a discretionary activity.

7.47 The discharge of contaminants into air from the storage, transfer,handling, treatment or disposalof waste, that was established on or before 1 June 2002, and where the CRC did not require aresource consent for the discharge of contaminants into air from that activity on or before 1 June2002, is a permitted activity provided the following conditions are met:




2. The discharge is not from the treatment or discharge of hazardous substances; and

3. There is no increase in the scale, intensity, frequency or duration of the effects of the dischargeof contaminants into air from the activity.

7.48 The discharge of contaminants into air from waste transfer sites is a permitted activity providedthe following conditions are met:


2. The discharge does not occur within 50m of a sensitive activity on another property; and

3. The discharge is only from the handling of non-hazardous municipal solid waste, green waste, orcleanfill; and

4. If there is a discharge of odour or dust beyond the boundary of the property of origin, an odourand/or dust management plan is prepared in accordance with Schedule 2 and implemented bythe person responsible for the discharge into air; and

5. The odour and/or dust management plan is supplied to the CRC on request; and

6. The quantity of solid waste on the property does not exceed 10t per day averaged over a calendarmonth.

7.49 The discharge of contaminants into air from the disposal of cleanfill is a permitted activityprovided the following conditions are met:

1. The discharge of dust does not cause an offensive or objectionable effect beyond the boundaryof the property of origin when assessed in accordance with Schedule 2; and

2. The discharge does not occur within 200m of a sensitive activity on another property, orwithin100m of a wāhi tapu, wāhi taonga or place of significance to Ngāi Tahu that is identified in an IwiManagement Plan; and

3. The amount of material stored does not exceed 1000t when it has an average particle size of lessthan 3.5mm; and


5. The dust management plan is supplied to the CRC on request.

7.50 The discharge of contaminants into air from the treatment and disposal of less than 50m3 per dayof human sewage effluent averaged over a calendar month is a permitted activity provided thefollowing conditions are met:

1. The discharge of odour does not cause an offensive or objectionable effect beyond the boundaryof the property of origin, when assessed in accordance with Schedule 2; and

2. If there is a discharge of odour beyond the boundary of the property of origin, an odour managementplan is prepared in accordance with Schedule 2 and implemented by the person responsible forthe discharge into air; and

3. The odour management plan is supplied to the CRC on request; and

4. Except where the discharge is from a single dwelling or other source discharging less than 2m3

per day averaged over a calendar month, the treatment system and any surface irrigation ofeffluent is at least 20m from the boundary of the property of origin; and

5. There is no uncovered storage of screened solids or uncovered drying and storage of sludge; and

6. Spray irrigation, and storage of effluent in uncovered vessels, including oxidation ponds, occursat least 50m from the boundary of the property of origin and at least 150m from any sensitiveactivity or wāhi tapu, wāhi taonga or place of significance to Ngāi Tahu that is identified in an IwiManagement Plan.



7.51 The discharge of contaminants into air from reticulated sewerage networks is a permitted activityprovided the following conditions are met:


2. Where the discharge is from an air pressure release valve, it does not occur within 100m of aresidential property or site intended for residential use, unless it is fitted with an odour mitigationdevice that prevents odour effects occurring within any residential property.

7.52 The discharge of contaminants into air from reticulated sewerage networks that does not complywith condition 2 of Rule 7.51, is a restricted discretionary activity.


1. The remedy or mitigation of the effects of odour within any property where there is a sensitiveactivity; and





Other

7.53 The discharge of contaminants into air, including vapour ventilation and displacement, from thestorage or transfer of petroleum products (including liquefied petroleum gas), is a permittedactivity provided the following conditions are met:

1. The total volume of petroleum product stored on the site is less than 1,000l; or

2. The total volume of petroleum product stored on the site is 1,000l or more, and if there is adischarge of odour or dust beyond the boundary of the property of origin, an odour managementplan is prepared in accordance with Schedule 2, implemented by the persons responsible for thedischarge into air, and supplied to the CRC on request.

7.54 The discharge of contaminants into air from dry cleaning units recovering hydrocarbon solventsemitted from fabric washing and drying processes is a permitted activity provided the followingconditions are met:

1. The discharge does not contain chlorofluorocarbons; and

2. The total mass of hydrocarbons discharged does not exceed 5kg per day or 50kg per month; and

3. A record is kept of the type and quantity of hydrocarbon cleaning solvents used each month, andthe quality of solvents recovered each month and this record shall be held for 3 years and providedto the CRC on request.

7.55 The discharge of contaminants into air from a forced extraction vent used by a laundry servingan institution, commercial, industrial or trade premise is a permitted activity provided thefollowing conditions are met:


2. Where the discharge is from a laundry that uses ozone, the discharge does not occur within 50mof a sensitive activity on a different property.

7.56 The discharge of contaminants into air from mechanical grinding, cutting and shaping byapplication of heat, machining, welding, soldering or arc air gouging of metals is a permittedactivity provided the following conditions are met:



1. All discharges via forced extraction to a vent or emission stack are managed so that there is novisible discharge of contaminants into air; and

2. Where the discharge is within 50m of a sensitive activity and occurs via forced extraction thedischarge is filtered to remove at least 95% of particulate matter; and

3. The activity is either:

(a) undertaken in the open air, where the discharge is at least 20m from the site boundary and50m from any sensitive activity beyond the boundary of the property of origin; or

(b) undertaken inside an enclosed building; or

(c) associated with the installation, repair, or construction of a structure which is fixed to theproperty on which the activity occurs or is a part of that structure.

7.57 The discharge of contaminants into air from the production of less than 50kg dry weight per dayof clay materials or glazing materials by firing in kilns heated by electricity or combustion ofnatural gas or liquid petroleum gas, is a permitted activity.

7.58 The discharge of heat, steam or water vapour into air from cooling towers or air-cooled heatexchangers, is a permitted activity provided the following condition is met:

1. Cooling towers and heat exchangers are maintained as often as necessary to minimise the dischargeof contaminants into air.

7.59 The discharge of contaminants into air from cooking or processing by application of heat, steamor smoke of up to 10t of animal or plant matter per day is a permitted activity provided thefollowing conditions are met:


2. If there is a discharge of odour or dust beyond the boundary of the property of origin from thecooking or processing by application of heat, steam or smoke of between 1t and 10t of animal orplant matter per day, an odour and/or dust management plan is prepared in accordance withSchedule 2 and implemented by the person responsible for the discharge into air; and

3. The odour and/or dust management plan is supplied to the CRC on request; and

4. The discharge is not from:

(a) extraction, distillation or purification of animal fats, other than as a process incidental tothe cooking of food; or

(b) rendering and reduction of animal matter by application of heat; or

(c) the processing of skins, including fellmongery and tanning; or

(d) the roasting of more than 200kg of coffee beans per day.

7.60 The discharge of contaminants into air from laboratory fume cupboards is a permitted activityprovided the following conditions are met:

1. The discharge does not cause corrosion of any structure beyond the boundary of the property oforigin; and

2. The emission stack complies with AS/NZS 2243.8:2014 Safety in Laboratories - Fume Cupboards.

7.61 The discharge of contaminants into air during fumigation is a permitted activity provided thefollowing condition is met:

1. The discharge does not include ethylene dibromide, ethylene oxide, methyl bromide, hydrogencyanide, phosphine or chloropicrin.

7.62 The discharge of contaminants into air from the ventilation of buildings located on industrial ortrade premises, where that discharge is not via forced extraction to an emission stack or treatmentsystem, is a permitted activity provided the following conditions are met:




2. At the point that the discharge exits the building, the concentration of any contaminant does notexceed the relevant Workplace Exposure Standard; and

3. If there is a discharge of odour or dust beyond the boundary of the property of origin, an odourand/or dust management plan is prepared in accordance with Schedule 2 and implemented bythe person responsible for the discharge into air; and

4. The odour and/or dust management plan is supplied to the CRC on request.

Activities not otherwise provided for

7.63 The discharge of contaminants into air:

1. that does not comply with one or more of the conditions of Rules 7.47 to 7.62, excludingcondition 1 of Rules 7.47, 7.48, 7.49, 7.50 7.51, 7.55, 7.59 and 7.62; or

2. that is from an industrial or trade premise and is not managed by Rules 7.47 -7.62;

and is not a prohibited activity, is a discretionary activity.

7.64 The discharge of contaminants into air that does not comply with condition 1 of Rules 7.47, 7.48,7.49, 7.50 7.51, 7.55, 7.59 and 7.62 is a non-complying activity.

Note: Those discharges into air likely to require resource consent under Rule 7.63 include, but are notlimited to, the following activities:

Printing processes usingsolvent-based inks (> 5% organicsolvent content by weight)

Glass manufactureHydrocarbon manufacture, refining orpurification

Some abrasive blastingoutsideAcid production and use

Radioactive materials production orusage (excluding use for medicalpurposes)

Ink and dye manufactureIsocyanate-containing materials –production and use (excluding spray coatingprocesses in booth using < 2 l/hr)

Adhesives manufactureAgricultural chemicalmanufactureAnodising, galvanising andelectroplating

Rendering of animal matter byapplication of heatLaminating using adhesives and resins

Asphalt productionBrewing of alcoholicbeverages

Resins, lacquers and plasticsmanufactureRubber manufacture

Metal melting, including foundries andsmelters, but excluding welding andsoldering

Brickworks Soap and detergent manufactureMilk treatment and dryingCement manufactureComposting

Spray painting in a booth, using > 2l/hr Spray painting in the open usingisocyanate-based coatings

Oil refiningOil well flaringPaint manufactureCremation

Stock food productionPaper manufactureEnamellingStripping by immersion usinghydrocarbon solvents

Particle board and plasterboard productionPharmaceutical product manufacture

FellmongeryFertiliser manufactureFibreglass application Tanning of hidesPowder coating processes (excluding filtered

discharge to internal workplace airaccording to OSH requirements)

Foam manufacture Timber drying kilnsTyre buffingWool scouring and dag crushing

The above list is not all-inclusive. It is likely that there will be other discharges into air from industrial or tradepremises, not listed, that require resource consent under this rule.



Farming

Intensive farming

7.65 The discharge of contaminants into air from intensive poultry farming, intensive pig farming ormushroom farming that was established at a permanent location on or before 1 June 2002, andwhere the CRC did not require a resource consent for the discharge of contaminants into air fromthat activity on or before 1 June 2002, is a permitted activity provided the following conditionsare met:


2. From 1 June 2002 there has been no increase in the scale of the farming activity.

7.66 The discharge of contaminants into air from intensive poultry farming, intensive pig farming ormushroom farming, established prior to 1 June 2002 and that does not comply with condition 1of Rule 7.65 is a restricted discretionary activity.


1. The quantity, quality and type of the discharge into air and any effects arising from that discharge,including cumulative effects; and

2. The methods to control the discharge and avoid, remedy or mitigate any adverse effects, includingthe odour and/or dust management plan; and

3. The location of the discharge, including proximity to sensitive activities; and

4. The efficient use and development of the physical resources of the existing farm; and





7.67 The discharge of contaminants into air from intensive poultry farming, established on or after 1June 2002 where the discharge is located at least 200m from a sensitive activity is a restricteddiscretionary activity provided the following condition is met:

1. The discharge of odour does not cause an offensive or objectionable effect beyond the boundaryof the property of origin, when assessed in accordance with Schedule 2.


1. The quantity, quality and type of discharge and any effects arising from that discharge, includingcumulative effects; and


3. The location of the discharge, including proximity to sensitive activities, wāhi tapu, wāhi taongaor places of significance to Ngāi Tahu; and







7.68 The discharge of contaminants into air from intensive poultry farming established on or after 1June 2002 where the discharged is located less than 200m from a sensitive activity is adiscretionary activity provided the following condition is met:


7.69 The discharge of contaminants into air from intensive pig farming established on or after 1 June2002, is a restricted discretionary activity provided the following condition is met:










7.70 The discharge of contaminants into air from the accommodation of more than 30 cattle (excludingcalves) in a barn or other roofed structure, whether enclosed or not, is a permitted activityprovided the following conditions are met:


2. The discharge is located:

(a) at least 200m from the property boundary; and

(b) 500m from a sensitive activity on another property; and

(c) 1000m from any land zoned for urban residential use at the date the discharge commenced;or

3. Where the discharge does not comply with condition 2:

(a) the discharge was existing on 28 February 2015; and

(b) a record of the number of cattle housed in that structure as at 28 February 2015 is providedto the CRC on request; and

(c) where the number of cattle has increased compared to the number of cattle present priorto 28 February 2015 an odour management plan is prepared in accordance with Schedule 2and implemented by the person responsible for the discharge into air.

7.71 The discharge of contaminants into air from the accommodation of more than 30 cattle (excludingcalves) in a barn or other roofed structure, whether enclosed or not, that does not comply withcondition 2 or 3 of Rule 7.70 is a restricted discretionary activity.


1. The quantity, quality and type of discharge into air and any effects arising from that discharge,including cumulative effects; and



2. The methods to control the discharge and avoid, remedy or mitigate any adverse effects, includingplant and equipment; and

3. The quality of, compliance with and auditing of any Odour Management Plan; and






7.72 The discharge of contaminants into air from mushroom farming, established after 1 June 2002,is a restricted discretionary activity provided the following condition is met:

1. The discharge of odour does not cause an offensive or objectionable effect beyond the boundaryof the property of origin when assessed in accordance with Schedule 2.








Animal effluent and solid animal waste

7.73 The discharge of contaminants into air from the collection, storage, treatment and applicationof liquid and slurry animal effluent or solid animal effluent onto production land, is a permittedactivity provided the following conditions are met:


2. From 1 January 2017, an odour management plan is prepared in accordance with Schedule 2 andimplemented by the person responsible for the discharge into air; and

3. The odour management plan is supplied to the CRC on request; and

4. A record of all effluents discharged for the previous 3 months is kept by the person responsiblefor the discharge and provided to the CRC on request. The record must include:

(a) the type of effluent applied to land; and

(b) the location of the application; and

(c) the estimated daily quantity of effluent discharged at each location; and

(d) the wind direction at the time of application.



7.74 The discharge of contaminants into air from the collection, storage, treatment and applicationof liquid and slurry animal effluent or solid animal effluent onto production land that does notcomply with one or more of conditions 2, 3, or 4 of Rule 7.73is a restricted discretionary activity.


1. The quantity, quality and type of discharge into air and any effects arising from that discharge,including cumulative effects; and

2. The methods to control the discharge and avoid, remedy or mitigate any adverse effects, includingthe odour management plan; and






Offal pits

7.75 The discharge of contaminants into air from the decay of animals, animal parts, or biodegradablewastes disposed of in an offal pit, is a permitted activity provided the following conditions aremet:


2. Offal not completely covered with impermeable material or soil is located greater than 150m fromany sensitive activity not located on the property of origin; or

3. Offal that is completely covered with impermeable material or soil is located greater than 50mfrom any sensitive activity not located on the property of origin.

7.76 The discharge of contaminants into air from the decay of animals or animal parts or biodegradablewastes, disposed of in an offal pit, that does not comply with condition 2 or 3 of Rule 7.75 is adiscretionary activity.

Agrichemicals and fertilisers

7.77 The discharge of contaminants into air from the application of agrichemicals or fertilisers is apermitted activity provided the following conditions are met:


2. The substance is approved under the Hazardous Substances and New Organisms Act 1996 andthe use and discharge of the substance is in accordance with all conditions of the approval; and

3. The application of the agrichemicals is undertaken in accordance with Appendix L4 (Storage),Part 5.3 (Use), Appendix S (Disposal) and Appendix C9 (Records) of NZS8409:2004 Managementof Agrichemicals where relevant to the particular substance and application method being used;and

4. The discharge does not have an adverse effect on vegetation or fauna beyond the boundary of thetarget location; and

5. The discharge does not have an adverse effect on any sensitive activity, non-target crops, ororganic farming systems, wāhi tapu, wāhi taonga or place of significance to Ngāi Tahu that isidentified in an Iwi Management Plan.



7.78 The discharge into air of contaminants from the application of agrichemicals for the purpose ofaddressing a biosecurity incursion as a requirement of the Biosecurity Act 1993 is a permittedactivity provided the following conditions are met:


2. The substance is approved under the Hazardous Substances and New Organisms Act 1996 andthe use and discharge of the substance is in accordance with all conditions of the approval; and

3. The application of the agrichemicals is undertaken in accordance with Appendix L4 (Storage),Part 5.3 (Use), Appendix S (Disposal) and Appendix C9 (Records) of NZS8409:2004 Managementof Agrichemicals where relevant to the particular substance and application method being used;and

4. The responsible authority advises the CRC and gives public notice not less than 48 hours prior tospraying occurring, of the following:

(a) the organism to be eradicated; and

(b) the principal actions that are to be taken in the attempt to eradicate the organism; and

(c) the geographical area of the intended spraying; and

(d) the duration of the discharge, the name of the agrichemical to be used, the rate and methodof application, and the name and contact details of the applicator.

7.79 The discharge of contaminants into air from the application of agrichemicals or fertilisers thatdoes not comply with one or more of the conditions 2, 3, 4 or 5 of Rule 7.77 or conditions 2, 3 or4 of Rule 7.78, is a restricted discretionary activity.


1. The substance to be discharged including its toxicity and volatility and the carrying agent(formulation); and

2. The proposed method of application, including the type of spray equipment to be used, the sprayvolume and droplet size, the direction of spraying and the height of release above the ground;and

3. The nature of any training undertaken by the operator; and

4. Measures to avoid agrichemical spray drift or fertiliser drift beyond the target location; and

5. The extent to which the use or application complies with NZS8409:2004 Management ofAgrichemicals; and

6. Benefits to the community; and





7.80 The discharge of contaminants into air that does not comply with condition 1 of Rules 7.65, 7.67,7.68, 7.69, 7.70, 7.72, 7.73, 7.75, 7.77 or 7.78 is a non-complying activity.



Small-scale heating appliances

Region Wide

Note: Rule 7.81 applies both outside and inside Clean Air Zones to accommodate small-scale heating applianceson industrial or trade premises.

7.81 The discharge of contaminants into air from a small-scale heating appliance located on anindustrial or trade premise that is not classified by Rules 7.82 to 7.108, is a permitted activity.

Outside Clean Air Zones

7.82 Outside a CleanAir Zone, the discharge of contaminants into air from a small-scale heatingappliance, including appliances fitted with a secondary emission reduction device is a permittedactivity provided either of the following conditions is met:

1. The site is 2ha or greater in area; or

2. Where the site is less than 2ha in area:

(a) there is no visible discharge for a period exceeding 15 minutes following start up or 5 minutesfollowing refuelling; and

(b) any enclosed solid fuel burner installed after 28 February 2015 is a low emitting enclosedburner, an ultra-low emitting enclosed burner; and

(c) the solid fuel to be burnt:

(i) has a sulphur content of no more than 1% by weight; and

(ii) has a moisture content no more than 25%; and

(iii) in any pellet burning device meets the fuel specifications for the device as set out inthe manufacturer’s instructions.

7.83 Outside a Clean Air Zone, the discharge of contaminants into air from a small-scale heatingappliance that does not comply with either condition 1 or condition 2 of Rule 7.82 is a prohibitedactivity.

Within Clean Air Zones

Note: Within Clean Air Zones, the relevant rules for any small-scale heating appliance burning solid fuel andfitted with a secondary emission reduction device are Rules 7.87 and 7.88.

7.84 Within any Clean Air Zone, the discharge of contaminants into air from a small-scale heatingappliance where:

1. the appliance is both on a site less than 2ha and is not registered and maintained in accordancewith Schedule 8; or

2. the appliance is an enclosed solid fuel burner installed after 28 February 2015 and is not a lowemitting enclosed burner or an ultra-low emitting burner;or

3. a visible discharge from the appliance continues for more than 15 minutes after start-up and 5minutes after refuelling; or

4. the solid fuel to be burnt:

(a) has a sulphur content greater than 1% by weight; or

(b) has a moisture content greater than 25%; or

(c) is burnt in a pellet fuel burning device and the fuel does not meet the specifications for theappliance set out in the manufacturer's instructions

is a prohibited activity.



7.85 Within any Clean Air Zone, the discharge of contaminants into air from an ultra-low emittingenclosed burner, or a small scale heating appliance burning liquid or gas fuel, is a permittedactivity, except where the discharge is otherwise prohibited by Rule 7.84.

7.86 Within any Clean Air Zone, the discharge of contaminants into air froma small-scale heating appliance located in a heritage building is a permitted activity providedthe following conditions are met:

1. The small-scale heating appliance is located within a heritage building that is listed in Schedule10 or a heritage building that is listed as a Category 1 heritage building by Heritage New ZealandPouhere Taonga; and

2. The small-scale heating appliance and chimney were original features of the building (includingrestored original features).

7.87 Within any Clean Air Zone, the discharge of contaminants into air from a small-scale heatingappliance in a heritage building that does not meet condition 1 or 2 of Rule 7.86 is a prohibitedactivity.

7.88 Within any Clean Air Zone on sites 2ha or greater in area, the discharge of contaminants into airfrom a small-scale heating appliance burning solid fuel and fitted with a secondary emissionreduction device is a permitted activity, except where the discharge is otherwise prohibited byRule 7.84.

7.89 Within any Clean Air Zone on sites 2ha or less in area, the discharge of contaminants into airfrom a small-scale heating appliance burning solid fuel and fitted with a secondary emissionreduction device is a restricted discretionary activity.


1. The attainable standard of the discharge into air as compared against the emission and efficiencystandards for an ultra-low emitting burner as set out in the definition Table 2.2.

2. The relevant requirements of the Resource Management (National Environmental Standards forAir Quality) Regulations 2004; and

3. Methods to prevent the secondary emission reduction device being bypassed or tampered within such a way as to affect the performance of the device; and

4. Methods to ensure the consistency of performance and design life of the secondary emissionreduction device; and

5. The maintenance requirements of the secondary emission reduction device; and


Within the Rangiora, Kaiapoi and Ashburton Clean Air Zones

7.90 Within the Rangiora, Kaiapoi and Ashburton Clean Air Zone, on sites less than 2ha in area, thedischarge of contaminants into air from an open fire is a prohibited activity.

7.91 Within the Rangiora, Kaiapoi and Ashburton Clean Air Zones on sites 2ha or greater in area, thedischarge of contaminants into air from an open fire, except where the discharge is otherwiseprohibited by Rule 7.84 is a permitted activity provided the following condition is met:

1. The discharge is from an open fire that was installed prior to 1 January 2013.

7.92 Within the Rangiora, Kaiapoi and Ashburton Clean Air Zones, the discharge of contaminants intoair from an older-style enclosed burner, except where the discharge is otherwise prohibited byRule 7.84, is a permitted activity provided either of the following conditions is met:

1. The older-style enclosed burner is located on a site that is 2ha or greater in area; or

2. The discharge does not occur after 15 years from the date of installation of that burner.



7.93 Within the Rangiora, Kaiapoi and Ashburton Clean Air Zones the discharge of contaminants intoair from a low emitting enclosed burner, except where the discharge is otherwise prohibited byRule 7.84, is a permitted activity provided either condition 1, or conditions 2 and 3 and 4 are met:

1. The low emitting enclosed burner is located on a site that is 2ha or greater in area; or

2. The low emitting enclosed burner is not installed after 1 January 2019; and

3. The discharge is not from a low emitting enclosed burner after:

(a) 20 years from the date of installation of that burner; or

(b) 1 January 2019

whichever is later; and

4. If installed after 28 February 2015 but before 1 January 2019, the low emitting enclosed burner islocated in:

(a) a dwelling, including an extension or alteration to that dwelling, for which a building consentwas issued prior to 31 December 2009 in Rangiora or Kaiapoi, or 31 December 2015 inAshburton; and

(b) if an existing dwelling the burner replaces an open fire, older-style enclosed burner or lowemitting enclosed burner that was lawfully operable throughout the 12 months prior to theinstallation.

7.94 Within the Rangiora, Kaiapoi and Ashburton Clean Air Zones, the discharge of contaminants intoair from an open fire that does not meet the condition of Rule 7.91; or from an older-style enclosedburner that does not meet either condition 1 or 2 of Rule 7.92; or from a low-emitting enclosedburner that does not meet either condition 1, or any of conditions 2, 3 or 4 of Rule 7.93 is aprohibited activity.

Within the Christchurch Clean Air Zone:

7.95 Within the Christchurch Clean Air Zone, on sites less than 2ha in area, the discharge ofcontaminants into air from an open fire or an older-style enclosed burner is a prohibited activity.

7.96 Within the Christchurch Clean Air Zone, on sites 2ha or greater in area, the discharge ofcontaminants into air from an open fire except where the discharge is otherwise prohibited byRule 7.84, is a permitted activity provided the following condition is met:

1. The discharge is from an open fire that was installed prior to 1 January 2013.

7.97 Within the Christchurch Clean Air Zone, on sites 2ha or greater in area, the discharge ofcontaminants into air from an older-style burner, except where the discharge is otherwiseprohibited by Rule 7.84, is a permitted activity.

7.98 Within the Christchurch Clean Air Zone the discharge of contaminants into air from a low emittingenclosed burner, except where the discharge is otherwise prohibited by Rule 7.84, is a permittedactivity provided either condition 1, or conditions 2 and 3 and 4 are met:



3. The discharge is not from a low emitting enclosed burner after:


(b) 1 January 2019


4. If installed after 28 February 2015 but before 1 January 2019, the low emitting enclosed burner islocated in:



a dwelling, including an extension or alteration to that dwelling, for which a building consentwas issued prior to 1 January 2003; and

(a)


7.99 Within the Christchurch Clean Air Zone, the discharge of contaminants into air from an open firethat does not meet the condition of Rule 7.96; or from a low-emitting enclosed burner that doesnot meet either condition 1, or any of conditions 2 or 3 or 4 of Rule 7.98 is a prohibited activity.

Within the Timaru Clean Air Zone:

7.100 Within the Timaru Clean Air Zone, on sites less than 2ha in area, the discharge of contaminantsinto air from an open fire is a prohibited activity.

7.101 Within the Timaru Clean Air Zone, on sites 2ha or greater, the discharge of contaminants into airfrom an open fire, except where the discharge is otherwise prohibited by Rule 7.84, is a permittedactivity.

7.102 Within the Timaru Clean Air Zone the discharge of contaminants into air from an older-styleenclosed burner, except where the discharge is otherwise prohibited by Rule 7.84 is a permittedactivity provided either of the following conditions is met:


2. The discharge does not occur after:


(b) 1 January 2017;

whichever is later.

7.103 Within the Timaru Clean Air Zone the discharge of contaminants into air from a low emittingenclosed burner except where the discharge is otherwise prohibited by Rule 7.84, is a permittedactivity provided either condition 1, or conditions 2 and 3 and 4 are met:



3. The discharge does not occur after:


(b) 1 January 2019


4. If installed after 28 February 2015, the low emitting enclosed burner is located in:

(a) a dwelling, including an extension or alteration to that dwelling, for which building consentwas issued prior to 31 December 2015; and


7.104 Within the Timaru Clean Air Zone, the discharge of contaminants into air from an older-styleenclosed burner that does not meet either condition 1 or 2 of Rule 7.102; or from a low-emittingenclosed burner that does not meet either condition 1, or any of conditions 2 or 3 or 4 of Rule7.103 is a prohibited activity.



Within the Geraldine and Waimate Clean Air Zones:

7.105 Within the Geraldine and Waimate Clean Air Zones the discharge of contaminants into air froman open fire, except where the discharge is otherwise prohibited by Rule 7.84, is a permittedactivity provided either of the following conditions is met:

1. The open fire is located on a site that is 2ha or greater in area; or

2. The discharge does not occur after 31 December 2016.

7.106 Within the Geraldine and Waimate Clean Air Zones the discharge of contaminants into air froman older-style enclosed burner, except where the discharge is otherwise prohibited by Rule 7.84,is a permitted activity provided either of the following conditions are met:


2. The discharge into air does not occur after the date on which the property in which the older-styleenclosed burner is located is sold or 1 January 2020, whichever is sooner.

7.107 Within the Geraldine and Waimate Clean Air Zones the discharge of contaminants into air froma low emitting enclosed burner, except where the discharge is otherwise prohibited by Rule 7.84,is a permitted activity.

7.108 Within the Geraldine and Waimate Clean Air Zones the discharge of contaminants into air froman open fire that does not meet either condition 1 or 2 of Rule 7.105; or from an older-style enclosedburner that does not meet either condition 1 or 2 of Rule 7.106, is a prohibited activity.



8 Schedules

Schedule 1: Information to be provided with applications for resource consent

The following are the general information requirements to assess a resource consent application to dischargecontaminants into air. This is followed by additional information required for specific activities.

The information provided will be in such detail to correspond with the scale and significance of the actual andpotential effects that the activity may have on the environment. In other words, if the environmental effectsare likely to be minor, less detail will be required than if the effects could be significant or their extent is notknown.

General information to be provided for all consent applications for discharges into air

Resource consent applications for all discharges into air must include the following information:

1. Detailed description of the activity and the contaminants (including odour, dust and particulates) to bedischarged, including the frequency, amount and concentrations where applicable.

2. A description, including diagrams, of structures involved in the discharge into air.

3. The legal description of the site.

4. A location map showing the separation distance between the discharge to property boundaries, dwellings,buildings and sensitive areas.

5. A description characterising the affected environment, including land use zoning set out in the relevantdistrict plan.

6. A detailed assessment of compliance with the relevant regional plans including how the activity andassociated activities comply with the rules for these activities.

7. A list of people who are potentially affected by the proposal. A description of any consultation undertakenwith these people, including written approvals if these have been obtained. The CRC can provide copiesof standard forms for recording of written approvals, if required.

8. A list of procedures, including maintenance for mitigating effects and the frequency that these proceduresshould occur. Where applicable, these should be in line with any relevant industry codes of practice orbest practice guidelines.

9. The consent duration being applied for.

10. Assessment of alternative options to the proposal.

Additional information to be provided for specific discharges into air

For resource consents for discharges into air of odour and/or dust

Resource consent applications for discharges into air of odour and/or dust should include the followinginformation:

1. An assessment of effects of the discharge in accordance with the following documents where applicable:MFE (2003) Good Practice Guide for Assessing and Managing Odour in New Zealand, MfE (2001) GoodPractice Guide for Assessing and Managing the Environmental Effects of Dust Emissions, relevant industry



best practice guidelines or industry codes of practice. This assessment will include a description of theextent of the effects as follows:

(a) the frequency of odour and/or dust effects; and

(a) the intensity of odour and/or dust effects; and

(b) the duration of the odour and/or dust effects; and

(c) the offensiveness of the odour and/or dust effects; and

(d) the location where the odour and/or dust effects can be experienced.

2. The assessment of effects discussed in 1 above may include some or all of the following techniques:

(a) comparison with the effects of existing processes of similar size and type, including reference toindustry standards and codes of practice; and

(a) dispersion modelling of contaminant emissions, where the emission rate has been measured (usingolfactometry, for example); and

(b) observation of the existing discharge and any effects; and

(c) information gathered from people that may be affected by an existing discharge, including surveysand examination of complaints records; and

(d) extrapolation from known emissions and effects of scale models or trials of the process.

3. A list of mitigation measures and procedures to ensure that the extent of effects do not constitute anoffensive or objectionable effect pursuant to Schedule 2.

4. For odorous activities, a draft odour management plan developed in accordance with Schedule 2.

5. For activities producing dust, a draft dust management plan prepared in accordance with Schedule 2should be provided which includes but is not limited to:

(a) what dust control procedures must be done and why; and

(b) who has to carry out the dust control procedure and/or ensure that they have been carried out;and

(c) how the dust control procedures will be carried out; and

(d) the anticipated outcomes; and

(e) how these outcomes will be monitored.

For resource consent applications for discharges into air from large scale fuel burning devices

Resource consent applications for discharges into air from large scale fuel burning devices should include thefollowing information:

1. The type of fuel burned, the maximum amount of fuel burned per hour and per week, and the approximatehours of operation of the device.

2. The net heat output rating of the device, and the type and age of device.

3. The height (proposed) of the emission stack above ground level and above the roof of the buildingcontaining the device

4. A description of the type of fitting attached to the top of the chimney (e.g., rain hat, cone, rain excluder,wind deflector), which may affect the emission velocity and dispersion of contaminants.

5. Where appropriate, a description of any thermal insulation of the chimney and of any control equipmentused to reduce the emission of contaminants such as sulphur dioxide.

6. Where known, a list of contaminant gases and/or particulates discharged and an estimate of their emissionrates where possible.

7. For solid fuel, the concentration of particulate matter in the emission stack(s) measured in accordancewith the methods specified in Schedule 7.



8. Where known, the predicted emission velocity and temperature of the discharge.

9. An assessment of the effects of the discharge on the environment. The techniques used to assess effectsmay include some or all of the following:

(a) knowledge of the effects of existing processes of similar size and type, including reference toindustry standards; and

(b) dispersion modelling of contaminant emissions, where the emission rate has been estimated bycalculation, measurement or from emission factors; and

(c) observation of the existing discharge and any effects; and

(d) information gathered from people who may be affected by an existing discharge, including surveysand examination of complaints records; and

(e) extrapolation from known emissions and results of trials using scale models or trials of the process;and

(f) identification of nearby emission sources that may contribute to the cumulative effects ofcontaminants discharged; and

(g) an assessment of the cumulative effects of the discharge, in combination with emissions from thesources identified above and background levels; and

(h) the location of nearby sensitive areas or activities that may be affected by the discharge; and

(i) the height, width and length of nearby buildings and structures that may influence wind-flow andthe dispersion of contaminants. This is best achieved by preparing a sketch map. This informationis particularly important for sources where dispersion modelling may be required.

10. A description of any proposed monitoring of the discharge or effects. This monitoring may include:

(a) measurement of emissions; and

(b) measurement of contaminant concentrations in air within or beyond the site boundary; and

(c) records of the maintenance of equipment and emission control devices to minimise emissions; and

(d) keeping records of material consumption and operating parameters related to emissions; and

(e) regular inspections of the discharge and associated processes; and

(f) recording of any complaints relating to the discharge and action taken to remedy any identifiedcause of complaint.

Information to be provided for resource consent applications for discharges into air from outdoorburning

Resource consent applications for discharges into air from outdoor burning must include the followinginformation:

1. The proposed time of year and time of day of burning.

2. Expected duration of the burn.

3. Approximate land area or volume of material to be burned.

4. The type and source of material to be burned.

5. An assessment of the effects of the discharge, having particular regard to the health, nuisance and visualeffects of particulate matter emitted from the fire.

6. Mitigation measures proposed, for example maximising distance from sensitive areas, ensuring thatvegetation is as dry as possible, and limiting burning to favourable weather conditions.



Information to be provided for resource consent applications for discharges into air from industrialor trade premises or processes

Resource consent applications for discharges into air from industrial or trade premises or processes mustinclude the following information:

1. A clear and concise description of all activities within the site that require resource consent for thedischarge of contaminants into air. This description should include typical hours of operation and thequantity of materials consumed in the process that leads to the discharge of contaminants into air. Asite map should be provided showing the location of all discharge sources.

2. Detail of the method of discharge from each process and the height (above ground level) of the dischargeinto air. For example, the discharge may be from a stack, a vent in the roof of a building, or a fugitiveemission from stockpiles or open doorways. In the case of emission stacks, the temperature, emissionvelocity and any fitting above the stack (such as a rain excluder) should be specified.

3. The height, width and length of nearby buildings and structures that may influence wind-flow and thedispersion of contaminants. This is best achieved by preparing a sketch map. This information is particularlyimportant for sources where dispersion modelling may be required.

4. An assessment of the effects of the discharge on the environment. The techniques used to assess effectsmay include some or all of the following:

(a) knowledge of the effects of existing processes of similar size and type, including reference toindustry standards; and

(b) dispersion modelling of contaminant emissions, where the emission rate has been estimated bycalculation, measurement or from emission factors; and

(c) observation of the existing discharge and any effects; and

(d) information gathered from people that may be affected by an existing discharge, including surveysand examination of complaints records; and

(e) extrapolation from known emissions and effects of scale models or trials of the process.

5. A list of mitigation measures proposed to prevent or reduce the predicted adverse effects. Some of thesemeasures could be imposed as conditions of consent, such as minimum stack height, maximum quantityof material processed or contaminants discharged, use and maintenance of filters, or monitoring of thedischarge.

6. A description of any proposed monitoring of the discharge or effects. This monitoring may include:

(a) measurement of emissions; and

(b) measurement of contaminant concentrations in air within or beyond the site boundary; and

(c) records of the maintenance of equipment and emission control devices to minimise emissions; and

(d) keeping records of material consumption and operating parameters related to emissions; and

(e) regular inspections of the discharge and associated processes; and

(f) recording of any complaints relating to the discharge and action taken to remedy any identifiedcause of complaint.

7. A description of any nearby emission sources that could, in combination with the proposed discharge,contribute to cumulative effects. Assess the additive effect of these emissions.

Information to be provided for resource consent applications where the effects of the activityare unknown or unpredictable due to absence of information

1. An assessment to determine the risks associated with the proposal given the lack of certain information.



Schedule 2: Assessment of offensive and objectionable effectsCriteria for assessing offensive or objectionable dispersal or deposition of smoke particles

The Canterbury Regional Council, for the purposes of assessing compliance with permitted activity conditions,resource consent conditions, or sections 17(3)(a), 314(1)(a)(ii) or 322(1)(a)(ii) of the RMA, and resource consentapplicants carrying out assessments pursuant to this Schedule, will have regard to the following matters whendetermining whether or not a discharge of smoke particles from a combustion source has caused anobjectionable or offensive effect:

1. The frequency of smoke events; and

2. The intensity of events, as indicated by quantity of smoke produced and the degree of effect; and

3. The duration of each smoke event; and

4. The offensiveness of the discharge, having regard to the nature of the smoke; including soiling of materialsand structures, any health effects, and associated odour; and

5. The location of the smoke, having regard to the sensitivity of the receiving environment, including takinginto account the relevant zone(s) and provisions in the relevant District Plan.

Note: odour may be associated with the smoke discharge and should also be considered in terms of the criteriafor assessing offensive and objectionable odour.

Assessment will be based on the combined impact of 1. to 5. above, determined by some or all of the followingsources, as applicable. (It will not be necessary to consider all the listed matters in items set out under points3 (a)-(h) in every case).

1. Other validated smoke complaints or events relating to smoke discharges from the same site, includingprevious validated complaints from one location.

2. Weather conditions at the time of the smoke event, particularly wind direction.

3. Information regarding operational conditions that may have caused the smoke discharge. The effectivenessof control measures used to minimise smoke emissions will be taken into account. Consideration will begiven to the extent to which good practice guidance was followed, including:

(a) Outdoor burning:

(i) the content and implementation of a smoke management plan prepared in accordance within Schedule 3.

(b) Large scale fuel burning equipment:

(i) operation according to manufacturer’s instructions and any relevant codes of practice (suchas the CRL Environmental Code of Practice for Coal Fired Boilers <5 MW Capacity); and

(ii) compliance with minimum fuel quality specifications, including: moisture content of wood;ash and fines content of coal; sulphur content (relating to odour and potential health effects);and

(iii) frequency of equipment maintenance, including ash removal, adjustment of the fuel to airratio and testing of combustion gases or compression ratio/power output (as appropriate);and

(iv) the results of any measurements of the concentration of suspended particulate matter in thecombustion gas; and

(v) compliance with minimum chimney height and design requirements.

(c) Small scale fuel burning devices:

(i) compliance with minimum fuel quality specifications, including: moisture content of wood;ash and fines content of coal; sulphur content (relating to odour and potential health effects);and

(ii) compliance with minimum chimney height and design requirements; and



(iii) compliance with suspended particulate emission criteria for the fuel burning device; and

(iv) operation of solid fuel burning appliances for extended periods at ‘low burn’ such that thefire smoulders (this is not regarded as good practice and can result in excessive smokeemissions).

(d) The duration of observed smoke emissions from the chimney or fire, having regard to circumstanceswhere the following guidelines are exceeded:

(i) Large scale fuel burning equipment:

(1) coal and wood burning – dark smoke (darker than Ringelmann Shade No.1) for not morethan 30 minutes in the case of a cold start and not more than four minutes during eachsucceeding hour of operation; and

(2) pellet burning - dark smoke (darker than Ringelmann Shade No.1) for not more than 15minutes in the case of a cold start and not more than two minutes during eachsucceeding hour of operation; and

(3) gas and oil burning equipment - dark smoke (darker than Ringelmann Shade No.1) fornot more than two minutes during each hour of operation.

(ii) Small scale fuel burning devices:

(1) visible smoke for not more than 15 minutes in the case of a cold start and more thanfive minutes during each succeeding hour of operation.

(e) Whether a complaint register is held at the site. In the case of large scale fuel burning equipmentor frequent outdoor burning the CRC may require the discharger to keep such a register and identifyany cause of an alleged smoke, including remedial action taken. Some existing consents includeconditions requiring that such a register be kept.

(f) Contents of smoke diaries held by people living and working in the affected area. If significantongoing effects occurs, people may be requested to keep such a diary. The diaries would recorddetails of any smoke event, including the date and time of the event, weather conditions (windspeed and direction) at that time, a description of the effect detected, and the duration of thesmoke event.

(g) Results of a public survey or field investigation commissioned by the CRC or the discharger. In thiscase, it is critical that the survey or investigation is professionally designed to ensure that credibleand reliable information is gathered.

(h) Collection of deposited particle samples and analysis to identify source (where necessary andappropriate).

Explanatory note

The extent of smoke problem will be determined from all available evidence relating to one or more events.In most cases the applicable information specified in items (e) to (h) (complaint register, diaries, surveys andanalysis of samples) will not be necessary. Ideally, good practice control measures will be implemented bythe person responsible for the discharge to remedy objectionable or offensive effects without the need for thislevel of investigation. However, for ongoing discharges with potential for significant effects or where enforcementaction is likely to be required, some or all of the techniques set out in items (e) to (h) may be required.

Criteria for assessing offensive or objectionable dust

The Canterbury Regional Council, for the purposes of assessing compliance with permitted activity conditions,resource consent conditions, or sections 17(3)(a), 314(1)(a)(ii) or 322(1)(a)(ii) of the RMA, and resource consentapplicants carrying out assessments pursuant to this Schedule, will have regard to the following matters whendetermining whether or not a dust discharge has caused an objectionable or offensive effect:

1. The frequency of dust events; and

2. The intensity of dust events, as indicated by dust quantity and the degree of effect; and



3. The duration of each dust event; and

4. The offensiveness of the discharge having regard to the nature of the dust, including soiling of materialsor structures and any potential health effects; and

5. The location of the dust, having regard to the sensitivity of the receiving environment, including takinginto account the relevant zone(s) and provisions in the relevant District Plan.

Assessment will be based on the combined impact of 1 to 5 above, determined by some or all of the followingsources. (It will not be necessary to consider all the listed matters in items 1 to 9 in every case).

1. Other validated dust complaints or events relating to discharges from the same site, including previousvalidated complaints from one location.

2. Collection of dust samples and analysis to identify source (where necessary and appropriate).

3. Weather conditions at the time of the dust event, notably wind speed, wind direction and rainfall.

4. Information regarding operational conditions that may have caused the complaint. The effectiveness ofdust control measures at the site will be taken into account.

5. A complaints register is held at the site. The CRC may require the discharger to keep such a register andidentify any cause of an alleged dust effect, including remedial action taken.

6. Dust monitoring both within and beyond the site boundary. This includes both deposited dust andsuspended particulate monitoring. Regard should be had to the Ministry for the Environment’s GoodPractice Guide for Assessing and Managing the Environmental Effects of Dust Emissions (January, 2001)when designing a dust monitoring programme and selecting the method of measurement.

7. Results of dispersion modelling carried out as part of an assessment of effects to predict suspendedparticulate concentrations and dust deposition. These results may be compared to the trigger levelsrecommended in the Ministry for the Environment’s Good Practice Guide for Assessing and Managing theEnvironmental Effects of Dust Emissions (January, 2001). Note that this method will have limitedapplication to dispersed area sources or small scale discharges. Its primary value lies in the predictionof the effects of point source dust discharges, such as stacks.

8. Contents of dust diaries held by people living and working in the affected area. People may be requestedto keep such a diary. The diaries would record details of any dust event, including the date and time ofthe event, weather conditions (wind speed and direction, rainfall) at that time, a description of the typeand amount of the dust detected, and the duration of the dust event.

9. Results of a public survey or field investigation commissioned by the CRC or the person responsible forthe discharge. In this case, it is critical that the survey or investigation is professionally designed to ensurethat credible and reliable information is gathered.

Explanatory note

The extent of dust problem will be determined from all available evidence relating to one or more dust events.In most cases the applicable information specified in items 6 to 9 (dust monitoring, modelling, diaries andpublic surveys) will not be necessary. Ideally, good practice dust control measures will be implemented bythe discharger to remedy objectionable or offensive effects without the need for expensive investigation.However, for large scale discharges with potential for significant effects or where enforcement action is likelyto be required, some or all of the techniques discussed in items 6 to 9 may be required.

Criteria for assessing offensive or objectionable odour

The Canterbury Regional Council, for the purposes of assessing compliance with permitted activity conditions,resource consent conditions, or sections 17(3)(a), 314(1)(a)(ii) or 322(1)(a)(ii) of the RMA, and resource consentapplicants carrying out assessments pursuant to this Schedule, will have regard to the following matters whendetermining whether or not a discharge of odour from an activity is likely to, or has caused “offensive orobjectionable” effects beyond the property boundary:

1. The frequency of odour events; and

2. The intensity of events, as indicated by the degree of strength, but taking account of character or quality;and



3. The duration of each odour event; and

4. The offensiveness of the discharge, having regard to the character of the odour; including reference tothe “hedonic tone”; and

5. The location of the odour, having regard to the sensitivity of the receiving environment, including takinginto account the relevant zone(s) and provisions in the relevant District Plan.

Assessment will be based on the combined impact of items 1. to 5. above, determined from some or all of thefollowing applicable information which outlines a range of assessment tools, situations where they are bestapplied and specific details regarding their implementation.

In the event that an assessment determines that a discharge has caused an "offensive or objectionable" effectbeyond the property boundary, a copy of the written assessment containing that determination will be providedto the emitter if this would result in the discharge no longer being permitted by the Plan.

The New Zealand Ministry for the Environment report Good Practice Guide for Assessing & Managing Odour inNew Zealand, (June 2003, ISBN:0-478-24090-2) suggests a national approach to assessing and managingoffensive odours and contains recommendations, based on expert advice, of good practice for the assessmentand management of odour. Table 4.1 of the Good Practice Guide provides specific procedural advice to councilofficers undertaking odour complaint investigations.

List of tools

The odour assessment tools that may be used to determine whether a discharge of odour is causing objectionableor offensive effects beyond the property boundary include the following:

1. Complaint records; and

2. Community consultation; and

3. Odour annoyance surveys, and other surveying tools such as field investigations; and

4. Odour diary programmes; and

5. Review of process controls & design, including consideration of the best practicable option; and

6. Review of site management & contingency plans; and

7. Odour emissions measurement and dispersion modelling; and

8. Analysis of site specific wind and topographical features; and

9. Experience and information from other sites where the discharge is of a similar nature and scale.

The applicability of each of these assessment tools will depend on the characteristics of the discharge and thenature of the receiving environment. The Good Practice Guide for Assessing & Managing Odour in New Zealand(2003) contains detailed guidance on the selection of appropriate tools.

Tool selection and assessment criteria

The appropriateness of the various assessment tools and recommended evaluation criteria are outlined inTables 1 and 2 below. Existing and new activities are discussed separately. When assessing potential odourfrom new activities it is important that odours released from both normal (controlled) and abnormal(un-controlled) emission scenarios are considered.

When investigating existing activities that may be causing adverse effects, it is important to ascertain the typeof adverse effect that is most likely to be occurring; in terms of “chronic” or “acute” odour effects due tonormal, controlled, or uncontrolled emissions into air. The correct identification of the type of adverse odoureffect will help in the selection of the appropriate odour assessment tool in a particular circumstance.

Use of BPO has special considerations that are fully discussed under the “Implementation Notes” section ofthis guideline. The appropriate selection of other assessment tools and associated criteria (excluding BPO)can be based upon technical matters alone.

Once specific odour assessment tools have been selected, refer to the following section (ImplementationNotes) for guidance on application.



Table 8.2.1 Odour Effects Assessment Tools – Existing Activities

Evaluation CriteriaAssessment ToolsOdour Effect Category

Number of Complaints per MonthComplaint RecordsChronic effectsResidual Emissions exControl System –Normal Operation ofPlant

Anecdotal EvidenceAnecdotal evidence of community feelingin regards to odour effects.

Community Consultation

Percentage (%) at Least AnnoyedOdour Annoyance Survey(i.e accumulatedannoyance over timedue to repeated low

5% to 15% - typical for controlpopulations.20% - effects become significant.

Urban and semi-urban areas

intensity odour impacts50% to 100% - extreme effects onpopulation.

caused by controlled,continuous, or

Percentage of Time (%) Exposed toRecognisable Odours from the Source

Odour Diaries & Weather Monitoring- isolated areas with low populationdensities

semi-continuousemissions from definedand consistentprocesses). Compliance with BPO, or Industry Codes

of Practice.Review of Process Emission ControlSystem(s) Hardware and Design Standard

Modelling Odour Guideline – ExistingOlfactometric Quantification of SourceOdour Emissions & Modelling Refer to the Good Practice Guide for

Assessing & Managing Odour in NewZealand (Table 4.6) for recommendedodour modelling guideline values basedon the sensitivity of the receivingenvironment. Note that for existingactivities, the results from other toolsshould be given more weight thanmodelling predictions.

Complaint RecordsAcute EffectsEquipment of SystemFailures/Mishaps/Abnormal Operation ofPlant

Community Consultation

Level of ACCEPTABLE RISK for UncontrolledOdour Discharges

Review of Odour Management Plan &Contingency Procedures

(i.e. short termoffensive impacts dueto unstable, highly

Odour Annoyance Survey

Odour Diary & Weather Monitoring

N/AOlfactometric Quantification of SourceOdour Emissions & Modelling

variable, oruncontrolled emissionsthat occuroccasionally).

Table 8.2.2 Odour Effects Assessment Tools – New Activities


Community FeedbackCommunity ConsultationChronic effectsResidual Emissions exControl System –Normal Operation ofPlant

Site CharacteristicsEstablish the prevalent seasonal windpatterns, topographical features and likelycold air drainage patterns at the site.

Other ExperiencesExperience with similar sites(i.e accumulatedannoyance over timedue to repeated low

Modelling Odour Guideline – New ActivityOlfactometric Quantification of SourceOdour Emissions & Modelling

intensity odour impacts Compliance with BPO, or Industry Codesof Practice

Review of Proposed Process EmissionControl System(s) Hardware and DesignStandard

due to the controlled,continuous, orsemi-continuous




emissions from definedand consistentprocesses).

- as for chronic effectsCommunity ConsultationAcute EffectsEquipment of SystemFailures/Mishaps/Abnormal Operation ofPlant

Level of ACCEPTABLE RISK for UncontrolledOdour Discharges.

Review of Odour Management Plan &Contingency Procedures

- as for chronic effectsExperience with similar sites

N/AOlfactometric Quantification of SourceOdour Emissions & Modelling

(i.e. short termoffensive impacts dueto unstable, highlyvariable, oruncontrolled emissionsthat occuroccasionally).

Implementation notes

This section provides guidance for conducting site investigations, odour surveys and odour modellingassessments.

1. Site Investigation in response to complaints

CRC officers will sometimes carry out a site investigation in response to a complaint. The CRC officershould advise the alleged offenders of the results of their investigations as soon as possible. This allowsstaff at the alleged source of odour to make their own investigations into the alleged odour incident.

The approach CRC staff are likely to take includes:

a. Record time and location of complaint and complainant’s description of the alleged odour event.

b. Where appropriate, encourage the complainant to communicate directly with the alleged emitter.

c. Advise the alleged emitter as soon as possible (preferably within 24 hours) to enable them to identifythe problem and take action to address the complaint.

d. Record the time that staff at the alleged source were contacted, the name(s) of persons spoken to at thesite and their comments regarding the status of the site activities during the time that the complainant(s)considered the odour to have occurred.

e. Ensure that the assessment of odour from the site is undertaken via a 360 degree sweep of the site, sothat other potential sources of odour can be identified and described.

f. Complete an investigation report that details:

(i) the location of complainant; and

(ii) the character and strength of odour at the alleged location; and

(iii) the wind direction and general weather conditions; and

(iv) an assessment of air upwind of source and complainant’s location; and

(v) a confirmation of likely source or sources of odour; and

(vi) the staff contacted at identified source and note the site’s operating status.

g. Immediately visit the site, or telephone staff to explain the results of the investigation and obtain feedbackupon any likely causes of the odour that were identified by staff, or from the investigation officer’s ownobservations of the site.

h. Provide a copy of the investigation officer’s report to the site’s management staff regarding the odourincident and subsequent investigation findings.



2. Odour annoyance surveys

Odour annoyance surveys are recommended when communities are sufficiently large to allow for astatistically significant odour survey to be instigated.

There are a number of considerations that must be made before an odour annoyance survey is undertaken.These include the existence of appropriate survey population sizes and the appropriate selection ofgroups within the general survey area. Odour annoyance surveys conducted to date have generallyaimed for a target of 50 to 70 responses from any one sub-group of the community, which provides atheoretical survey margin of error in the order of 10%.

Sub-groups are normally defined by their general location with respect to the odour source, such thatpersons living or working within the sub-group receive a similar level of odour impact and during thesame types of wind condition. A useful approach for selecting a sub-group of the survey population isto map out as large an area as possible that will receive a similar level of odour impact for some generalwind condition. In most cases, it is necessary to have three or four sub-groups within an overall surveyarea.

As survey sub-groups are selected for their differing levels of odour exposure, and/or differing directionsfrom the source, the results from such groups should generally stand alone (and not be averagedtogether to provide an overall result), when assessing adverse effects. There is now a significant bodyof odour annoyance survey results for control populations within New Zealand. But it is still preferablethat a control population that is relevant to the survey population is included within the survey design.

It is normal practice to survey residential areas by telephone interview during 7:00 pm to 9:00 pm ona single evening. This allows the survey to be completed quickly and with minimal opportunity forrespondents to communicate with each other about the survey. However on some occasions the surveymay include commercial, industrial zones or educational zones. In these instances, face to faceinterviewing may be the only practical method to complete the odour annoyance survey questionnaireswithin a day or less.

Before completing an odour survey, considerable effort is sometimes necessary to consider the prevalentwind directions within the area, define the target survey sub-groups and ascertain the most practicalapproach for conducting interviews in each case. Note that completing a survey over an extensive areaof a community, without the sufficient pre-analysis of appropriate sub-groups will almost certainlyresult in averaged survey data that is little use.

Odour annoyance survey margins of error can be calculated by fitting a generalised linear model withbinomial errors to the proportion of respondents using a general statistical package such as Genstat 5for Windows 5th edition. This allows for a summary of the 95-percentile confidence intervals for thepercentage of the population who are “at-least annoyed” due to all sources and that is attributed to aparticular odour annoyance source.

3. Odour diary programmes

Diary records from members of the public can be very useful to help improve the general understandingof what specific source is causing incidents of odour effect beyond the boundary and under whatcircumstances. In such cases the aim of the programme is focused towards improving the understandingof the odour sources. This can be important for complex processing sites that have numerous potentialsources of odour. It is important that plant operators record the status of plant operations that wereassociated with the recorded odour incidents and description of the odour to assist in identifying thelikely odour source.

The second common reason for undertaking an odour diary programme is to allow the extent of odourimpacts at a location to be quantified and their environmental significance to be assessed. In thiscircumstance it is important to focus upon the frequency and duration of odour impacts and thedescription of the odour. This allows the percentage of time exposed to recognisable odours to beestimated, as well as the weather conditions that typically lead to these events.



Generally odour annoyance surveys should be undertaken in preference to odour diary programmes forassessing environmental effects. However, when odour impacts are very infrequent, yet capable ofcausing significant short-term effects, then an odour diary programme may be more effective than anodour annoyance survey for monitoring the adverse effects upon the community.

4. Odour emissions measurement & dispersion modelling

The measurement of odour emissions and subsequent dispersion modelling is a complex process thatrequires a high level of expertise to undertake successfully. Reference should be made to detailedguidance provided in the Good Practice Guide for Assessing & Managing Odour in New Zealand (2003)and the Good Practice Guide for Atmospheric Dispersion Modelling (2004). Both guidance documentsare available online at www.mfe.govt.nz

5. Best practicable option (BPO)

The BPO is defined by the RMA as the best method for minimising the discharge of contaminants whentaking the following into account:

a. the nature of the discharge and receiving environment; and

b. the financial implications; and

c. current state of technical knowledge and likelihood that the option will be successful.

Implementation of BPO normally requires an air pollution control expert and/or an individual withindustry specific expertise to assess whether or not proposed odour emission control measures representthe use of BPO in any particular instance. Because the RMA’s definition of BPO allows for a substantialdegree of discretion, experts may not always agree on what represents BPO in a specific circumstance.The BPO for any one activity often changes over time, as technology advances.

The Good Practice Guide for Assessing & Managing Odour in New Zealand (2003) contains furtherdiscussion on the application of BPO under the RMA.

Content of dust, odour and smoke management plans

Management plans, for dust, smoke and odour must describe the practices and actions, or targets whererequired, that the person responsible for the discharge of contaminants into air will take to ensure that theoverall effect of the frequency, intensity, duration, offensiveness and location of the discharge is not offensiveor objectionable.

The management plan can form part of a Farm Environment Plan prepared and implemented in accordancewith Schedule 7 Part A of the Canterbury Land and Water Regional Plan.

The level of detail required for the odour, smoke or dust management plan is relative to the scale of thedischarge and the likelihood of the effect being offensive or objectionable.

The specific requirements of a smoke management plan for the outdoor burning of organic material in ruralareas are set out in Schedule 3. For clarity, a smoke management plan addressing the matters set out inSchedule 3 will be considered to comply with the information requirements of Schedule 2.

A management plan that does not form part of a Farm Environment Plan prepared and implemented inaccordance with Schedule 7 Part A of the Canterbury Land and Water Regional Plan must include the following:

1. A description of the activity that will result in the discharge of contaminants into air; and

2. A description of how often the contaminants will be discharged - e.g. constant, daily, between 10am and2pm on weekdays, only on windy days, once a month; and

3. A description of the intensity and character of the discharge - e.g. is the odour very pungent or light, isthere likely to be a lot of dust or just a small amount and is it fine or course, is the smoke light or dark?;and



http://www.mfe.govt.nz/

4. A description of the maximum duration of the effect of the discharge - e.g. what is the prevailing windand how often will sensitive activities or neighbours be affected by the discharge? Will the effect occurduring times when neighbours would be more or less effected?; and

5. A description of the offensiveness of the discharge - e.g. what are the characteristics of the odour? Is itan unpleasant odour such as sewage, or is it something that is often considered pleasant such as thesmell of baking bread? Is the dust a particular colour that will make property appear dirty, or does itcontain corrosive elements? Is the dust very fine? Is the smoke thick and acrid?; and

6. A description of the location of the discharge, including a description of the activities that occur onneighbouring properties and location of any sensitive activities that may be affected. A sketch plan shouldbe prepared showing the location of the discharge and the location of sensitive receptors (such asdwellings, schools, meeting places, retail premises) and the separation distance between these receptorsand the discharge; and

7. An explanation as to how any adverse effects on sites that are sensitive to Ngāi Tahu, such as statutoryacknowledgement areas, silent file areas or wāhi tapu or wāhi taonga are to be managed; and(2)

8. A description of the management practices being implemented to minimise the discharge or the effectsof the discharge of contaminants - e.g. filters replaced regularly, equipment cleaned regularly, inputtypes, limiting discharges to certain times or conditions (wind direction etc), effluent management system(design features, maintenance etc), filter types, design of stacks and vents, process features (stocknumbers, feed type, type of detergent/ink/oil/chemical used), methods for dampening down dust, oilingroads, flocculent use, establishment of vegetation etc. Reference should be made to controlsrecommended in any relevant good practice guides for the activity; and

9. For smoke management, plans will address the matters set out in Schedule 3.

A management plan that does form part of a Farm Environment Plan prepared and implemented in accordancewith Schedule 7 Part A of the Canterbury Land and Water Regional Plan must include the following:

1. A description of the good management practices to be implemented to actively manage the frequency,intensity, duration, offensiveness and location of the effects of the odour, dust or smoke under therelevant Farm Environment Plan objectives. For the collection, storage, treatment or application of animaleffluent to land, reference should be made to the section on "how to avoid pond odour problems" in theDairyNZ Effluent Technical Note: Odour Management for Storage Ponds; and

2. Explanation as to how any adverse effects on sites that are sensitive to Ngāi Tahu, such as statutoryacknowledgement areas, silent file areas or wāhi tapu or wāhi taonga are to be managed; and(3)

3. An outline of actions and targets for improvement where risks or issues have been identified. For thecollection, storage, treatment and application to land of animal effluent reference should be made tothe section on "dealing with an odour issue" in the DairyNZ Effluent Technical Note: Odour Managementfor Storage Ponds.

2 If in any doubt, the landowner should contact te Rūnanga o Ngāi Tahu or the appropriate papatipu rūnanga.3 If in any doubt, the landowner should contact te Rūnanga o Ngāi Tahu or the appropriate papatipu rūnanga.



Schedule 3: Content of smoke management plans for the outdoor burning of organic material in ruralareasA smoke management plan required by the conditions of rules 7.11 and 7.14 or conditions of resource consentpursuant to rule 7.13 is to contain the following information:

1. Dates of the intended burn - the dates may change if conditions are not favourable on the intended dates,and a note should be kept of the actual burn dates from ignition to when the fire is extinguished.

2. Type of material to be burnt - is it standing crop residue, shelter belt clippings, stumps, entire hedges,forestry debris; paper, cardboard or untreated timber.

3. Forecast windspeed and direction for the actual duration of the fire. Ideally windspeed will be between1 and 15km per hour. For burns planned to take place over a timeframe of more than three days, thesmoke management plan will identify prevailing wind conditions for the time of year.

4. Condition of the material to be burnt - for example: is it green or seasoned; wet or dry; is the materiallarge solid pieces such as tree stumps or smaller loose material such as branches or a combination?

5. Identification of potentially affected parties and sensitive activities - include neighbours living closeenough to be affected, Transit New Zealand if the burn is close to a state highway, New Zealand FireService if it is likely the public will call to raise concerns about the fire.

6. The methods for minimising impacts on people effected - examples include but are not limited to:

(a) Choosing a day to burn when neighbours are away or not likely to be effected;

(b) Burning when wind is blowing away from effected people or sensitive activities;

(c) Locating the fire in a remote area, or at a suitable distance from sensitive activities;

(d) Having machinery available to keep the fire burning hot, or extinguish it if necessary;

(e) Preparing the fire so that the material will burn fast and hot and not slowly smoulder;

(f) Notifying neighbours that you are going to burn; notifying the New Zealand Fire Service before theburn;

(g) Having traffic management in place if the burn causes reduced visibility on roads; not burning incool calm conditions as smoke is unlikely to disperse.

The Canterbury Land and Water Regional Plan manages hill and high country vegetation clearance and shouldbe consulted prior to undertaking any burning in the hill and high country. Check with CRC if in doubt.

A fire permit may be required from:

1. The relevant district or city council;

2. The relevant rural fire authority; or

3. The Department of Conservation, when burning occurs within one kilometre of land administered by theDepartment or when burning occurs in an area owned by the Crown.

Vegetation burning on Crown land may require consent under the Land Act 1948, from the Commissioner ofCrown Lands.



Schedule 4: Contaminants

The main air quality contaminants of interest in the Canterbury Region are discussed below.

PM10 can get deep within our lungs and cause wide ranging health and respiratory problems. The main sourceof PM10 in urban areas is home heating, but industry and transportation also emit PM10. There is no safe levelof PM10 exposure. Acceptable levels of PM10 have been set nationally by the NESAQ, based on the World HealthOrganisation Guideline for PM10. This is a limit of fifty micrograms of PM per cubic metre (50μg/m3) averagedover a 24 hour period. One exceedance of this standard is allowed each year and targets for compliance withthis health-based standard are set for each polluted airshed.

PM2.5 is a component of PM10 consisting of particles of 2.5 microns and smaller. Due to their smaller size theycan get deeper within our lungs. PM2.5 emission sources include home heating, transport and industry. Thereare no national guidance values for PM2.5, but the World Health Organisation recommends a limit of 25 microgramsof PM2.5 per cubic metre (25μg/m3) averaged over a 24 hour period.

It is likely the World Health Organisation guidance values for PM2.5 are regularly exceeded in all of Canterbury'spolluted airsheds. Monitoring shows these values are regularly exceeded in Christchurch and Timaru.

Nitrogen dioxide is a gas that can aggravate asthma symptoms and reduce lung development in children. Themain source of nitrogen dioxide is motor vehicles. Monitoring of nitrogen dioxide in Canterbury has beenundertaken in areas with a high volume of traffic. Even in these congested areas, monitoring shows nitrogendioxide remains below the Ministry for the Environment's guideline values.

Carbon monoxide is a gas that can aggravate heart conditions, and reduce the amount of oxygen received bybody tissues. The main sources of carbon monoxide in Canterbury are home heating and vehicle emissions. Inmost of Canterbury, carbon monoxide levels remain below the Ministry for the Environment's guideline values.However, there are infrequent breaches of guideline values in Christchurch.

Sulphur dioxide is associated with, and can aggravate, respiratory conditions. In Canterbury, the main sourceof sulphur dioxide is industrial emissions. As with carbon monoxide, in most of Canterbury sulphur dioxidelevels remain below the Ministry for the Environment's guideline values. However, there are infrequent breachesof guideline values in Christchurch.

Benzo(a)pyrene is associated with health problems ranging from respiratory irritation to cancer. Home heatingis the main source of benzo(a)pyrene in Canterbury. Concentrations of Benzo(a)pyrene exceed the Ministry forthe Environment's guideline values in Christchurch and Timaru.

Ambient Air Quality Standards are set by the Resource Management (National EnvironmentalStandards for Air Quality) Regulations 2004 for the following contaminants

1. Carbon monoxide (8 hour average)

2. Nitrogen dioxide (1 hour average)

3. Ozone (1 hour average)

4. PM10 (24-hour average)

5. Sulphur dioxide (1 hour average)

Health-based ambient air quality guidelines are set for the following contaminants (Ambient AirQuality Guidelines 2002 Update):

1. Hydrogen sulphide

2. Lead

3. Benzene (year 2002)

4. Benzene (year 2010)

5. 1,3-Butadiene



6. Formaldehyde

7. Acetaldehyde

8. Benzo(a)pyrene

9. Mercury (inorganic)

10. Mercury (organic)

11. Chromium VI

12. Chromium and metal chromium III

13. Arsenic (inorganic)

14. Arsine

15. Carbon monoxide

16. Nitrogen dioxide

17. Ozone

18. PM10

19. Sulphur dioxide



Schedule 5: Emission Stack Heights for Large Scale Fuel Burning Devices

The emission stack height specified in Table 8.5.1 below must be met for the device.

Reference to “any building or structure” means any building or structure that was established, or for whichbuilding consent or resource consent was granted, at the time the stack was established.

For the purposes of this table, structure means anything capable of creating building downwash effects on thestack emission plume.

Table 8.5 .1 Emission stack heights for large scale external combustion devices

Emission stack height (metres about ground level) shall be the greaterof:

Net energyoutput capacity(kilowatts)

Fuel

1m above any building or structure within 15m of the emission stack41-500Gas

7m above ground level within 25m of the stack, or501-5000Gas3m above any building or structure within 35m of the emission stack

7m above ground level within 25m of the stack, or41-500Dieselat least 2m above any building or structure within a distance from theemission stack of 5 times the building height.

8m above ground level within 25m of the stack, or501-2000Dieselat least 3m above any building or structure within a distance from theemission stack of 5 times the building height.

8.5m above ground level within 25m of the stack, or41-100Solid fuelat least 3.5m above any building or structure within a distance from theemissions stack of 5 times the building height.



12m above ground level within 25m of the stack, or301-500Solid fuelat least 6.5m above any building or structure within a distance from theemissions stack of 5 times the building height.

13m above ground level within 25m of the stack, or501-700Solid fuelat least 2.5 times the height of any building or structure within a distancefrom the emissions stack of 5 times the building height.

15m above ground level within 25m of the stack, or701-1000Solid fuelat least 2.5 times the height of any building or structure within a distancefrom the emissions stack of 5 times the building height.



Schedule 6: Application of Ringelmann Scale

THE SOLID FUEL TECHNOLOGY INSTITUTEwww.soliftec.com

SOLIFTEC INFORMATION PAGE

The RingelmannSmoke Chart

CONTENTSPage 1 ExplanationPage 2 Miniature Smoke ChartsPage 3 Recording TablePage 4 The Ringelmann Smoke Chart

Dark smoke is partially burned particles of fuel, the result of incomplete combustion. It can be dangerous because small particles are absorbed into the lungs. White smoke is mainly tiny water droplets, generated when vapour released during combustion condenses

in cool air. Generally, dark smoke is clearly visible against a light sky but difficult to see at night or against a dark background, white smoke is visible in darkness when illuminated but will be more difficult to see against a light sky background.Smoke is commonly measured in terms of its apparent density in relation to a scale of known greyness. The most widely-used scale is that developed by Professor Maximilian Ringelmann of La Station d'Essais de Machines in Paris in 1888. It has a 5 levels of density inferred from a grid of black lines on a white surface which, if viewed from a distance, merge into known shades of grey.There is no definitive chart, rather, Prof. Ringelmann provides a specification; where smoke level '0' is represented by white, levels '1' to '4' by 10mm square grids drawn with 1mm, 2.3mm, 3.7mm and 5.5 mm wide lines and level '5' by all black. A popular version is that published by the U.S. Bureau of Mines in circular 8333 of 1967. The British Standard version (BS2742:1969) alters Ringelmann's specification to give a chart similar, on modern paper with modern ink, to the probable appearance of charts produced on earlier, possibly darker, paper, with paler ink.It should be remembered that the data obtained has definite limitations. The apparent

darkness of a smoke depends upon the concentration of the particulate matter in the effluent, the size of the particulate, the depth of the smoke column being viewed, and natural lighting conditions such as the direction of the sun relative to the observer while the accuracy of the chart itself depends on the whiteness of the paper and blackness of the ink used.USING THE CHARTSThe large chart on page 4 should be printed with black ink onto very white card and mounted vertically on a board. It is preferably fixed to a pole or held by an assistant at a sufficient distance (typically c20m) for the lines to appear to merge into uniform grey rectangles and to be seen in line with the top of the chimney. The addition of a white (No. 0) square can provide a useful indication that both the chart and chimney are equally illuminated. If a larger chart is needed, the shaded rectangles can be made up into larger ones as mosaics.The observer glances from the smoke, as it issues from the stack, to the chart and notes the number most nearly corresponding with the shade of the smoke. A clear stack is recorded as No. 0, and 100 percent black smoke as No. 5.There is very little value in making a single observation. A series of observations should be made, preferably by two or more observers, over an extended period, at regular intervals. There is an example of a recording table on page 3.The Miniature Charts on page 2 are not the official Ringelmann chart, but a handy interpretation of it, intended to be held at arm's length.

PRINTING THESE CHARTSPrint this document on very white A4 size (210mm x 297mm) card – when printed, the box below should be 150mm long and 10mm high. For the charts on page 4, use only highest print quality and only black ink – you may have to adjust your printer settings.

Smoke Laws in both the UK and RoI define the level of smoke prohibited by law as 'dark smoke', darker than shade 2 of the Ringelmann Chart RoI: The Control of Atmospheric Pollution Regulation (1970) prohibits the emission of dark smoke from non-domestic premises for more than a very few (specified) minutes per day. UK: The Clean Air Act (1993) prohibits the emission of dark smoke from all industrial premises and from domestic premises in designated smoke control areas, but allows a defence that the heating equipment was cold and being first lit.

PREPARED BY: Glyn Hughes [email protected] ISSUED: 05/08/10 check for updates at www.soliftec.com

Soliftec.com Ringelmann Chart. Page 1



MINIATURE SMOKE CHARTSThese charts are not the official Ringelmann chart, but simplified interpretations of it for everyday use.

BAR TYPEBlack and white print. Cut along the edge shown, hold at arm's length and compare the smoke source with the cut edge.

CIRCLE TYPEGrey-scale print. Cut out the central hole and hold at arm's length and view the smoke source through the hole.




Ringelmann Smoke Observations RecordAn example of a smoke observation record made every minute over a half-hour period. For observations of a commercial smokestack observations might be made every two to five minutes over 24 hours.

Recorded byDatePoint of observationDistance to stackDirection of windVelocity of wind

MEASUREMENT NUMBER TIME

OBSERVED RINGELMANN

NUMBER1 12:00 02 12:01 03 12:02 04 12:03 05 12:04 06 12:05 07 12:06 18 12:07 19 12:08 1

10 12:09 211 12:10 212 12:11 213 12:12 014 12:13 315 12:14 316 12:15 317 12:16 118 12:17 119 12:18 120 12:19 121 12:20 122 12:21 123 12:22 124 12:23 125 12:24 126 12:25 327 12:26 328 12:27 329 12:28 330 12:29 3

TOTAL 42

SUMMARY Average Ringelmann

NumberAverage smoke density,

%

Total of Ringelmann Numbers 42

= 1.4 x 20 = 28Total number of

observations 30







Schedule 7: Testing for particulate matter in exhaust gasesCombustion sources having a net energy output capacity of less than or equal to 2MW within a CleanAir Zone or 5MW outside a Clean Air Zone

As a minimum requirement the particulate sampling must comply with either ISO9096:2003(E), ASTMD3685M-98, AS 4323.2-1995, USEPA Method 5, USEPA Method 17 or a current equivalent method that complieswith the fundamental sampling requirements of ISO9096:2003(E). Where this methodology is used alone, itwill be assumed for compliance purposes that all particulate matter is PM10. In circumstances where additionalsize specific sampling is necessary to demonstrate compliance with PM10 emission limits in the Plan, theparticulate sampling must comply with USEPA Method 201 or USEPA Method 201A or a current equivalentmethod that complies with the fundamental sampling requirements of that method.

Combustion sources having a net energy output capacity of more than 2MW within a Clean Air Zoneor 5MW outside a Clean Air Zone

For these larger combustion sources both filterable and condensable particulate matter are to be measured.As a minimum requirement the filterable particulate sampling must comply with either ISO9096:2003(E), ASTMD3685M-98, AS 4323.2-1995, USEPA Method 5, USEPA Method 17 or a current equivalent method that complieswith the fundamental sampling requirements of ISO9096:2003(E). Where this methodology is used alone itwill be assumed for compliance purposes that all filterable particulate matter discharged is PM10. Incircumstances where additional size specific sampling is necessary to demonstrate compliance with PM10

emission limits in the Plan, the filterable particulate sampling must comply with USEPA Method 201 or USEPAMethod 201A or a current equivalent method that complies with the fundamental sampling requirements ofthat method. The condensable particulate sampling must comply with USEPA Method 202 or a current equivalentmethod that complies with the fundamental sampling requirements of that method. The test results shouldspecify total particulate matter as the sum of filterable and condensable components.

For all combustion sources of any output, the emission testing must be undertaken:

1. By a person competent in stack emission testing;

2. By an organisation that is ISO 17025 accredited (IANZ) for the methods being used; and

3. Must occur when all fuel burning equipment is operating at greater than 50% of the maximum continuousrating.

An emission test must constitute three samples.

Test results must be adjusted to 0° Celcius, 101.3 kilopascals, and 8% oxygen or 12% carbon dioxide on a drygas basis. For the purpose of this adjustment the concentration of carbon dioxide or oxygen will be analysedusing suitably calibrated equipment. The results shall include a description of the methods used, the rate offuel combustion during testing and any assumptions made.

Discharges via a saturated stack

Where discharges occur via a saturated stack, the testing method will be agreed with the CRC.



Schedule 8: Registration and maintenance of small-scale heating appliances burning solid fuel

Registration and maintenance

If located within a Clean Air Zone, the owner of a small scale heating appliance burning solid fuel must providethe following information to the CRC when an appliance is installed or when ownership of the appliance changes:

1. The full name(s) of the appliance owners;

2. The contact details for the appliance owners;

3. The site address or legal description of the property on which the appliance is installed;

4. The appliance type, make and model.

Upon request by a CRC officer, the person responsible for the small-scale heating appliance must provide thefollowing information to the CRC:

1. A record of maintenance of the appliance in accordance with manufacturers' instructions (can be receipts,photographs or diary entries).



Schedule 9: Small-scale heating appliance auditing process

Audit schedule for low emitting enclosed burners: information required to demonstrate that a burnerachieves the required standards.

National regulations

The appliance must meet any regulations specific to enclosed burners in any relevant Regulations. At the timeof publication these regulations are set out in the Resource Management (National Environmental Standardsfor Air Quality) Regulations 2004.

Test method

The low emitting enclosed burner (including pellet burners) must be tested to demonstrate that it achievesthe emissions and efficiency standards using a test methodology consistent with the Resource Management(National Environmental Standards for Air Quality) Regulations 2004.

Test laboratory or practitioner accreditation

The testing must be undertaken by an independent laboratory or practitioner accredited by an accreditationauthority to carry out the tests involved.

Burner identification

Information needs to be supplied to the testing laboratory or test practitioner, and subsequently to the CRCwith the test report, to uniquely identify the burner unit tested and define all of those parameters that mayaffect the performance of the enclosed burner, including dimensioned assembly drawings with specificationof major components.

Information to be provided to the Canterbury Regional Council

A copy of the following documentation must be provided to the CRC:

1. Test report for emissions and efficiency; and

2. Design drawings and detailed description of the enclosed burner (and water booster if fitted) includingpart identification numbers which match the specifications of the test model to the production model;and

3. Dimensioned assembly drawings with specification of major components; and

4. Sales brochure (if available); and

5. Manufacturer's installation and operating instructions; and

6. Proposed authorisation label.

Technical audit and report

On receipt of the above information, CRC will certify a burner as meeting the appropriate standards if thefollowing criteria are met.

1. A representative example of the enclosed burner is made available for inspection; and

2. The enclosed burner achieves the emissions and efficiency requirements of the Air Plan and the ResourceManagement (National Environmental Standards for Air Quality) 2004; and

3. The burner achieves the enclosed burner design criteria specified in Table 2.2 of the Air Plan; and

4. The summary results in the test report accurately reflect the results recorded in the test runs raw data;and



5. The dimensional information and description provided in the test report is consistent with that shownon the drawings; and

6. The representative enclosed burner is consistent with both the drawings and what was tested.

Five yearly audit

The enclosed burner will be subject to a physical audit of a production model not less than once every fiveyears to determine whether the unit is consistent with the drawings supplied and what was tested for.

Audit schedule for ultra-low emitting enclosed burners: information required to demonstrate thata burner achieves the required standards.

Enclosed burner design

The enclosed burner must be designed to achieve the efficiency and emissions standards when operated by aperson in their own home. This means:

1. The burner cannot be reasonably operated in such a way as to bypass the technology (taking into accountimprovements in available technology over time) that results in ultra-low emissions; and

2. The burner cannot be reasonably tampered with in such a way as to affect its performance - this meansthat is unable to be tampered with using hand tools available in a home such as screwdrivers, spannersand files; and

3. The burner is designed to perform to achieve the emissions and efficiency standard when operated by aperson in their own home; and

4. If maintenance such as cleaning or filter changing is required for the technology to be effective in achievingthe emissions and efficiency standard there must be a process in place to ensure this happens; and

5. The technology for reducing PM10 emissions must be designed to be effective for the duration of theenclosed burner's life.

National regulations

The enclosed burner must meet the minimum requirements of any regulations specific to enclosed burners inany relevant national standards. At the time of publication these regulations are set out in the ResourceManagement (National Environmental Standards for Air Quality) Regulations 2004.

Test method

To be considered to meet the definition of an ultra-low emitting enclosed burner, devices must be tested tosimulated real life conditions, unless the burner is a pellet burner that can be tested in accordance with testmethodology that is consistent with the Resource Management (National Environmental Standards for AirQuality) Regulations 2004. This is a test that is more stringent than the minimum requirements of the ResourceManagement (National Environmental Standards for Air Quality) Regulations 2004.

Test operating regime

The enclosed burner is to be tested over the normal operating regime of the enclosed burner and operatedover a range of output settings: i.e. at maximum and minimum outputs. Results at nominal (maximum) outputsetting would not be accepted unless the enclosed burner can be operated only at this output setting.

The testing must involve a minimum of two tests that include start-up, a period of operation at maximum heatoutput, and a period of operation at minimum heat output reflecting the normal operating conditions for theenclosed burner.

To be valid, results from each test period phase (high and low output) must be within 10% of the mean valueof the tests for this corresponding phase.



Fuel

For log burners, the enclosed burner is to be tested using commercially available wood, including knots andbark, and including test phases for softwood, hardwood and partially seasoned softwood.

For other types of burners that can only operate on a specified fuel, the enclosed burner must be tested usingthe specified fuel for the appliance - for example, this applies to pellet fires.

Efficiency determination

The efficiency may be determined by either a calorimeter room method or a stack loss method.

The efficiency must be converted to gross calorific basis.

The average efficiency must be calculated for the full range of test runs as per the test operating regime above.

The results need to be averaged.

Particulate measurement

The measurement of particulates must be by a method that determines all those particulates that will formwhen the discharge is cooled to not more than 32oC. This includes filterable particulates plus condensables.

In some cases, tests that do not necessarily measure all particulates that would be collected from a dilutiontunnel method with filters at 32oC can be considered with an appropriate scaling that takes this intoconsideration.

Test laboratory or practitioner accreditation

The testing must be undertaken by an independent laboratory or practitioner holding applicable accreditation.

Burner identification

Information needs to be supplied to the testing laboratory or test practitioner, and subsequently to the CRCwith the test report, to uniquely identify the burner unit tested and define all of those parameters that mayaffect the performance of the enclosed burner, including dimensioned assembly drawings with specificationof major components.

Information to be provided to the Canterbury Regional Council

A copy of the following documentation must be provided to the CRC:

1. Test report for emissions and efficiency; and

2. Design drawings and detailed description of the enclosed burner (and water booster if fitted) includingpart identification numbers which match the specifications of the test model to the production model;and

3. Dimensioned assembly drawings with specification of major components; and

4. Sales brochure (if available); and

5. Manufacturers installation and operating instructions; and

6. Proposed authorisation label.

Technical audit and report

On receipt of the above information, CRC will certify a burner as meeting the appropriate standards for anultra-low emitting enclosed burner if the following criteria are met.

1. A representative example of the enclosed burner is made available for inspection; and



2. The enclosed burner achieves the emissions and efficiency requirements of the Air Plan and the ResourceManagement (National Environmental Standards for Air Quality) 2004; and

3. The enclosed burner achieves the enclosed burner design criteria specified in Table 2.2 of the Air Plan;and

4. The summary results in the test report accurately reflect the results recorded in the test runs raw data;and

5. The dimensional information and description provided in the test report is consistent with that shownon the drawings; and

6. The representative enclosed burner is consistent with both the drawings and what was tested.

Five yearly audit

The enclosed burner will be subject to a physical audit of a production model not less than once every fiveyears to determine whether the unit is consistent with the drawings supplied and what was tested for.



Schedule 10: Heritage Buildings

Table 8.10.1 Heritage Buildings - Christchurch Clean Air Zone

#coal burners#open firesLegal descriptionNameStreet address

3Pt TR 62Eliza's Manor House /former dwelling

82 Bealey Avenue

5+5+The area zoned SpecialPurpose (Ferrymead) inthe operativeChristchurch City Planas at 28 February 2015

Ferrymead Park269 Bridlepath Road

3Lot 1 DP42570Canterbury Club129 Cambridge Terrace

3Lot 5 Pt Lot 4 DP12421Former home of KateSheppard

83 Clyde Road

4Lot 2 DP 19964 Lots 2-3DP40363

Dwelling "Daresbury"67 Fendalton Road

2Lots 1-17 DP6163 Lots69-70 PT71-3

Sign of the Takahe200 Hackthorne Road

3Pt Lot 24 DP 15781Dwelling "Nydfa"34A Hansons Lane

1Pt RS 12Former Ilamhomestead/UniversityStaff Club

Ilam Road

13Lot 1 DP10263Riccarton HouseKahu Road

4Lot 2 DP70089St Lukes Vicarage185 Kilmore Street

11RS 41299Former BelfastSchoolhouse

665 Main North Road

2Lot 1 DP10263Midland Club176 Oxford Terrace

3Pt Lot 1 DP 12581Glenmore House435 Port Hills Road

4Lot 30 DP49665Chokebore Lodge148 Racecourse Road

5Lot 9 DP1351Single storey brick villa45 Ranfurly Street

1Pt Res 25 ChristchurchCity

Christ's College HareMemorial Library -

33 Rolleston Avenue

2TS103Ironside House32 Sailsbury Street

11Lot 1 DP 45687 RS 3089Tip Tree CottageSavills Road, Harewood

1Lot 1 DP13624 Lot21DP29333

Cracroft (old stonehouse)

15 Shalamar Drive

2Lot 2 DP 19885Ngāi o Marsh House37 Valley Road

1Lot 30 pt Lot 1 DP2668Wooden arts and craftstyle dwelling

2 Whisby Road

1TS 419-440Former ArchitectsRoom/Arts Centre

2 Worcester Boulevard

1TS 419-440Former CanterburyCollege Hall/the GreatHall - Arts Centre

2 Worcester Boulevard

1Lot 12 DP1003Single storey villa17 WorcesterBoulevard

5Lot 11 DP1003Single storey villa21 WorcesterBoulevard



#coal burners#open firesLegal descriptionNameStreet address

4Pt TS 759, TS 761, TS763, TS 764, TS 765

Christchurch Club154 Worcester Street

Table 8.10.2 Heritage Buildings -Rangiora Clean Air Zone

Legal DescriptionSite NameSite AddressDistrict PlanSite No.

Lot 1 DP 305893Ashley Farm Homestead(Private Home)

269 West Belt RangioraH046

Lot 3 DP 82008Turvey House208 King Street RangioraH047

Lot 2 DP 24808 PtBelgrove52 Kippenberger Avenue RangioraH049Lot 2 9976 also PtRS 267

Lot 3 DP 36263Broadgreen29 George Street RangioraH050

Lot 1 DP 80275Brooklands521 Rangiora Woodend RoadH051

Lot 5 DP 11217Church of St John the Baptist(Anglican)

351 High Street RangioraH052

Lot 2 DP 22648Cottage47 Edward Street RangioraH057

Pt Lot 2 DP 13945Cottage62 Ivory Street RangioraH058

Gaz 92-127 Sec 2Courthouse143 Percival Street RangioraH059SO 17511

Lot 94 DP 30729Fleetwood14 Strachan Place RangioraH060

Pt RS 53House56 Church Street RangioraH063

Lot 3 DP 77512House367 High Street RangioraH064

Flat 1 DP 59879 onHouse66 Ivory Street RangioraH065Lot 2 DP 59835

Lot 2 DP 12916House152 King Street RangioraH067

Lot 1 DP 22450House16 Seddon Street RangioraH069

Lot 1 DP 12159House22 Seddon Street RangioraH070

Lot 1 DP 43552Hunnibell's Shop257 High Street RangioraH071

Lot 2 DP 28806Johnston Buildings - 2 storeyportion only

Cnr Victoria & High Streets RangioraH072

Pt Lot 3 DP 1569Junction Hotel (former)112 High Street RangioraH073

Lot 2 DP 10838 PtNorthern A & P AssociationBuilding (former)

93 Ivory Street RangioraH076Lot 3 DP 6146

Lots 2-4 DP 12852Public Library133 Percival Street RangioraH077

Lots 6 & 7 DP 71Rangiora Bowling ClubPavilion

Cnr Blackett & Good Streets RangioraH078

Pt RS 53Town Hall303 High Street RangioraH079

Lot 2 DP 45094St Mary & St Francis de SalesChurch

39 Victoria Street RangioraH116

Rural Sec 1211Stratford Grove458 Rangiora Woodend RoadH121

Lot 8 DP 69077 BlkRangiora Railway Station2 Blackett Street RangioraH124VI Rangiora SD



Table 8.10.3 Heritage Buildings -Kaiapoi Clean Air Zone


Lot 1 DP 36550Bank of New Zealand buildingand fence

188 Williams Street KaiapoiH012

Lot 1 DP 331683Chadwell250 Williams Street KaiapoiH013

Pt RS 320Cottage5 Meadow Street KaiapoiH015

Pt RS 320Cottage52 Sewell Street KaiapoiH016

Pt RS 366Cottage65 Sneyd Street KaiapoiH017

Pt RS 366Cottage73 Sneyd Street KaiapoiH018

Lot 1 DP 320188Cottage259 Williams Street KaiapoiH019

Lot 4 DP 23453House14 Beswick Street KaiapoiH021

Lot 1 DP 27593House7 Meadow Street KaiapoiH022

Lot 3 DP 49595Kaiapoi Woollen Mill (former)35 Ranfurly Street KaiapoiH026

Pt Lot 1 DP 37286Methodist Church53 Fuller Street KaiapoiH027

Lot 3 DP 5089Old St Paul's Manse56 Sewell Street KaiapoiH029

Lot 15 DP 919 Lot 1Kaiapoi Railway Station65 Charles Street KaiapoiH030DP 42983

Lot 3 DP 26905St Bartholomew's Church23B Cass Street KaiapoiH032

Lot 2 DP 33541The Cream House183 Main North Road KaiapoiH034Lot 2 DP 69220Lot 1 DP 70266

Lot 1 DP 56058Cherryvale56 Cass Street KaiapoiH102

Table 8.10.4 Heritage Buildings - Ashburton Clean Air Zone


Lots 1 & 2 DP 43726Church of the Holy Name(Catholic)

Sealy St, Ashburton17Lot 1 DP 19738 TS659-663669-672

Sec 20 of AshburtonTown

St Andrew's PresbyterianChurch (former)

126-134 Havelock St, Ashburton18

Lot 1 DP 22770 TS 202 Pt203/204

St Andrew's Church (Presby.)74-78 Park St & Havelock St,Ashburton

19

Ashburton Town

Lot 1 DP 19738Presbytery (Catholic)Sealy St, Ashburton20

Pt Lot 125/6 DP 236MenorlueAshburton College, 23 Walnut Ave25Ashburton

Lot 1 DP 36145 TS 495Former Historical Soc. &Museum Building andAshburton Technical SchoolBuilding

242-256 Cameron St, Ashburton26Pt TS 478Ashburton Town

Lot 2 DP 11506Former ANZ Bank230-232 East St & Tancred St,Ashburton

27(now AFL Properties Ltd)

Lot 1 DP 14708Former Tucker's Building147-159 West St, Ashburton28

Pt TS 132Federated Farmers Building163-165 West St & Tancred St,Ashburton

29Ashburton Town(former Bank)

Lot 1 DP 9913W. Patching Building179-185 West St, Ashburton30




Lot 1 DP 30445Westburn Courts201-213 West St & Burnett St,Ashburton

31

TS 193 Pt TS 194Peter Cates Grain Store229-239 West St, Ashburton32Ashburton Town

Lot 2 DP 49621Canty Roller Mill concretestore

407-413 West St, Ashburton33

Lot 2 DP 49621Canterbury Roller Flour Mill415 West St, Ashburton34(orig bldg)

Lot 1 DP 20442 PtCanterbury Roller Flour Mill415-429 West St, Ashburton35Lot 1 DP 18825(Ashfords Mill House)

TS 181Former Westpac BankCnr Cass & Burnett St, Ashburton36

Lot 1 DP 62073Former Ashburton RailwayStation

East St, Ashburton37

Lot 2 DP 9681Plunket Rooms111 Victoria St, Ashburton38

Pt TS 1276Old Engineers Office (ACC)239 Havelock St, Ashburton39

Lot 1 DP 23304House50 Bridge St, Ashburton40

Lot 4 DP 33197Former H.D Acland House105 Walnut Ave, Ashburton41with interest in ROW

Town Sec 1003House21 Philip St, Ashburton42

Lot 3 DP 2357House46 Short St, Ashburton43

Res 2283. Pt Res 1775Ashburton CemeterySexton's Hut44

TS 565 CT 27A/619House22 Aitken St, Ashburton101

Lot 3 DP 11060Former House of Dr McBeanStewart

4 Beach Rd, Ashburton103

Lot 23 DP 1494HouseBuckleys Terrace, Ashburton104

Lots 10/11 DP 12044Arcade BuildingBurnett/Tancred Streets, Ashburton105

Lot 2 DP 36616Former House (now offices)73 Burnett St, Ashburton106

TS 146 Pts 136/137 & 147Residence/Offices96-100 Burnett St, Ashburton107

Lot 1 DP 61939Former Anglican Vicarage86 Burnett St, Ashburton108

TS 79062 Cox St (former MalvernHome)

Cnr William & Cox Streets, Ashburton109

Lot 1 DP 58990Cottage54 Eton St, Ashburton110

Lot 1 DP 28103House42 Havelock St, Ashburton111

PT TS 757Dr Baker's House60 Peter St, Ashburton112

Lot 1 DP 12239 CT 481/197House34 Short St, Ashburton113

Lot 2 DP 12308 CT 6B/155House44 Short St, Ashburton114

Lot 9 DP 23494 CT3A/1475

House113 Walnut Ave, Ashburton115

Lot 10 DP 23494House117 Walnut Ave, Ashburton116

TS 1278House172 Walnut Ave, Ashburton117

Lots 441-4 DP 91House4 Wilkin St, Tinwald118

Lot 2 DP 23688House69 Walnut Ave, Ashburton119

Lot 2 DP 40234 CT18A/856

Brigadoon22 Carters Terrace, Ashburton120

Lot 5 DP 24777Bleak HouseCross St, Ashburton121




Lot 5 DP 1995House7 Rapley St, Ashburton122

Lot 1 DP 29348Former Dr Trevor's House32 Trevors Rd, Ashburton123

Lot 59 DP 430House57 Harrison St, Ashburton124

TS 224 & 225Court House122 Cameron St (Baring SquareWest), Ashburton

125

Lot 1 DP 9084Old GlassworksCnr Bremners/Glassworks Rd,Ashburton

126

Lot 1 DP 14206Coldstream StablesEaling - Coldstream Rd RD 3,Ashburton

128Lots 1, 3, 4, Pt 2 DP 8841Blk IV Coldstream SD



Schedule 11: Areas affected by the Ngāi Tahu Claims Settlement Act 1998

The Ngāi Tahu Claims Settlement Act 1998 implements a number of settlement provisions recognising theparticular cultural, spiritual, historical and traditional associations of Ngāi Tahu with particular sites, areasand species. These provisions include the identification of taonga species and the establishment of tōpuni,statutory acknowledgements and nohoanga sites, with the purpose of improving the effectiveness of Ngāi Tahuparticipation in resource management.

The map below shows the areas in Canterbury affected by the Ngāi Tahu Claims Settlement Act 1998. Furtherdescription of these sites is provided as Appendix 1 to the Canterbury Regional Policy Statement.

It is important to recognise that there are other places of significance to Ngāi Tahu, particularly at a local level,including those held on silent files(4). Indigenous biodiversity is also very important to Ngāi Tahu, and indigenousspecies that are not included in the Settlement Act are still taonga.

Statutory acknowledgements

Statutory Acknowledgements recognise Ngāi Tahu mana in relation to a range of sites and areas in the SouthIsland. They provide for the recognition of this mana to be reflected in the management of those areas throughRMA processes.

The Statutory Acknowledgements and definitions of the areas in the Canterbury region and how they affect theresource management process are set out in Schedules 14 to 77 of the Settlement Act.

Pursuant to Section 220 of the Settlement Act, Local and Territorial Authorities within the Ngāi Tahu claim areamust attach to all Regional Policy Statements and Regional and District Plans, information recording all statutoryacknowledgements affecting statutory areas covered wholly or partly by such Policy Statements or Plans, eitherby providing the information in full or by way of reference to the appropriate part of the Settlement Act. Thisschedule identifies the appropriate areas and references Schedules 14 to 77 of the Ngāi Tahu Claims SettlementAct.

Tōpuni

Tōpuni are landscape features of special importance or value to Ngāi Tahu. They place an ‘overlay’ of NgāiTahu values on specific pieces of land managed by the Department of Conservation and ensure that Ngāi Tahuvalues are recognised, acknowledged and provided for.

A list of Tōpuni sites in the Canterbury region and a description of the values associated with them are inSchedules 80 to 93 of the Settlement Act.

Nohoanga

Nohoanga are temporary campsites to facilitate customary fishing and gathering of other resources. The NgāiTahu Settlement provides for 72 such sites. Sites over which Nohoanga Entitlements are to be granted in theCanterbury region are set out in Schedule 95 of the Settlement Act.

Taonga species management

Within the Settlement Act (Section 288), the Crown recognises the special association of Ngāi Tahu with certainbird, plant and marine mammal species. The aim is to improve Ngāi Tahu involvement in the management ofthese species through increased consultative requirements with Ngāi Tahu. A list of taonga species is providedin Schedule 97 of the Settlement Act.

4 Silent files as identified in Te Maire Tau (et al.). 1990 Te Whakatau Kaupapa identifies the general location of wāhi tapu or other specialsites without disclosing their precise location.



Statutory Acknowledgement Areas

What are statutory acknowledgements?

A statutory acknowledgement is an acknowledgement by the Crown of the special relationship of Ngāi Tahuwith identifiable areas. Namely the particular cultural, spiritual, historical and traditional association of NgāiTahu with those areas (known as statutory areas).

The statutory areas within the Canterbury region are identified on the map below.

What are the purposes of statutory acknowledgements?

The purposes of Statutory Acknowledgements are:

1. To ensure that the particular association of Ngāi Tahu with certain significant area in the South Islandare identified and that Te Rūnanga o Ngāi Tahu is informed when a proposal may affect one of theseareas.

2. To improve the implementation of Resource Management Act 1991 processes, in particular by requiringconsent authorities to have regard to statutory acknowledgements when making decision on theidentification of affected parties.

Who may be affected by statutory acknowledgements?

You may be affected by a statutory acknowledgement if you are applying for resource consent for an activitythat is within, adjacent to, or directly impacting on a statutory area.

What happens when you apply?

If you are applying for resource consent for an activity within, adjacent to, or directly impacting on a statutoryarea:

1. The local authority must send a summary of your resource consent application to Te Rūnanga o NgāiTahu, and

2. The local authority must have regard to the statutory acknowledgement in going through thedecision-making process on whether Te Rūnanga o Ngāi Tahu is an affected party in relation to theresource consent application.

How can statutory acknowledgements be used in submissions?

How statutory acknowledgements can be used in submission is set out in section 211 of the Ngāi Tahu ClaimsSettlement Act 1998. Pursuant to section 211:

Te Rūnanga o Ngāi Tahu and any member of Ngāi Tahu Whānui may cite the relevant statutoryacknowledgement in submission to, and in proceedings before a consent authority or the EnvironmentCourt concerning activities within, adjacent to, or impacting directly on a statutory area as evidenceof Ngāi Tahu’s association with the statutory area.

The content of the association, as recorded in a statutory acknowledgement, is not by virtue of thestatutory acknowledgment binding as deemed fact upon consent authorities, the Environment Court,parties to proceedings before those bodies, or any other person able to participate in thoseproceedings, but the statutory acknowledgement may be taken into account by them.

Neither Te Rūnanga o Ngāi Tahu nor any member of Ngāi Tahu Whānui is precluded from statingthat Ngāi Tahu has any association with the statutory area not described in the relevant statutoryacknowledgment, nor does the content or existence of the statutory acknowledgement derogate fromany such statement.



Purpose of statutory acknowledgements

Pursuant to section 215, and without limiting section 216-219 of the Ngāi Tahu Claims Settlement Act 1998 thepurposes of statutory acknowledgements are:

1. To require that consent authorities forward summaries of resource consent applications to Te Rūnangao Ngāi Tahu, as required by regulations made pursuant to section 207; and

2. To require that consent authorities, the Historic Places Trust, or the Environment Court, as the case maybe, have regard to the statutory acknowledgements in relation to the statutory areas, as provided insection 208 to 210; and

3. To empower the Minister of the Crown responsible for management of the statutory areas, or theCommissioner of Crown Lands, as the case may be, to enter into deeds of recognition, as provided insection 212; and

4. To enable Te Rūnanga o Ngāi Tahu and any member of Ngāi Tahu Whānui to cite statutoryacknowledgements as evidence of the association of Ngāi Tahu to the statutory areas, as provided insection 211.

Limitations on effect of statutory acknowledgements

1. These statutory acknowledgements do not affect, and are not to be taken into account in, the exerciseof power, duty, or function by any person or entity under any statute, regulation, or bylaw; and

2. without limiting paragraph 1, no person or entity, in considering any matter or making any decision orrecommendation under the statute, regulation, or bylaw, may give any greater or lesser weight to NgāiTahu’s association with these areas (as described in the statutory acknowledgements) that that personor entity would give under the relevant statute, regulation, or bylaw, if these statutory acknowledgementdid not exist.

Except as expressly provided in this Act, these statutory acknowledgements do not affect the lawful rights orinterests of any person who is not a party to the deed of settlement. Except as expressly provided for in thisAct, these statutory acknowledgements do not, of themselves, have the effect of granting, creating, or providingevidence of any estate or interest in, or any rights of any kind whatsoever relating to these statutoryacknowledgement areas.

Coastal marine area statutory acknowledgements

There are also two statutory acknowledgments within the Canterbury Region in the Coastal Marine Area. Theseare Te Tai o Marokura (Kaikōura Coastal Marine Area) and Te Tai o Mahaanui (Banks Peninsula Coastal MarineArea).






9 Clean Air Zone Map Series



¥1

¥71

Rangiora

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District Planning ZonesBusiness Zone

Residential Zone

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¥71

¥1

Mabers Road

Old N

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Lords Road

Pa Road

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Jelfs

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State Highway 1

Ferry Road

Sney

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Millbrook Lane

Camwell Park

Millcroft Lane

Harbour Road

Fuller Street

Lords Road

Hilton Street

Courtenay Drive

Wood

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Cox Road

Dunns Aven ue

Bayliss Drive

Tuahiwi Road

Earlham Street

Smith Street

Sutherland Drive

Main

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Easterbrook Road

Ohoka Road

Mulcock

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Threlkelds Road

Paisley Road

Charles Street

Cass Street

Sewell Street

Adderley Terrace

Neeves Road

Power Road

Bramley

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Doub

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Heywards

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Raven Quay

Flaxton Road

Skewbridge Road

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Main North Road

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Lees Road

Giles

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Beach Road

South Eyre Road

Kainga Road

Clifford Road

Ferry R

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Christchurch Northern Motorway

Island

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Chris

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Lineside Road

Main Drain Road

State Highway 71

Willia

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Mill Road

Tram RoadStyx River

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Airsheds


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¥74A

¥74

¥75

¥73

¥73A

¥1

¥1

Waimakariri River

Avon River/Otak aro

Otukaik ino Creek

Halswell River

Heathcote River

Styx River

Hei Hei

Burnside

Ilam

Addington

Saint Albans

Shirley

Avonside

New Brighton

South New Brighton

Redcliffs

W oolstonSaint MartinsSouthshore

Scarborough

Broom field

Islington

Russley

CasebrookRedwood

Mairehau

Richm ond

Heathcote ValleyHalswell

Sockburn

Avonhead

Upper RiccartonRiccarton

Papanui

Dallington

Linwood

Aranui

North New BrightonW aim airi Beach

Harewood Park lands

HillsboroughSom erfield

Sydenham

Cashm ere

Hillm orton

Oak landsHoon Hay

Middleton

Fendalton

Bryndwr

Bishopdale

W ainoni

Burwood

Avondale

Brom ley

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¥79

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High Street

Fo rest RoadWalle

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Tiplady Road

Waihi

Terrac

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George Street

Totara Street

Tripp Street

Sherratt Road

Gale Cutting Road

Huffey Street

Kennedy Street

Rib

bonwood Road

Connolly Street

Shaw Road

Wilso

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Gale Cutting Road

Martin Road

Peel

Stree

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Hislop StreetWoodb uryRoad

Pye Road

Guilford Road

McKenzie Street

Templer Street

Te Moana Road

Kalaugher Road

Sercombe Road

Cox S

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Wait

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Geraldine-Fairlie HighwayMain North Road

Bennett Road

Talbot StreetGreenvale Road

Orari Station Road

Pleasant Valley Road

Downs Road

Orari Back Road

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Geraldine



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Geraldine/ Raukapuka Clean AirZone



¥78

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Wa shd ykeLag oo n

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Gleniti

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Watlington

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Waimataitai

Parkside

Maori Hill

Marchwiel

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Glenwood

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Timaru / Te Tihi-o-Maru Clean AirZone



¥82

Maude Street

Durham Street

Creek Road

Michael

Street

George Street

Tennant Street

Courts R

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Moores Road

Browns

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James Street

Manse Street

Dobson Street

Augustine Street

Taylors Road

Hillary Street

Exeter Street

Studhol

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Paul Stree

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Princes

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Carlisle Street

Manchester StreetOpie

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John S

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Edinburgh Street

Norto

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Cashel Street

Racecourse Road

Wilkin Street

Oxford StreetRegent Street

Champions Road

Hannifins Road

Harris S

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Gorge

Roa

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Allan Stree

tKing

StreetHunt

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Hodges Road

William Street

Belt Stree

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Mt John Road

Rhodes

Street

Slaughteryard Road

Shearman

Street

Bathgates Road

Bakers Road

Painstown Road

Horgans

Road

Park Road

Hakataramea Highway

Whitneys Road

Manchesters Road

Fitzmaurice Road

Garlands Road

Waihao Back Road

Queen S

treet

Point Bush Road

Parsonage Road

McNamaras Road

Molloys Road

Mill Road

Maytown Road

Timaru Road

High StreetState

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Waimate / Waimatemate Clean AirZone



10 Canterbury Airsheds



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Ellis Road

Townsend Road

Kinley Street

B al la

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Buckleys Road

Papawai Drive

Rata Street

Kotare Avenue

Cones Road

Ashgrove Street

Queen Street

Oa kg rove Drive

PalmviewDrive

Edward Stree t

Millton Avenue

Railway Road

Belmont Avenue

Youngs RoadDurham Street

Hunti

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Pentecost Road

Bush Street

Brick Kiln Road

Ayers Street

Ivory Street

Charles Upham Drive

Enverton Drive

Kensington Avenue

Good Street

Watkins Drive

Newnham StreetTodds R

oad

Oakwood Drive

Charles Street

Acacia Avenue

White Street

Easterbrook Road

March

mont R

oad

Church Street

Kippenberger Avenue

Blackett Street

Kingsbury Avenue

Smart

s Roa

d

Mountvista Road

Flaxton Road

State Highway 71

Priors Road Golf Links RoadSouth Belt

Rangiora Woodend Road

Percival Street

Lineside Road

High Street

Camside Ro ad

Ashley StreetMerton Road

Marsh Road

Northbrook Road

King Street

River RoadWest Belt

East Belt

Boys Road

Oxford Road

Plaskett Road

Coldstream Road

Lehmans Road

Fernside Road

Johns Road

Rangiora

Z:\PET\Air_plan_Working\Airsheds_MB_A4L_160203.mxd0 1 2 3 4 5 60.5

Kilometres

G a z e t t e d R a n g i o r a A i r s h e d

%2 Air Quality Monitoring site

/

Service Layer Credits: Land Information NewZealand, Eagle Technology

Rangiora Airshed



%2

¥71

¥1

Cam Road

Moor e

Stree

t

Davie Street

Dale Street

Store

r Stre

et

Old N

orth R

oad

Barnard Street

Doubled

aysRoad

Belcher Street

Vickery Street

Ranfu

rly St

reet

Feldwick Drive

Mulcock

s Roa

d

Perak

i Stre

et

Akaro

a Stre

etWesle

y Stre

et

Isaac Wilson Road

Otak

i Stre

et

Sovereign Boulevard

Sney

d Stre

et

Main No

rth Ro

ad

Main Drain Road

Robe

rt Cou

p Roa

d

Baylis s DriveSuther la nd Drive

Skewbridge Road

Fairweather Crescent

Fuller Street

Hilton Street

Courten

ayDri

ve

Smith Street

Beachvale Drive

Silver

stream

Boulevard

Ohoka Road

Neeves Road

State Highway 1

Mood

ys Ro

ad Charles Street

Cass Street

Sewell Street

Adderley Terrace

Butchers Road

Lees Road

Ferry

Road

Mill Road

Reve

lls Ro

ad

Raven QuayLo

werC

amsi d

e Ro a

d

G iles

Road

Lineside Road

Beach Road

State Highway 71

Clifford Road

Island

Roa

d

Chris

tchurc

h Nort

hern

Motor

way Wi

l li am s

S tree

t

Kaiapoi

Z:\PET\Air_plan_Working\Airsheds_MB_A4L_160203.mxd0 1 2 3 4 50.5

Kilometres

G a z e t t e d K a i a p o i A i r s h e d


/


Kaiapoi Airshed



%2

%2

%2

%2

¥1

¥74A

¥74

¥75

¥73

¥73A

Waimakariri River

Avon River/Otakaro

Otukaikino Creek

Halswell River

Heathcote River

Styx River

Sockburn

Avonhead

Upper RiccartonRiccarton

Papanui

Merivale Dallington

Linwood

Aranui

North New Brighton

Waimairi Beach

Harewood Parklands

Mount PleasantHillsboroughHuntsbury

Somerfield

Sydenham

Cashmere

Hillmorton

OaklandsHoon Hay

Hei Hei

Burnside

Ilam

Addington

Shirley

Avonside

New Brighton

South New Brighton

Saint MartinsSouthshore

Scarborough

Middleton

Fendalton

Bryndwr

Bishopdale

Wainoni

Burwood

Avondale

Bromley

Spreydon

Hornby

Cracroft

Broomfield

Islington

Russley

CasebrookRedwood

Mairehau

Richmond

Heathcote ValleyHalswell

Lyttelton

Diamond Harbour

Z:\PET\Air_plan_Working\Airsheds_MB_A4L_160203.mxd0 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 310.5

Kilometres

G a z e t t e d C h r i s t c h u r c h A i r s h e d


/


Christchurch Airshed



%2%2¥1

¥77

Leeston Street

Clark Street

McGr

ath Ro

ad

Gray

burn

Road

Burnett Street

Victoria Street

George Street

Beach Road

Park Stree

t

River Terrace

JB Cullen Drive

Pages Road

Carters Road

Fords

Roa

d

Rem i

ngton

sRo a

d

Wills Street

Havelock Street

Walnut Avenue

Oxford Street

Timaru Track Road

Grove Farm

RoadElizabeth Street

Taits Road

Glassworks Road

Belt Road

Creek Road

Eton Street

Johnstone Street

Cass Street

Farm Road

Company Road

Albert Street

Thews Road

Carters Terrace

Alford Forest Road

Tarbottons Road

Grahams Road

McMurdo Street

Allens Road

Grove Stree

t

Harrison Street

Bremners Road

Hinds Highway

Trevors R

oadWilliam Street

Maronan Road

Hendersons Road

Chalmers Avenue

Middle Road

Smithfield Road

Bridge Street

Thomson StreetFrasers Road

Melcombe Street

Wilkins Road

Seafield Road

Archibald

Street

East Stree

tWest S

treet

Hollands Road

Racecourse Road

Rakaia Highway

Milton Road SouthBeach Road East

Tinwald Westerfield Mayfield Road

Wakanui Road

State Highway 77

State Highway 1

Netherby

Hampstead

Allenton

ASHBURTON

Tinwald

Z:\PET\Air_plan_Working\Airsheds_MB_A4L_160203.mxd0 1 2 3 4 5 6 7 80.5

Kilometres

G a z e t t e d A s h b u r t o n A i r s h e d


/


Ashburton Airshed



%2%2

¥79

Burke Road

Davie

s Stre

et

Jollie Street

Main

North

Roa

d

Majors Road

Darby Street

Craig Road

High Street

Tancred Street

Forest Road

Templer Street

Walle

r Roa

d

Maling Street

Campbell Street

Waihi

Ter ra

ce

Martin Road

Tiplady Road

George StreetTotara StreetPekapeka Lane

Gale Cutting Road

Waitu

i Driv

e

Guilford Road

Tripp Street

Huffey Street

Kennedy Street

Ribbonwood Road

Connolly Street

Wilso

n Stre

et

Peel

Stree

t


Hislop Street

Orari

Back

Roa

d

Pye Road

McKenzie Street

Cox S

treet

Geraldine-Fairlie Highway

Downs Road

Talbot Street

Orari Station Road

Greenvale Road

State

High

way 7

9

Geraldine

Z:\PET\Air_plan_Working\Airsheds_MB_A4L_160203.mxd0 1 2 3 40.5

Kilometres

G a z e t t e d G e r a l d i n e A i r s h e d


/


Geraldine Airshed



%2

WashdykeLagoon

¥1

¥8

Kelvin StreetTyne Street

Cartwrights Road

Sheffield Street

Kent Street

Selwyn Street

Grants Road

Morga

ns R

oad MacDonald Street

Lindsay StreetAndrew Street

Luxmoore Road

Jellicoe Street

Timaru

-Tem u

kaHig

hway

Pleasant Point Highway

Racecourse Road

Old North Road

EvansStr

eet

Aorangi Road

Kellands Hill Road

Pages Road

Sead

own R

oad

State Highway 8

Washdyke Flat Road

Mead

ows R

oad

Hilton

Highw

ay

State Highway 1

Waimataitai

Marchwiel

Washdyke

Grantlea

Puhuka

Z:\PET\Air_plan_Working\Airsheds_MB_A4L_160203.mxd0 1 2 3 4 50.5

Kilometres

G a z e t t e d W a s h d y k e A i r s h e d


/


Washdyke Airshed



%2

%2

WashdykeLagoon

¥78

¥1

Marin

e Para

de

Brookfield Road

Parade

Park

L ane

Sefton Street

Tawa Street

Kent Street

Hayes Street

Poplar S treet

Fraser Street

Quarry Road

Rose

Stree

t

H ilton

High

way

Queen Street

Grants RoadLindsay Street

College Road

Andrew Street

Victor

iaSt r

eet

Jellicoe Street

Domain Avenue

Coonoor Road

Pudje

ck Road

Arthur Street

Orbell Street

Old N

orth R

oad

Craig ie Avenue

Hassall Street

High Street

Kellands Hill Road

Stafford StreetSouth StreetRockdale Road

Oakwood Road

Douglas Street

Morga

n sRo

a d

Mountai

n Vie w

Road

Timaru-Pare oraHighway

Selwyn Street

Sutto

n Roa

d King Street

Adair Road

Church Street

Rocky Hundreds Road

North Street

Claremont Road

Barto

n Roa

d

Evans Street

Gleniti Road

Beaconsfield Road

Otipua Road

Wai-Iti Road

Pages Road

Fairview Road

Landsborough Road

StateHig

hwa y

1

Gleniti

Kensington

Watlington

Highfield

Waimataitai

SeaviewWest End

Glenwood

Grantlea

Maori Hill

Marchwiel

Z:\PET\Air_plan_Working\Airsheds_MB_A4L_160203.mxd0 1 2 3 4 5 6 7 80.5

Kilometres

G a z e t t e d T i m a r u A i r s h e d


/


Timaru Airshed



%2

%2¥82

Maude Street

Town B

elt

Wall Stree

t

Milford StreetBro

wns Road

Victori

a Stree

t

Herbert

Street

Smith

Street

Coronation Street

Cameron Street

Leonard Street

Creek RoadSettlement Road

Butche

rs Lane

Michael

Street

George Street

Tennant StreetInn

es Stree

tMcNamaras Road

Naylor S

treet

Manse Street

Dobson Street

Augustine Street

Hillary Street

Molloys

Road

Exeter Street

Maytown Road

Moorhou

se Stree

t

Studho

lme Stree

t

Paul Stree

t

Princes

Street

Carlisle Street

Manchester Street

Fitzmaurice Road

Opie Stree

t

Mt John Road

John S

treet

Edinburgh Street

Cashel Street

Racecourse RoadWilkin Street

Waihao Back Road


Hannifins Road

Harris S

treet

Gorge

Roa

d

Allan S

treetHunt

s Road

King S

treet

Garlands Road

William Street

Belt Stree

tRhod

es Stree

t

Painstown Road

Shearman

Street

Park R

oad

Timaru Road

Parsonage Road

Point Bush Road Queen S

treet

Mill Road

High Street

State Highway 82

Waimate

Z:\PET\Air_plan_Working\Airsheds_MB_A4L_160203.mxd0 1 2 30.5

Kilometres

G a z e t t e d W a i m a t e A i r s h e d


/


Waimate Airshed



11 Crop Residue Burning Buffer Area Map Series



¥77

¥1

Land Information New Zealand, Eagle TechnologyLand Information NewZealand, Eagle Technology


\\gisdata\ProjectArchive\PET\2014_2015\Air_Plan_140324\Proposed_150115\Proposed_Crop_Burning_Areas_MB_A4L_150216.mxd0 2 4 6 8 10 12 14 16 18 20 22 24 26 28 30

Kilometres

A s h b u r t o n / H a k a t e r e C r o p R e s i d u e B u r n i n g B u f f e r A r e a

/

Ashburton / Hakatere Crop ResidueBurning Buffer Area


Residential Zone



¥78

¥1

¥8

Land Information New Zealand, Eagle TechnologyLand Information NewZealand, Eagle Technology


\\gisdata\ProjectArchive\PET\2014_2015\Air_Plan_140324\Proposed_150115\Proposed_Crop_Burning_Areas_MB_A4L_150216.mxd0 2 4 6 8 10 12 14 16 18 20 22 24 26 28 30 32

Kilometres

T i m a r u / T e T i h i - o - M a r u C r o p R e s i d u e B u r n i n g B u f f e r A r e a

/

Timaru / Te Tihi-o-Maru CropResidue Burning Buffer Area


Residential Zone



12 Canterbury Air Regional Plan General Map Series



TIMARU

CHRISTCHURCH

1714 15 16

11 12 138 9 10

6 754

2 31

23 24 2520 21 22

18 19

26 27 28

29

34 3532 3330 31

36 37

38

1450000

1450000

1500000

1500000

1550000

1550000

1600000

1600000

5050

000

5050

000

5100

000

5100

000

5150

000

5150

000

5200

000

5200

000

CANTERBURY AIR REGIONAL PLANMap Series

MAPINDEXCanterbury Air Regional Plan

Map Series

CANTERBURY AIR REGIONAL PLANMap Series

Scale 1:700,000(on A3 Page)

Ref

eren

ce ¯

\\gisdata\Projects\PET\Air_Plan_160201\Proposed_160301\Air_Plan_Index_A3L_20170714.mxd

0 10 20 30 40 505 Km

Basedata

Local Authority Inland BoundaryOpen River BedLand Parcel Boundaries

State Highways

Clean Air ZonesAirshedsCrop Residue Burning Buffer Area

District Planning ZonesBusiness ZoneCultural ZoneResidential Zone



C a n t e r b u r yR e g i o n

Hu r un u i D i s

t r ic t

Wa ima k a r i r

i D i st r i

c t

Round Hill Road

Henrys Ford Road

Downs Road

Bairds Road

Ramsay Road

Carbo

ys Road

Purple Heights RoadCanterbury Street

Courtney Road

Te Puke Road

Stony Creek Road

Gorries

Road

Fletchers Road

River Road

Toom

ebrid

ge R

oad Dunlops Road

Mowatts Road

Barro

n Ave

nueRossiters Road

Thomson Road

Hodgsons Road

Nicol Road

Copples Road

Wallers R

oad

Thomson Road

Doyles R

oad

Fawcetts Road

Rangiora Leithfield Road

Barkers Road

Beatties Road

Lawrence Road

Upper Sefton Road

Cones Road

Douds Road

Lower Sefton Road

Forestry Road

Mount Grey Road

Boun

dary

Road

Dixons Road

Loburn Whiterock Road

Carrs Road

Marsh

mans

Road

Shaw Creek

Stony Creek

MakerikeriRiver

Ashley

Loburn

Rangiora CleanAir Zone

1562000

1562000

1564000

1564000

1566000

1566000

1568000

1568000

1570000

1570000

5210

000

5210

000

5212

000

5212

000

5214

000

5214

000

2 354

1

MAP Canterbury Air Regional Plan

Re

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¯(on A3 Page)

\\gisdata\Projects\PET\Air_Plan_160201\Proposed_160301\Air_Plan_Left_MB_A3L_20170714.mxd

1Canterbury Air Regional Plan 0 200 400 600 800Metres


1:25,000

BasedataLocal Authority Inland BoundaryState Highways

Land Parcel BoundariesOpen River Bed

AirshedsClean Air Zones





¥71

Ellis Road

Green Str eet

Townsend Road

Kinley Street

George Street

Galatos Street

Balla

rat R

oad

Buckleys Road

Papawai Drive

Rata Street

Martyn Street

Rowse Street

Kotare Avenue

Boundary Road

Easterbrook RoadAshgrove Street

Queen Street

Oakgrove Drive

PalmviewDrive

State Highway 71

Edward Street

Elm DriveRailway Road

Belmont Avenue

Flaxton Road

Durham Street

Mairaki Road

Huntin

gdon Drive

Pentecost Road

Bush Street

Koura Drive

Millton Avenue

Ayers StreetWhite Street

Ivory Street

C harles UphamDrive

Enverton Drive

Kensington Avenue

Good Street

Watkins Drive

Newnham Street

Rangiora Woodend RoadLineside Road

Victoria Street

Todds Road

Oakwood Drive

Charles Street

Mount Thomas Road

Acacia Avenue

White Street

Lower Sefton Road

March

mont

Road

Church Street

Blackett Street

Kingsbury Avenue

ConesRoad

Golf Links Road

South Belt

Bridge Road

Percival StreetHigh Street

Ashley Street

Marsh Road

Boys Road

Merton Road

O'Roarkes Road

Northbrook RoadKing Street

River Road

West Belt

Plaskett Road

Coldstream Road

East Belt

Lilly Road

Swannano

a Road

Mount Thomas Road

Fernside Road

Dalziels Road

Lehmans Road

Priors Road

Johns Road

Oxford Road

AshleyRiver/Rakahuri

MakerikeriRiver

South Brook

North BrookFernside

Coldstream

Rangiora

Southbrook

RangioraAirshed


1560000

1560000

1562000

1562000

1564000

1564000

1566000

1566000

1568000

1568000

5204

000

5204

000

5206

000

5206

000

5208

000

5208

000

1

4

3

5

2


Re

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\\gisdata\Projects\PET\Air_Plan_160201\Proposed_160301\Air_Plan_Right_MB_A3L_20170714.mxd

Map Series 0 200 400 600 800Metres

1:25,000

MAP2

CanterburyAirRegional Plan




Airsheds

Clean Air Zones





¥1

Wai

ma k

a ri r

i Di s

t ri c

t

Allin Drive

GibbsDrive

Marsh Road

Welsford Street

Waiora Lane

Tahuna Street

Judsons Road

Harris Road

Stokes Road

Waikoruru Road

Greens Road

Aroh

a Stre

etLa

kesid

e Driv

e

Preeces Road

Whakatipu Street

Gateh

ouse

Lane

Queens Avenue

Te Pouapatuki Road

Hewitts Road

Copp

er Be

ech R

oad

Tutaipatu Avenue

Park

Terra

ce

Tutaipatu Avenue

Hakatere Road

Kings Avenue

Parsonage Road

Eders Road

Arah

uraRo

ad

TeKo

hang

aDriv

eKawa

ri Driv

e

Te Hurunui Drive

Coldstream Road

Boys Road

Topito Road

Okaihau Road

Petries Road

Wards Road

Pegasus Main S tr eet

Legg

itts R

oad

Turiwhaia Road

Camside Road

Infinity Drive

Cams

ideRo

ad

Tiritiri Moana DriveCh

innery

s Roa

d

Maple

ham

Drive

Pegasus Boulevard

Waikuku Beach RoadSm

arts R

oad

Kaiapoi

Pa Road

Tuahiwi Road

Gladstone Road

Gressons Road

Tulls Road

Rangiora Woodend Road

StateHigh

way1

Main North

Road

CamRiver/Ruataniwha

TūtaepatuLagoon

WaikukuStream

Waikuku Beach

Woodend

Waikuku

Pegasus


1570000

1570000

1572000

1572000

1574000

1574000

1576000

1576000

1578000

1578000

5204

000

5204

000

5206

000

5206

000

5208

000

5208

000

1

2

4 56 7

3


Re

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1:25,000








¥71

Siena PlaceAschens Road

Dawsons Road

Keetly Pl ace

Truro Close

Warwick Road Velino Place

Whites R

oad

Tristram Road

Modena Place

Egans Road

Mandeville Road

Power Road

Millbrook Lane

Verona PlaceRoscrea Place

Dawsons Road

Camwell Park

Clear View Lane

Vicenza Drive

Millcroft Lane

O'Roarkes Road

Mand

alea R

oad

Youngs Road

Butchers Road

Two C

hain R

oad

Jeffs D

rain R

oad

Mulcock

s Road

Threlkelds Road

Barkers Road

Paisley Road

McRo

berts

Road

McHughs Road

Radde

ns Ro

ad

Plaskett Road

Cullen Avenue

Pattersons Road

Skewbridge Road

Mountvista Road

Jackso

ns Ro

ad

Easterbrook Road

Fernside Road

State Highway 71

Lineside Road

Ashworths RoadFlaxton Road

Hicklands Road

Wards Road

No 10 Road

Tram Road

Bradleys Road

Mill Road

Main Drain Road

Ohoka Stream

MandevilleNorth

Ohoka

Wetheral

WilsonsSiding


KaiapoiClean

Air Zone

1560000

1560000

1562000

1562000

1564000

1564000

1566000

1566000

1568000

1568000

5198

000

5198

000

5200

000

5200

000

5202

000

5202

000

5

2

6

3

7

4


Re

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1:25,000

MAP4





Airsheds

Clean Air Zones





¥71

¥1

Wai

mak

ari r

i Di s

t ri c

t

Davie Street

Dale Street

Storer

Stree

t

Old N

orth R

oad

Barnard Street

Barke

rs Road

Perak

i Stre

et

Main Drain Road

Ferry RoadAkaro

a Stre

et

Church Bush Road

Youngs Road

Ranfu

rly St

reet

Skewbridge RoadFel

dwick Drive

Pa Road

Wesle

y Stre

et

Camside Road

StateHighway 1

Otak

i Stre

et

Te Pouapatuki Road

Ferry

Roa

d

Sand

hill R

oad

Sovereign Boulevard

Giles Road

Sney

d Stre

et

Charles Street

Sand

hill R

oad

Topito Road

Fuller StreetHilton Street

Dunns Avenue

Cox Road

Power Road

Baylis

s Driv

e

Smith Street

Sutherland Drive

Fullers Road

Raven Quay

Beachvale Drive

Silve

rstream

Boulevard

State

Highw

ay 1

Butch

ers R

oad

Cass Street

Sewell Street

Jelfs RoadMill Road

Gree

nsRo

ad

Island Road

Tuahiwi Road

Bramley

s Road

Main

North

Roa

d

Lowe

r Cam

side R

oadReve

lls Ro

ad

Lees Road

Lineside RoadState Highway 71

Beach Road

Clifford Road

Woodend Beach Road

Ferry R

oad

Willia

msStr

eet

Chris

tchurc

h Nort

hern

Motor

way

Kaiapoi River

CamRiver/Ruataniwha

Kairaki Creek

Woodend Beach

Tuahiwi

Flaxton

The PinesBeach

Ohapuku

KairakiKaiapoi

KaiapoiAirshed

RangioraClean

Air Zone

Kaiapoi CleanAir Zone

1570000

1570000

1572000

1572000

1574000

1574000

1576000

1576000

1578000

1578000

5198

000

5198

000

5200

000

5200

000

5202

000

5202

000

32

4

6 7

1

9 108

5


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1:25,000








Wa i m a k a r i r i D i s t r i c t

C h r i s t c h u r c h C i t y

Whites R

oad

Harrs

Roa

d

Elders Road

Lorimas RoadMabers Road

Lords Road

Madeleys Road

Jackso

ns Ro

ad

Hamp

tonDr

iveNo

rris D

rive

McHughs R

oad

Clothiers Road

Leyla

nd Cr

esce

nt

West

Denb

ieLa

ne

Harpers Road

Taylors Road

Diversion Road

Radde

ns Ro

ad

Mood

ysRo

ad

Wood

s Roa

d Gardiners Road

Pashbys Road

Chiltons R

oad

Eyre Main Drain Road

Jeffs D

rain R

oad

Giles Road

Baynons Road

Edmunds Road

Moffatts Road

Diversion Road

Lords Road

Burge

sses R

oad

Driscolls Road

Baileys Road

No 10 Road

Coutts Island Road

North Eyre Road

Mandeville Road

Heywards Road

Tram Road

South Eyre Road

WaimakaririRiver

Eyre RiverDiversion

Kaiapoi River

Old BedEyre River

Old BedEyre River

Eyre MainDrain

Eyreton

KaiapoiCleanAir Zone

Christchurch/ Ōtautahi

Clean Air Zone

1560000

1560000

1562000

1562000

1564000

1564000

1566000

1566000

1568000

1568000

5192

000

5192

000

5194

000

5194

000

5196

000

5196

000

8

54

9

7

10

6


Re

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¯(on A3 Page)



1:25,000

MAP6





Airsheds

Clean Air Zones





¥1

Wa i ma k a r i r

i D i s t r ic t

C h r i st c

h u r ch

C i t y

Chri s tc hu rchC it y

Ferry Road

State Highway 1

Sewell Street

Watts

Road

Belcher Street

Vickery Street

Mood

ys Ro

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Isaac Wilson Road

Charles Street

StateHigh

way1

Robe

rt Cou

p Roa

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Farrells Road

Marshland Road

Fairweather Crescent

Willia

ms St

reet

Harbour Road

Raven Quay

Courtenay Drive

Turne

rs Ro

ad

Ohoka Road

Earlham Street

Heyders Road

Giles

Road

Dickeys Road

Neeves Road

Doub

leday

s Roa

d

Coutts Island Road

Tram Road

Island

Roa

d

Greigs Road

Christ

churc

h Nort

hern

Motor

way

Spencerville Road

Kainga Road

Christchurch Northern Motorway

Lower Styx Road

Main

North

R oad

Bottle LakeForest

ChaneysPlantation

CourtenayStream

Kaiapoi River

WaimakaririRiver

OtukaikinoCreek

BrooklandsLagoon

Styx River

KaikainuiStream

Bridgend

Brooklands

Kainga

StewartsGully

Chaneys

Spencerville

Clarkville

CouttsIsland

ChristchurchAirshed

ChristchurchAirshed

KaiapoiAirshed

Kaiapoi CleanAir Zone


Clean Air Zone

1570000

1570000

1572000

1572000

1574000

1574000

1576000

1576000

1578000

1578000

5192

000

5192

000

5194

000

5194

000

5196

000

5196

000

54

6

9 10

2 3

1312811

7


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1:25,000








W a i m a k a r i r i D i s t r i c tC h r i s t c h u r c h C i t y

Chr i

s tc h

u rc h

Ci t

y

S el w

y n D

i st r

i ct

Mine

rs Ro

ad

Two C

hain R

oad

School Road

Weed

ons R

oss R

oad

Clarks

ons R

oad

Conservators Road

Chatt

erton

s Roa

d

McLeans Island Road

McLeansIsland

ChristchurchAirshed


Clean Air Zone

1552000

1552000

1554000

1554000

1556000

1556000

1558000

1558000

1560000

1560000

5186

000

5186

000

5188

000

5188

000

5190

000

5190

000

6

9

11 12

8


Re

fere

nce

¯(on A3 Page)



1:25,000

MAP8





Airsheds

Clean Air Zones





¥74

¥1Shipleys RoadBroughs Road

Sefto

n Stre

et

Kilburn Street Sisson

Drive

Bainton Street

Uxbri

dge S

treet

Morriso

n Aven

ue

Norrie Street

Wilkinsons Road

Royd

vale

Aven

ue

Twyford Street

Dunedin Street

Traffo

rdStr

eet

Waterway Lane

Glenmore Avenue

O'NeillAv

enue

Becm

ead D

rive

Rotoit

i Lane

Perimeter Road

Groynes Drive

Prestons Road

Peter

Leem

ingRo

adWingate Street

Daniels Road

Isleworth RoadSk

yeda

leDr

ive

Jessons Road

Farquhars Road

Winters Road

Queen Elizabeth II Drive

Watson

s Roa

d

Tuckers RoadGlasne

vinDrive

Sturrocks Road

Barnes Road

Waimakariri Road

Cotsw

oldAv

enue

Crofto

n Roa

d

LowryAvenue

Englefield Road

Vagues Road

Beechwood Drive

Hoani Street

Woold

ridge

Roa

d

Stanle

ys R

oad

Regent's Park Drive

Aviatio

n Drive

Veitches Road

Logistics Drive

Farrington Avenue

Breen

s Roa

d

Cranford Street

Harts Creek Lane

Durey Road

Reynolds Avenue

Langdons Road

Clearwater Avenue

Sawyers Arms RoadSavills Road

Greers

Road

Northcote Road

Coutts Island Road

Northwood Boulevard

Claridges Road

Hussey Road

Russl

ey Ro

ad

Cave

ndi sh

Road

Orchard

Road

Pound Road

Styx Mill Road

Highst

ed Ro

ad

Wairakei Road

Gardi

ners

Road

Sawyers Arms Road

State

Highw

ay 74

Harewood Road

Main

North

Roa

d

McLeans Island Road

Johns

Road

State Highw

ay 1

WaimakaririRiver

Styx RiverCasebrook

Harewood

Bishopdale

Redwood

TemplersIslands

ChristchurchAirshed


Clean Air Zone

1560000

1560000

1562000

1562000

1564000

1564000

1566000

1566000

1568000

1568000

5186

000

5186

000

5188

000

5188

000

5190

000

5190

000

8

6 7

11 12

10

13

4 5

1514 16

9


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1:25,000








¥74

¥1

Chr is tc h u rc hC i t y

Jutland Street

Johns Road

Frosts Road

Guthries

Road

Richill Street

Selkirk Place

Forest Drive

Ashw

oodS

treet

Georgina Street

Eastwood Rise

Rushm

ore

Drive

Reka Street

Bower Avenue

Innes

Road

Hills R

oad FairwayDrive

Philp

otts R

oad

Willowview Drive

Ascot Avenue

Chartwell Street

Blake

s Roa

dBla

kes Ro

ad

Dunbarton Street

Lamorna Road

PuharaAve nu e

Thompsons Road

Quaids Road

Ruapani Street

Greenhaven Drive

Cottonwood Street

Lakewood Drive

McSaveneys Road

Putake Drive

Inwoo

ds Ro

ad

Tedder Avenue

Old Windsor Lane

Winters Road

Tyron

e Stre

et

Marine Parade

Metehau Street

Pacific Road

State

Highw

ay 74

EffinghamStreet

Walters Road

Guthr

ies Ro

ad

Factory Road

Broadhaven Avenue

Waitikiri Dri ve

Te Rito Street

Royal Park Drive

Quee

nspa

rkDr

ive

Turner

s Road

Te Korari Street

Bowe

r Ave

nue

Beach Road

Hawkins Road

Grim

seys

Roa

d

Travis Road

Aston Drive

State

Highw

ay 1

Burwood Road

Hills Road

Radcliffe Road

Belfast Road

Main N

orth R

oad

Rothesay Road

Mairehau Road

Lower Styx

Road

Prestons Road

Queen Elizabeth II Drive

Marshland Road

State Highway 74

Bottle LakeForest

QueenElizabeth

II Park

KaputoneCreek

Styx River

Parklands

Marshland

Belfast

WaimairiBeach

Ouruhia

ChristchurchAirshed

Christchurch /Ōtautahi CleanAir Zone

1570000

1570000

1572000

1572000

1574000

1574000

1576000

1576000

1578000

1578000

5186

000

5186

000

5188

000

5188

000

5190

000

5190

000

6

9

7

12 13

10


Re

fere

nce

¯(on A3 Page)



1:25,000

MAP10





Airsheds

Clean Air Zones





¥73A

¥73

¥1

Ch r i s t c h u r c h C i t y

S e l w y n D i s t r i c t

Amyes Road

Wilson Street

Hickory Place

Seymour Street

Paparua Drive

Corin

ga Ro

ad

Mortlake Street

Isling

to nAv

enue

Ivey Road

Kanie

reAven

ue

Shands RoadForemans Road

Leggett Road

Clarks

ons R

oad

Lawford Road

Carm

enRo

ad

Scarl

et Oa

k Driv

e

Hei H

ei Ro

adGr

ays R

oad

Jarnac

Boule

vard

Langdales Road

Gilbe

rthorp

es Ro

ad

Barters Road

Kettlewell Drive

Roberts Road

Yaldhurst Road

Guys

Road

Maddisons Road

Ryans Road

Jowers

Road

Curraghs Road

Main South Road

Miners Road

Chatt

erton

s Roa

d

Dawsons Road

Waterloo Road

State Highway 1

Kirk Road

Haske

tts Ro

ad

Newtons Road

School Road

Buchanans Road

Old West Coast Road

Poun

d Roa

d

West Coast RoadState Highway 73

Hei Hei

Yaldhurst

Islington

ChristchurchAirshed


Clean Air Zone

1554000

1554000

1556000

1556000

1558000

1558000

1560000

1560000

5180

000

5180

000

5182

000

5182

000

5184

000

5184

000

8 9

14

12

15

6

17

107

1311


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1:25,000







C a n t e r b u r y R e g i o n

¥1,73

¥73

¥73A

¥1

Otara Stree

tTika Street

Arts Road

Rata Street

Darvel Street

Grov

e Roa

d

Derby Street

Lyndon Street

Hewitts Road

Strowan Road

Dee Street

Pilkington Way

Worthy Street

Yardl

eyStr

eet

Andover Street

BalgayStreet

Whitby Street

Garvins Road

Hartley Avenue

Clare Road

Browns Road

Thames Street

Severn Street

Lunns Road

Holmwood Road

Nancy Avenue

Mary Street

Cable Street

Guildford Street

Lochee Road

Charl

cott S

treet Proctor Street

Truman Road

Deep

dale

Stree

t

Arthur Street

Ambleside Drive

Jennife

r Stree

t

Princess Street

Matsons

Avenue

Windermere Road

Hawthorne Street

Warrington Street

Grassmere Street

Wroxton Terrace

Oxford Terrac

e

Weka Street

Hudson Street

Flockton Street

Worcester Street

Kintyre Drive

Plynlimon Road

Harva

rdAv

enue

Montr

eal S

treet

Perry Street

English Street

Trafalgar Stre et

Mahars Road

Spring

s Road

Treffers Road

Gray

s Roa

d

Orbe

ll Stre

et

Carlton Mill Road

Ranfurly Street

Kirkwood Avenue

Tui S

treet

Ruskin Street

Brisb

ane S

treet

Forfar Street

HounslowS treet

University Drive

Toorak Avenue

Carlyle Street

Coleridge Street

Stead

man R

oad

Westholme Street

Brynley Street

Paparoa Street

Wai-Iti Terrace

Gray

s Roa

d

Brodie

Stree

t

Garreg Road

Wigram Road

Colman Avenue

Parkstone Avenue

Kotare Street

Solwa

y Aven

ueKahu Road

Ron G

uthrey

Road

Kellys Road

Cutts

Road

Hinau S

tr eet

Philpotts Road

Watford Street

Wairarap

a Terrac

e

Victoria Street

Neill Street

McFaddens Road

Bristol Street

Arco

nDriv

e

Francis Avenue

Norto

nsRo

ad

Harewood Road

MashamRoad

Tomes Road

Byron Street

Merivale LaneRugby Street

Hansons Lane

Staveley Street

Wainui Street

Grants Road

Caled

onian

Roa

d

Pack

e Stre

et

Sherb

orne S

treet

Middleton Road

Burke Street

Wharenui Road

Gass

on S

treetDisraeli Street

Kilmarnock Street

Malvern Street

Teesd

aleSt

reet

Leinster Road

Epsom Road

Chapter Street

Mandeville Street

St James Ave nue

Mersey Street

Parkhouse Road

Holly Road

Hagley Avenue

Normans Road

Madra

s Stre

et

Peer

Stree

t

Halwyn Drive

Vickerys Road

Chey

enne

Stree

t

Whiteleigh Avenue

Picton AvenueHarakeke Street

Park Terrace

Creyke Road

Heaton Street

Purchas Street

Canon Street

Bryndwr Road

Pu ri ri St reet

Walth

am R

oad

CorfeStreet

Mays Road

Clarence Street

Merrin StreetSt Albans Street

Wrights Road

McAlpine StreetBirmingham Drive

Suva Street

Hazeldean Road

Annex Road

Apsley Drive

Ryans Road

Woodbury Street

Cashel Street

Elizabeth StreetLichfield Street

Harper Avenue

Mooray Avenue

Strav

enRo

ad

Harris Crescent

Hamilton Avenue

Blighs Road

Totara

Street

Selw

yn St

reet

Edgeware Road

Wordsworth Street

Rutland Street

Roydval

e Aven

ue

Matipo Street

State Highway 73A

Midd

lepark

Road

Rossall Street

Syd Bradley RoadGeorge Bellew Road

Oxford Terrace

Peterborough Street

Springfield RoadJeffreys Road

Riccarton Avenue

Glandovey Road

Antig

ua S

treet

Lincoln Road

Kendal Avenue

Salisbury Street

Condell Avenue

Hayton Road

Kilmore Street

Peverel Street

Aorangi Road

Armagh Street

Hereford Street

Gloucester Street

Colom

bo St

reet

Durha

m St

reet S

outh

Hawth

ornde

n Roa

d

Barba

does

Stree

t

Dean

s Ave

nue

Tuam Street

Waterloo Road

Buchanans Road

Westmins

ter Stree

t

Carm

en Ro

ad

Bealey Avenue

Idris

Road

Colom

bo St

reet

Weston Road

Barba

does

Stree

t

St Asaph Street

Fendalton Road

Knowles Street

Montr

eal S

treetRacecourse Road

Madra

s Stre

et

Maidstone Road

Curletts RoadState Highway 73A

Brougham Street

Withe

lls Ro

ad

Cranford Street

Graham

s Road

Christchurch Southern Motorway

Innes Road

Greers R

oad

Moorhouse Avenue

Manc

heste

r Stre

et

Papanui Road

Waimairi Road

Riccarton Road

Russl

ey Ro

ad

Wairakei Road

Clyde

Roa

d

Ilam Road

Yaldhurst Road

Main South Road

Memorial Avenue

Blenheim Road

Avonhead Road

State Highway 76

State

Highw

ay 1

State Highway 73

SouthHagleyPark

NorthHagleyParkAlbert Lake

WaimairiStream

Ilam Stream

WairarapaStream

AvonRiver/Ōtakaro

OkeoverStream

Addington

Burnside

Ilam

Avonhead

Sockburn

St Albans

Russley

Riccarton

Merivale

UpperRiccarton

Papanui

Sockburn

Fendalton

Avonhead

Mairehau

Bryndwr

ChristchurchAirshed


Clean Air Zone

1562000

1562000

1564000

1564000

1566000

1566000

1568000

1568000

1570000

1570000

5180

000

5180

000

5182

000

5182

000

5184

000

5184

000

98

11

14 15

10

13

16

12


Re

fere

nce

¯(on A3 Page)



1:25,000

MAP12





Airsheds

Clean Air Zones





¥73

¥74

Ch r i s t ch u r c hC i t y

Tahuna

StreetBirch Street

Ryan

Stree

t

Raupo Stree

t

Avalon Street

Shuttle Drive Blake Street

Wyon Street

Dacre Street

Stevens Street

Seaview Road

Vogel Stre

et

Mundys Road

Doreen Street

Morris Street

Duna

ir Driv

e

Akaro

a Stree

t

Cowes Street

Chrys

tal St

reet

PattenStr

eet

London Street

Harrow Street

Matlock Street

Bayn

es St

reet

Bealey Avenue

Skipto

n Stree

t

Kilmore Street

Lichfield StreetWickham Street

Lan

dy Street

Cardr

o naS

treet

Cuffs Road

Marriotts Road

Hope Street

Dunarnan Street

Mathe

sons R

oad

Wildberry Street

Brook Street

Warrington Street

Edgeware Road

Edward Avenue

Robson Avenue

Fitzgerald Av en ue

Briarmont Street

Coopers Road

St Joh

ns Str

eet

Basingstoke Street

Mowbray Street

Chelsea

Street

Bexley Road

Barbo

ur Str

eet

Stour

Drive

Niven Street

Owles Terrace

Brisb

ane S

treet

Jollie S

treet

Pembro

keStr

eet

Golf Link sR oad

Charles Street

Achilles Street Wairoa Street

Atlantis Street

Burw

oodR

o ad

Woolley Street

Westmins

ter St

reet

Brougham Street

Beresford Street

North

Parad

e

Nurse

ry Ro

ad

Ensor

s Roa

d

Oram Avenue

Orrick Crescent

Ottawa Road

Risela

wStr

eet

Lonsda

le Stree

tQueensbury StreetAylesford Street

Mackw

orth S

treet

Hargood

Stree

t

Banks Avenue

Rand

olph S

treet

Avon

side D

rive

Pack

e Stre

et

Hawke Street

Innes Road

Cham

pion S

treet

B ass

ettSt r

eet

Bickerton Street

Willry

an Av

enue

Retreat Road

CarisbrookeStree

t

BrookerAvenueWa

ttle D

rive

Fleete Street

Eurek

a Stre

et

Warden Street

Shirley Road

Vivian

Stree

t

Ruru Road

Avon

dale

Road

Borde

sley S

treet

Marlow Road

WalthamR oad Tilf

ord St

reet

Rowses Road

Travis Road

Bake

r Stre

et

Waitaki Street

Ollivie

rs Ro

ad France

llaStreet

North Avon Road

Keighleys Road

Ruru Road

Wilso

ns Ro

ad No

rth Linwood Avenue

Kerrs

Roa

d

Tancre

d Stree

t

Moorhouse Avenue

McBratneys Road

Slater

Stree

t

Petrie

Stree

t

Smith

Stree

t

Briggs Road

Bowhill Road

Dallin

gton T

errac

e

Oxford

Terrace

Joy Street

Stapl eton s Road

Buckleys

Road

Aldwin

s Roa

d

Palm

ers R

oad

Bowe

r Ave

nue

Hay Stree

t

Wainoni

Road

Rocking Horse Road

Mace

s Roa

d

Bridge Street

Keyes Road

England

Street

Union

Stree

t

St Asaph Street

Hamp

shire

Street

Cuthberts Road

Horse

sho e

Lake

Road

Avons ide Drive

Kingsford Street

Geral

dine S

treet

Emme

tt Stre

et

Gayhurst Road

McG r

egors

Road

Fitzg

erald

Aven

ue

Armagh Street

Quinns Road

Tuam Street

Bexley Road

Marshland Road

Barba

does

Stree

t

Hulverstone Drive

Wainoni R

oad

Barba

does

Stree

t

Woodham Road

Stanm

ore R

oad

Shortland Street

Hereford Street

Estuary Road

Cashel Street

Locks

ley Av

enue

Lake Terrace Road

Pine Avenue

RiverRoad

Worcester Street

Hills

Road

Gloucester Street

Anzac Drive

Ferry RoadDy

ers Ro

ad

Pages Road

Breezes Road

State Highway 74

State

Highw

ay74Linwood Avenue

Avonside Drive Marine Parade

New Brighton Road

Te Huingi ManuWildlife Refuge

Dudley Creek AvonRiver/Ōtakaro

North New Brighton

Avondale

Avonside

Bexley

Wainoni

Southshore

Linwood

New Brighton

Burwood

Bromley

Shirley

Dallington

Aranui

South NewBrighton

Richmond

ChristchurchAirshed


1572000

1572000

1574000

1574000

1576000

1576000

1578000

1578000

1580000

1580000

5180

000

5180

000

5182

000

5182

000

5184

000

5184

000

9

12

15

10

1614

76

17

11 13


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fere

nce

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1:25,000








¥75

¥1



Stark Drive

Dix Street

Carrs Road

Neill Street

Owaka

Road

Oakle

y Drive

Barters Road

Carrs Road

Hinde

ss Str

eet

Skyhawk Road

Quadran

t Drive

Hickory Place

Winfield Drive

Hamill Road

Wroots Road

Witham Street

Lindsa

y Drive

Brigham Drive

Valia

nt Str

eet

Charwell Lane

Rich Terrace

Waipuna Road

Klondyke Drive Platinum Drive

Bennington Way

Cairnbrae Drive

Awatea Gardens

Boston Avenue

Leadleys Road

Wigram Road

Tongariro Street

Edmont

on Road

Gallagher Drive

Halsw

ellRo

ad

Farth

ingDr

ive

Westlake Drive

Meadowlands Road

Alameda Place

Bailey Street

Busch LaneAmyes Road

Seymour

Stree

t

Block

Road

Napier Drive

Roydon Drive

State Highway 76

Sioux Avenue

State

Highw

ay75

Ca ulfie ld Avenue

Dunbars Road

Kirk Road

Patterson Terrace

Richmond Avenue

Larcombs Road

Blankn

eySt

reet

Lodestar Avenue

Wilmers Road

Bran

ston S

treet

Wigram

Road

Foun

tains

Road

Maddisons Road

Sabys Road

Wales Street

State Highway 76Christchurch Southern Motorway

The Runway

Long

staf fs

Road

Bella

m Ro

ad

Aberdeen Road

Devine Drive

Cross Road

Downies Road

Corsair Drive

Ellesmere Road

Hodgens Road

Waterloo Road

Dawsons Road

Birchs Road

Awatea Road

Selwyn Road

Whinc

ops R

oad

Kittyh

awk Avenue

Quaifes Road

Jones Road

Tosswill Road

State Highway 76

Blakes Road

Trices Road

Robinsons Road

Trents Road

Water

holes

Road

State Highway 1

Main South Road

Marshs Road

Hamptons Road

Halswell Junction Road

Spring

s Road

Shand

s Road

Christchurch Southern Motorway HeathcoteRiver

NottinghamStream

KnightsStream

Prebbleton

Templeton

Hornby

Oaklands

ChristchurchAirshed


Clean Air Zone

1556000

1556000

1558000

1558000

1560000

1560000

1562000

1562000

1564000

1564000

5174

000

5174

000

5176

000

5176

000

5178

000

5178

000

11 12

15

17

13

14


Re

fere

nce

¯(on A3 Page)



1:25,000

MAP14





Airsheds

Clean Air Zones





¥73

¥74A

¥75

Ngaio Street

Mavin Road

The Runway

York

Stree

t

Kairos Street

Hurunui Street

Hinde

ss Str

eet

Fern Drive

Rahera Street

Rydal Street

Torrens Road

Redruth Avenue

Sandwich Road

Sonter Road

Nicholls Road

Victors Road

Wyn Street Curries Road

Martin Avenue

Norw

ood S

treet

McBeath Avenue

Tankerville Road

Stourbridge StreetWychbury S

treet

Beckford Road

Bengal Drive

Euph

rasie Drive

Ensig

n Stre

et

Sylvan Street

MacKenzie Avenue

Maunsell Street

Checketts Avenue

Hastings Street East

Ensor

s Roa

d

MuirAv

e nue

Balcairn Street

Grange Street

Frankleigh Stree

t

MacMillan Avenue

Coronation Street

Wales Street

Landsdowne Terrace

Longhu

rstTe

rrace

Samuel Street

Malcolm AvenueRoberta Drive

Bletsoe Avenue

Birdw

oodA

venu

e

Kaiwara Street

Hayton Road

State Highway 74ATennyson Street

Conway Street

Sullivan AvenueWaltham Road

Cobham Street

Fisher Avenue

King Street

Stanbury Avenue

Ravensdale Rise

Domain Terrace

Rowley Ave nue

Neville Street

Riverlaw Terrace

Cumn

orTe

r race

Albert

Terra

ce

Southampton Street

Huxley Street

St Martins Road

Ayns

leyTe

rrace

Annex Road

Kidson Terrace

Roker Street

Studholme Street

Palat

ineTe

rraceMathers R

oad

Halswell Junction Road

Dunbars Road Verno

n Terr

ace

Garlands Road

Edinburgh Street Radley

Street

Hollis

s Ave

nue

Somerfield Street

Saby

s Roa

d

Wilsons Road South

Bowenvale Avenue

Lincoln Road

Richards

onTer

race

Summit Road

McMaho

n Drive

Sutherlands Road

Strickland Street

Simeon Street

Shalamar Drive

Port Hills Road

Rose StreetBibiana Street

William

Britta

nAve

nue

Riverlaw Terrace

Warren Crescent

Waim

eaTe

rrace

Curletts Road

Milns Road

State Highway 76

Aidanfield Drive

Major AitkenDrive

Milton Street

Wigram Road

Penruddock

Rise

Selwyn Street

Hoon Hay Valley Road

Kennedys Bush Road

Colom

bo St

reet

Easte rn Terrace

Hendersons Road

Ashgrove Terrace

Hackthorne Road

Lyttelton Street

Christch

urchSouthern Motorway

State Highway 76

Opawa RoadFifield Terrace

Barrington StreetHoon Hay Road

Summ

it Roa

d

Huntsbury Avenue

Rapaki Road

Centaurus Road

Worsleys Road

Spark

s Road

Brougham Street

Dyers Pass Road

State Highway 76

Halsw

ell Ro

ad

Cashmere Road

State

Highw

ay 75

Victoria Park

HeathcoteRiver

Heathcote River

Cracroft

Hoon Hay

Somerfield

Saint Martins

Hillsborough

Huntsbury

Hillmorton

Woolston

Cashmere

Beckenham

Halswell

Waltham

Westmorland

Spreydon

Sydenham

Opawa

ChristchurchAirshed


1566000

1566000

1568000

1568000

1570000

1570000

1572000

1572000

1574000

1574000

5174

000

5174

000

5176

000

5176

000

5178

000

5178

000

14

12

17

13

16

1198 10

15


Re

fere

nce

¯(on A3 Page)




1:25,000








¥74

¥73

¥74A

Chr is t ch ur chC i t y

Days Road

State Highway 74

Dryden Street

Godle

y DriveHead

Street

Truro Street

Celia Street

Campbell Street

Ti Rakau Dr iv e

Laing Crescent

Augusta Street

Mauger Drive

Ross

Terrac

eCo

rnwall

Road

Arnold Street

Ferrymead Park Drive

Oxfor

d Stre

et

Bamford

Stree

t

Broad leaf Lane

Barton Street

Colenso Street

Scruttons Road

D yers

Road

State

Highw

ay 74

Wiggins Street

AvocaVall eyR oad

Rutherfo

rdStr

eet

Horot ane Valley Road

Flinders Road

H aw khurst Road Jacks

ons R

oad

Martindales Road

Humph reys D rive

Pano

rama Road

Chapmans Road

Rocking Horse Road

Somes Road

Cante

rbury

Stree

t

Beachville Road

Solea

resAv

enue

Ferry Road

Nayland Street

Esplanade

State Highway 76

Wake

field

Aven

ue

Ferry Road

State High

way74A

Glenst

raeRo

ad

Clifton Terrace

Richm

ond H

il l Roa

d

Sumner Road

Heberden

Avenue

Old Sumner Lyttelt

onRo

adEv

ans P

assRoad

Monck

s Spur

Road

Cumn

orTe

rrace

Major

Hornb

rook R

oad

Bridle Path

Captain ThomasRoad

Taylors Mistake Bay (Beach)

Bridle Path RoadPort Hills Road

Main Road

Mt Pl

easa

nt Ro

ad

Tunnel Road

Summit R

oad

FerrymeadPark

Jollies Bush

Harris Bay

Boulder Bay

McCormacksBay

Moncks Bay

Breeze BayLivingstoneBay

Estuary of theHeathcote and AvonRivers/Ihutai

HeathcoteValley

Ferrymead

Redcliffs

Scarborough

Te Onepoto/TaylorsMistake

MountPleasant

ChristchurchAirshed


Clean Air Zone


Clean Air Zone

1574000

1574000

1576000

1576000

1578000

1578000

1580000

1580000

1582000

1582000

5174

000

5174

000

5176

000

5176

000

5178

000

5178

000

15

13

17

12

16


Re

fere

nce

¯(on A3 Page)



1:25,000

MAP16





Airsheds

Clean Air Zones





¥75



Lighthouse Lane

Jetty Road

Sherw

oodRise

Osterholts Road

Rhodes Road

Meyer Road

Tancreds Road

Osborn Road

Hayes Road

Holmes Road

Allandale Lane

Leadleys Road

Main Road

Bamford

s Road

Governor

s BayRo

ad

Worsleys Road

Early Valley Road

Holmeswood Rise

Dyers

Pas

s Roa

d

Bush Road

Gove

rnors

Bay T

eddin

gtonR

oad

Burkes Bush Road

Kennedys Bush Road

Tai Ta

pu Ro

adState

Highw

ay 75

Old T

ai Ta

pu Ro

ad

Summ

it Road

Rhodes Park

KennedysReserve

Hoon HayReserve

HalswellRiver

CashmereStream

Governors Bay

Head ofthe Bay

Taukahara

Allandale

Governors Bay

Ohinetahi

Lansdowne

ChristchurchAirshed

Christchurch /Ōtautahi Clean Air

Zone


Clean Air Zone

1564000

1564000

1566000

1566000

1568000

1568000

1570000

1570000

1572000

1572000

5168

000

5168

000

5170

000

5170

000

5172

000

5172

000

14 15 1612 1311

17


Re

fere

nce

¯(on A3 Page)




1:25,000








¥77Olivers Road

Rooneys

Road

Ashburton Staveley Road

Dromore Methven Road

Winchm

ore La

uriston

Road

Mitcham

Road

Pole Road

Winchm

ore Scho

ol Road

Winchmore Dromore Road

State Highway 77

Methven HighwayNorth BranchAshburtonRiver/Hakatere

WinchmoreAshburton / HakatereCrop Residue Burning

Buffer Area

1494000

1494000

1496000

1496000

1498000

1498000

1500000

1500000

1502000

1502000

5146

000

5146

000

5148

000

5148

000

5150

000

5150

000

20 21

19

22

18


Re

fere

nce

¯(on A3 Page)



1:25,000

MAP18





Airsheds

Clean Air Zones





¥1

Lethams Road

Coplands Road

Jamiesons Road

Mitcham

Road

Bebbingtons Road

State Highway 1

Rakaia Highway

Dromore Methven Road

Dromore

Hatfield R

oad

Some

rton R

oad

Ashburton / HakatereCrop Residue

Burning Buffer Area

1504000

1504000

1506000

1506000

1508000

1508000

1510000

1510000

1512000

1512000

5146

000

5146

000

5148

000

5148

000

5150

000

5150

000

18

21 222524

2023

19


Re

fere

nce

¯(on A3 Page)




1:25,000








Sheates Road

Blacks Road

Simps

ons R

oad Lowes Road

Tindalls Road

Jacksons RoadWester

field Scho

ol Road

Langdo

ns Ro

ad

Rushford RoadMill Road

Westerfield Lismore Road

Winslow Westerfield Road

Frasers Road


Timaru Track Road

RemingtonCreek

Lagmhor Creek

Westerfield

Lagmhor

Ashburton /Hakatere Crop Residue

Burning Buffer Area

1484000

1484000

1486000

1486000

1488000

1488000

1490000

1490000

1492000

1492000

5140

000

5140

000

5142

000

5142

000

5144

000

5144

000

23

21

18

24

20


Re

fere

nce

¯(on A3 Page)



1:25,000

MAP20





Airsheds

Clean Air Zones





¥1

¥77

Andrew Street

Wakelins

Road

Clark Street

Melrose Road Lane Street

Creek R

oad

Tucker Street

Northpark Road

Glassworks Road

Hanrahan Street

Carters RoadRundles Road

Bucha

nsRo

ad

JB Cullen Drive

Alford Forest Road Belt Road


Taits Road

Farm Road


Hills Road

Bremners Road

Harrison Street

Allens R

oad

Middle Road

Blacks Road

Timaru Track Road

Rakaia H

ighway

State Highway 1

Ashburton Staveley Road

Hepburns Road

Rawles Crossing Road

Racecourse Road

Mitcham Road

Methv

enHig

hway

State

Highw

ay 77

AshburtonRiver/Hakatere

Wakanui Creek

Allenton

AshburtonAirshed

Ashburton/ Hakatere

Clean Air Zone

Ashburton / HakatereCrop Residue Burning

Buffer Area

1494000

1494000

1496000

1496000

1498000

1498000

1500000

1500000

1502000

1502000

5140

000

5140

000

5142

000

5142

000

5144

000

5144

000

20

23

18

24

22

19

25282726

21


Re

fere

nce

¯(on A3 Page)




1:25,000








¥1

Rainey Way

Office Road

Lynn Street

Crum StreetAshford Avenue

Drummond and Etheridge Walk

JB Cullen Drive

Milton R

oad North

Hanrahans Road

Company Road

Chert

sey R

oad

Fairfield Road


Hepburns RoadTaverners Road

Stanley Road

Singletree Road

State Highway 1

Rakaia H

ighway

Fairton

Dromore

Newland

Ashburton/ Hakatere

Clean Air Zone


Burning Buffer Area

1504000

1504000

1506000

1506000

1508000

1508000

1510000

1510000

1512000

1512000

5140

000

5140

000

5142

000

5142

000

5144

000

5144

000

21

18

24

19

25

22


Re

fere

nce

¯(on A3 Page)



1:25,000

MAP22





Airsheds

Clean Air Zones





Millars Road

Scales Road

Ferrimans Road

Siberia Road

Lovetts Road

Mulligans Road

Ferrimans Road

Lowerys Road

Lills Road

Lowes Road

Siberia Road

Barford Road

Lowes Road

Plantation Road

Simps

ons R

oad

Frasers Road


Maronan Road

Brooks Creek

Brooks Creek


Burning Buffer Area

1484000

1484000

1486000

1486000

1488000

1488000

1490000

1490000

1492000

1492000

5134

000

5134

000

5136

000

5136

000

5138

000

5138

000

20

26

21

27

24

1822

25

28

19

23


Re

fere

nce

¯(on A3 Page)




1:25,000








¥1

¥77

Leeston S

treet

South Park Road

East Street

BirdStree

t

Porter Street

Sealy Street

Anne

Stree

tSuffolk StreetWilkin Street

Agnes Street

Graham Street

Brya

ntStr

eetLagmhor Road

Bremners Road

Saunders Road

Harland Street

Magnolia Drive

Queens Drive

Range Street

Long

beac

h Roa

d

Grigg Stree

t

Glassworks Road

McGr

ath Ro

ad

Cross Street

Gray

burn

Road

Keen

ans R

oad

Wills Street

Cameron StreetCox Street

Burnett Street

Aitken StreetWalnut Avenue

Havelock Street

Lills Road

Victoria Street

George Street

Beach Road

River Te rrace

Creek R

oad

Lowerys Road

Kennels Road

Pages Road

Grey Street

Alford Forest Road

Robinson Street

Oak Grove

Dobson Street

South Street

Elizabeth StreetWills Street

Cameron Street

Havelock Street

Walnut Avenue

Oxford Street

Millars Road

Tancred Street

Grove Farm Road

Princes Street

Eton Stree

t

Cochranes R

oad

Johnstone Street

Cass Street

Albert Street

Thews Road

Carters Terrace

Company Road

Tarbottons Road

McMurdo Street

Grove Street

Gartartan Road

Trevors R

oad

William Stree

t

State Highway 77

Chalmers Aven

ue

Bridge Street

Fords

Roa

d

Smithfield Road

Thomson StreetMelcombe Street

Archibald Street

East Stree

t

West Street

Hollands Road

Seafield RoadState Highway 1

Remingtons Road

Grahams Road

Maronan Road

Milton Road S

outh

Wilkins Road

Frasers Road

Hinds Highway

Hendersons Road

Wakanui Road


Beach Road East

State Highway 1


Carters Creek

Netherby

ASHBURTON

Hampstead

AshburtonAirshed

Ashburton /Hakatere Clean

Air Zone


Burning Buffer Area

1494000

1494000

1496000

1496000

1498000

1498000

1500000

1500000

1502000

1502000

5134

000

5134

000

5136

000

5136

000

5138

000

5138

000

20

26

23

21

27

22

28

2524


Re

fere

nce

¯(on A3 Page)



1:25,000

MAP24





Airsheds

Clean Air Zones





Milton R

oad North

Nicolls R

oad

Smithfield Road

Buttericks Road

Beach Road East

Morris R

oad

Milton R

oad Sout

h

Murdochs Road

Wakanui Road

Elgin Road

Singletr

ee Road

Cochran

es Road Hoattens Road

Christys

Road

Le Bretons Road

Fairfield Road

Chert

sey R

oad

Stanle

y Road

Seafield Road

Seafield

Ashburton/ Hakatere

Clean Air Zone

Ashburton /Hakatere Crop Residue

Burning Buffer Area

1504000

1504000

1506000

1506000

1508000

1508000

1510000

1510000

1512000

1512000

5134

000

5134

000

5136

000

5136

000

5138

000

5138

000

21

27

24

28

2218 19

26

23

20

25


Re

fere

nce

¯(on A3 Page)




1:25,000








¥1

Annetts Road

Lynnford Road


Hinds Lismore Road

Winslow Willowby Road

Boundary Road

Lovetts Road

Chatmos Road

Barford Road

Dicksons Road

Swamp Road

Windermere Road

Hendersons Road

Winslow Road

Hinds HighwayState Highway 1

Winslow

Windermere


Buffer Area


Buffer Area

1484000

1484000

1486000

1486000

1488000

1488000

1490000

1490000

1492000

1492000

5128

000

5128

000

5130

000

5130

000

5132

000

5132

000

23

27

24

26


Re

fere

nce

¯(on A3 Page)



1:25,000

MAP26





Airsheds

Clean Air Zones





O'Keefe Road

Hendersons Road

Ludlow Drive

State Highway 1

Wakanui School Road

Grahams Road

Maginness Road

Riversdale Terrace

Huntingdon Avenue

Gartartan Road

Montgomerys Road

Winslow Willowby Road

Griffiths

Road

Lake Hood Drive

Greens Road

River

Road

Grah

ams R

oad Stranges Road

Long

beac

h Roa

d

Fords Road

Boundary Road Carters Creek


Lake Hood

Willowby

Huntingdon


Burning Buffer Area

1494000

1494000

1496000

1496000

1498000

1498000

1500000

1500000

1502000

1502000

5128

000

5128

000

5130

000

5130

000

5132

000

5132

000

26

23 24

28

2520 21 22

27


Re

fere

nce

¯(on A3 Page)




1:25,000








Collisons Road

Corbetts Road South

Gibsons Road

Innes Road

Stanley Road

Beggs Road

Painters Road

Buckl

eys Road

Chert

sey R

oad

Valve

rde Ro

ad

Wakanui Road

River Road

River

Road

Wilso

ns R

oad

Wilsons Road

Inverrose Road

Wrights Road

Wakanui School Road

Denshire

s Road

South

Wakanui Township Road

Christys

Road

Buttericks Road

Le Bretons Road

Beach Road East

Wakanui Creek

Wakanui

Elgin


Buffer Area


Buffer Area

1504000

1504000

1506000

1506000

1508000

1508000

1510000

1510000

1512000

1512000

5128

000

5128

000

5130

000

5130

000

5132

000

5132

000

27

24 25

28


Re

fere

nce

¯(on A3 Page)



1:25,000

MAP28





Airsheds

Clean Air Zones





¥79

Craig Road

High Street

Tancred Street

Forest RoadWalle

r Roa

d

Campbell Street

Logan Road

Burke Road

Waihi

Terrac

e

George Street

Vance Road

Willia

ms R

oad

Totara StreetVance Road

Tripp Street

Sherratt Road

Taylor RoadGale Cutting Road

Huffey Street

Kennedy Street

Ribbonwood RoadRacecourse Road

Connolly Street

Tiplady Road

Wilso

n Stre

et

Gale Cutting Road

Brophy Road

Martin Road

Palmer Road

Peel

Stree

t

Hislop Street

Seaward Road

Pye Road

School RoadGuilford Road

Shaw Road

Ellery Road

McKenzie Street

Woodbury Road

Templer Street

Kalaugher Road

Cox S

treet

Waitu

i Driv

eGeraldine-Fairlie Highway

Main

North

Roa

d

Bennett Road

Talbot StreetGreenvale Road

Orari Station Road

Te Moana Road

Arundel Belfield Road

Downs Road

Sercombe Road

Orari Back Road


State Highway 79

Hae Hae TeMoana River

Downs Creek Orari RiverWaihi River

GeraldineDowns

Belfield

Geraldine

GeraldineAirshed

Geraldine/Raukapuka

Clean Air Zone

1456000

1456000

1458000

1458000

1460000

1460000

1462000

1462000

1464000

1464000

5114

000

5114

000

5116

000

5116

000

5118

000

5118

000

29


Re

fere

nce

¯(on A3 Page)




1:25,000








¥8

Beck Road

Marsh

all R

oad

Keane R

oad

Connells Road

Falvey Road

Levels Store Road

Bassett Road

EslerRoad

Naughton Road

Kerry

town R

oad

Oliver Road

Rosewill Valley Road

Driscoll

Road

Smart Munro Road

State Highway 8


Doake

Road

Rollin

g Ridg

esRo

ad

Levels Valley Road

German Creek

Papaka Stream

Waitawa Creek

RosewillStream

Waitawa

Levels Valley

Timaru / Te Tihi-o-MaruCrop Residue

Burning Buffer Area

1448000

1448000

1450000

1450000

1452000

1452000

1454000

1454000

1456000

1456000

5090

000

5090

000

5092

000

5092

000

5094

000

5094

000

32

31

33

30


Re

fere

nce

¯(on A3 Page)



1:25,000

MAP30





Airsheds

Clean Air Zones





¥1

¥8

T ima ru

D i s t r ic t

Breen Road

Falvey Road

Divan Road

Acac

ia Dr

ive

Blackler RoadWilson Road

Falvey Road

Lynch Road

Connolly Road

Levels Store Road

Dominion Road East

Phar Lap Road

Dominion Road

Hides

Roa

d

Keret

a Roa

d

Hedley Road

Naughton Road Waipopo

Road

Foley

Roa

d

Brosnan Road


State Highway 8

Beach RoadLev

els Plain

Road

State

Highw

ay 1

Timaru

-Temu

ka Hi

ghwa

y

Sead

own R

oad

Levels

Seadown

Timaru / Te Tihi-o-MaruCrop Residue Burning

Buffer Area

1458000

1458000

1460000

1460000

1462000

1462000

1464000

1464000

1466000

1466000

5090

000

5090

000

5092

000

5092

000

5094

000

5094

000

30

32 333534

31


Re

fere

nce

¯(on A3 Page)




1:25,000








Sprin

g Roa

d

Poplar Street

Cliffs Road

Oakwood Road

Basse

tt Roa

d


Pages Road

Claremont Road

Taiko Road

Gleniti Road

Rolling Ridges Road

King Road

Broc

kley R

oad

Rosebrook Road

Spur Road

Fraser Road

Hadlow Road

Otipua CreekNorth Branch

OakwoodStream

Hadlow

Rosewill

TimaruAirshed

Timaru / TeTihi-o-Maru

Clean Air Zone


Burning Buffer Area

1448000

1448000

1450000

1450000

1452000

1452000

1454000

1454000

1456000

1456000

5084

000

5084

000

5086

000

5086

000

5088

000

5088

000

30

34

31

33

35

32


Re

fere

nce

¯(on A3 Page)



1:25,000

MAP32





Airsheds

Clean Air Zones





¥1

¥8

T im a r

uD i s

t r ic t

Kelvin Street

June Street

Tyne Street

Hun t er H ills Drive

Glen Street

Dobson Street

Sheffield Street

Kent StreetMurchison Drive

Spur Road

Grants Road

Seaton Road

MacDonald Street

Lindsay StreetAndrew Street

Luxmoore Road

Jellicoe Street

Orbell Street

Racecourse Road

Old North Road

Kennels Road

Morga

ns R

oad

Old North

Road

Selwyn Street

Moun

tain V

iew R

oad

Douglas Street

Aorangi Road

Timaru

-Temu

ka Hi

ghwa

yPleasant Point Highway

Kellands Hill Road

Cartwrights Road


Evan

s Stre

et

Washdyke Flat Road

Pages Road

Mead

ows R

oad

Seado

wn Ro

ad

Hilton Highway

State Highway 8

State Highway 1

Morrison ParkLeslie Park

WashdykeCreek

Papaka Stream

WashdykeLagoon

Caroline Bay

TaitarakihiCreek

Waimataitai

Grantlea

Smithfield

Marchwiel

Seaforth

Puhuka

Washdyke

TimaruAirshed

WashdykeAirshed


Clean Air Zone


Buffer Area


Burning Buffer Area


Burning Buffer Area

1458000

1458000

1460000

1460000

1462000

1462000

1464000

1464000

1466000

1466000

5084

000

5084

000

5086

000

5086

000

5088

000

5088

000

30

32

34

31

353736

33


Re

fere

nce

¯(on A3 Page)




1:25,000








T i m a r u D i s t r i c t

Wa i m a t e D i s t r i c t

Guscott Road

Brien Road

Claremont Road

Pareora River Road

Sutto

n Roa

dPurves Road

Barto

n Roa

d

Claremont Bush Road

Brockley Road

Pudjeck Road

George Ward Road

Beaconsfield Road

Mt Horr

ible R

oad

Beaconsfield Flat Road

Beaconsfield Road

Holme Station Road

Claremont Road

Adair Road

Landsborough Road

Fairview Road

GordonsStream

Pig HuntingCreek

Otipua CreekSouth Branch

Pig HuntingCreek

Pareora West

Claremont

Otipua

Adair

GlenitiTimaruAirshed


Clean Air Zone


Burning Buffer Area

1448000

1448000

1450000

1450000

1452000

1452000

1454000

1454000

1456000

1456000

5078

000

5078

000

5080

000

5080

000

5082

000

5082

000

36

32 33

37

3534


Re

fere

nce

¯(on A3 Page)



1:25,000

MAP34





Airsheds

Clean Air Zones





¥78

¥1 T ima r

uD i s

t r ic t


Marin

e Para

de

Brookfield Road

Raymond Street

Edward Street

Dee Street

Sutton Road

Devon Street

Shaw Street

Nile Street

Puriri Street

June Street

Kauri

Street

Aynsley Street

Rege

nt St

reet

Park

Lane

Oxfor

d Stre

et

Rimu Street

St Geor

ge Str

eet

Sophia Street

Selwyn Street

Pres

ton S

treet

Rathm

ore St

reet

Sefton Street

Bank

Stre

et

Maltby Avenue

York

Stree

t

James StreetMowb

ray St

reet

Tawa StreetPukatea Street

Port Loop Road

Catherine Street

Elizabeth Street Hayes Street

Evans Street

Fraser Street

Canada Street

Quarry Road

Heaton Street

Wood

lands

Roa

d

Queen Street

Grey

Roa

d

Harpe

r Stre

etCa

in St

reet

College Road

Victor

iaSt

reet

Domain Avenue

Coonoor Road

Arthur Street

Le C

ren St

reet

Aven

ue R

oad

Wilso

n Stre

et

Theo

dosia

Stre

et

CraigieAvenue

Hassall Street

High Street

Stafford Street

South Street

Rockdale Road

Salisbury Road

Scarborough RoadKin

g Stre

et

Talbot Road

Church Street

Rocky Hundreds Road

Landsborough Road

North Street

Fairview Road

Timaru

-Pare

ora H

ighwa

y

Otipua Road

Wai-Iti Road

Beaconsfield Road

State

Highw

ay 1

RosedaleGardens

SaltwaterCreek

Caroline Bay

West End

Watlington

Seaview

MaoriHill

Scarborough

Highfield

Redruth

Salisbury

Kensington

TIMARU

Parkside

TimaruAirshed

Timaru /Te Tihi-o-MaruClean Air Zone


Buffer Area

1458000

1458000

1460000

1460000

1462000

1462000

1464000

1464000

1466000

1466000

5078

000

5078

000

5080

000

5080

000

5082

000

5082

000

36

32

34

37

3330 31

35


Re

fere

nce

¯(on A3 Page)




1:25,000









Wa i m a t e D i s t r i c t

Clay R

oad

Sands RoadChapel Road

Gordons Valley Road

Talbo

ts Roa

d

Lyallda

le Road

Scotts Road

Ward Road

Jefcoates

Road

Brassel

ls Road

Summerl

eaze

Road

Summerleaze Road

Campbell Road

Brasel

l Road

Beaconsfield Road

Pooke Road

Munro Road

Bristol Road

Cairds

Road


Pareora River Road

Pareora River

Southburn


Burning Buffer Area

1448000

1448000

1450000

1450000

1452000

1452000

1454000

1454000

1456000

1456000

5072

000

5072

000

5074

000

5074

000

5076

000

5076

000

34

37

35

36


Re

fere

nce

¯(on A3 Page)



1:25,000

MAP36





Airsheds

Clean Air Zones





¥1

Tim

a ru

D i st r i

c t

Cliffo

rd Str

eet

William Street

Queen Street

River S

treet

Lagoon Drive

Sands Road

Pooke Road King Street

Munro Road

Talbot Road

The Avenue

Ellis Road

Half Chain Road

Campbell Road

Craigie Road

Norm

anby

Roa

d

Bristol Road

Daniels Road

Timaru

-Pareora

Highway

State Highw

ay 1

Kingsdown

Pareora


Burning Buffer Area

1458000

1458000

1460000

1460000

1462000

1462000

1464000

1464000

1466000

1466000

5072

000

5072

000

5074

000

5074

000

5076

000

5076

000

36

34 3532 33

37


Re

fere

nce

¯(on A3 Page)




1:25,000








¥82

Maude Street

Boyes Road

Innes

Street

Courts R

oad

Moores Road

Browns

RoadNayl

or Stree

t James Street

Bond Street

Adam

s Roa

d

Hillary Street

Paul Stree

t

Princes

Street

Manchester Street

Opie Stree

t

John S

treet

Edinburgh Street

Cashel Street

Racecourse Road

Wilkin Street


Dunbars Road

Champions Road

Hannifins Road

Harris S

treet

Yesber

gs Road

Gorge

Roa

d

Allan Stree

tKing

Street

Hunts R

oad

Hodges Road

William Street

Belt Stree

t

Boyce R

oad

Mt John Road

State

Highw

ay 1

Waim

ate Hi

ghwa

y

Rhodes

Street

Slaughteryard Road

Shear

manStree

t

Studholme Settlement Road

Champions Road

Bathgates Road

Bakers Road

Waituna Back Road

Painstown Road

Horgans

Road

Waim

ateHu

nter R

oad

Park Road

Parkers

BushRoad

Garlands Road

Crouch Road

Queen S

treet

Fitzmaurice Road

Parsonage Road

Norto

n Res

erve R

oad

Point Bush Road

Centrewood Park Road

Mitchells Road

Maytown Road

Hakataramea Highway

High Street

Waihao Back Road

Manchesters Road

Whitneys Road

McNamaras Road

Molloys Road

Timaru Road

Mill Road

State Highway 82CentrewoodPark

KnottingleyPark

Deep Creek

Waimate Creek

Waimate Creek

Waimate

NortonReserve

Te Waimate

Maytown

WaimateAirshed Waimate

/ WaimatemateClean Air Zone

1442000

1442000

1444000

1444000

1446000

1446000

1448000

1448000

1450000

1450000

5042

000

5042

000

5044

000

5044

000

5046

000

5046

000

38


Re

fere

nce

¯(on A3 Page)



1:25,000

MAP38





Airsheds

Clean Air Zones




13 Special Zones



Ruahine

Place

Kohi

Drive

Bower AvenueQuee

nspark

DrivePuhara Avenue

Forest Drive

Anglesea Avenue

Aston Drive

Roya

lPark

Drive

Broadhaven Avenue

Rothesay Road

BurwoodLandfill Specific

Purpose Site

Canterbury Maps

B u r w o o d L a n d f i l l S p e c i f i c P u r p o s e S i t e

\\gisdata\Projects\PET\Air_plan_Work ing\Burwood.mxd0 1 2 3

Kilometres

/

Burwood Landfill Specific Purpose SiteLand Parcel

CHRISTCHURCH

Canterbury Maps



¥74

Park Terrace

Old SumnerLyt

telton

Road

Tunnel Road

Governors Bay Road

Summit RoadBridle PathState Highway 74

Sumn

er Ro

ad

Summit Road

Jollies Bush

Motukauatirahi/CassBay

Rapaki Bay

Otokitoki/GollansBay

LytteltonHarbour/Whakaraupō

Te Waipapa/DiamondHarbour

Motukauatiiti/CorsairBay

Cass BayTe Awaparahi

Proposed Christchurch /Ōtautahi Clean Air Zone


\\gisdata\ProjectArchive\PET\2014_2015\Lyttelton_Port_R ecovery_Plan_Draft_150210\LPRP_CARP_Amendment_A4L_150313.mxd0 1 2 3 4 5

Kilometres

P o r t o f L y t t e l t o n L a n d U s e A r e a

Port Land Use Area

Proposed Clean Air Zones

Airsheds


Cultural Zone

Residential Zone

/

BasedataLocal Authority Inland Boundary

State Highways

Land Parcel Boundaries

Open River Bed



Christchurch200 Tuam Street PO Box 345 Christchurch 8140P. 03 365 3828

Timaru75 Church Street PO Box 550 Timaru 7940P. 03 687 7800

Kaikōura96 West End PO Box 59 Kaikoura 7340P. 03 319 5781

Environment Canterbury OfficesFacilitating sustainable development in the Canterbury regionwww.ecan.govt.nz

R17/36

Documents

Canterbury Air Regional Plan - Te mahere ā-rohe mō te hau o