Proposal To Change The Status Of The Tawharanui Marine Park To A Marine Reserve
Auckland Regional Council
The Tawharanui Marine Park was established in 1981 by the then Auckland Regional Authority using provisions from both the Fisheries Regulations and the Harbours Act 1950. The Fisheries Regulations that apply to the Marine Park prohibit the taking of all marine life.
Studies have shown that whilst some species have flourished under the marine park regime, others have not. It is believed that illegal fishing in the marine park may be to blame.
The Auckland Regional Council proposes to reclassify the Tawharanui Marine Park as a Marine Reserve under the Marine Reserves Act 1971. This change will mean that:
- The existing restrictions on the taking of marine life from within the marine park will continue to apply.
- The boundaries of the marine reserve will undergo a minor alterations to enable clearer identification of the boundaries of the reserve.
- Fishing in the area subject to the boundary alterations will be prohibited.
- Protection within the reserve will be improved due to the public’s better understanding of what rules apply to marine reserves, and through improved compliance and law enforcement.
Please Tell Us what You Think
In order to effect this change, the Council needs to make an application for a marine reserve to the Director General of Conservation under the Marine Reserves Act 1971. Prior to making this application, the Council seeks your views on the proposal. A response form has been incorporated.
In order to assist the ARC in making this application please write or complete the reply form attached and return the completed form to the ARC. Submission deadline is now Friday 22 August 2003 NOTE – This date has been extended, submissions still being accepted now
Copies of the discussion document and reply form are available from Auckland Regional Council (Phone 366 2000)
If you would like further information please contact Alan Moore on Phone 366 2000 ext 7058 or email firstname.lastname@example.org.
1.1 Purpose of Document
The Tawharanui Marine Park was established in 1981 using regulations under the Fisheries Regulations and the Harbours Act 1950. Research and monitoring at the reserve has suggested that fish stocks have not replenished as expected. It is thought that one of the main reasons for this is illegal fishing. It is considered that the key contributing factors are:
i. the public’s lack of understanding of the protection afforded to the area by the marine park status; and
ii. a lack of compliance with the prohibition on taking of marine life and effective law enforcement.
In order to overcome this, the ARC is proposing to apply to the Director General of Conservation to change the legal status of the area from a marine park to a marine reserve.
The purpose of the discussion document is to seek comment from selected individuals and groups on this proposal. These comments will be used to amend the proposal. The revised proposal will then be put to the Director General of Conservation as an application for a marine reserve under the Marine Reserves Act 1971.
An outline of the process for considering applications for marine reserves is included as Appendix 1.
2.0 TAWHARANUI MARINE PARK
Tawharanui Marine Park is located on the northern side of the Tawharanui Peninsula which separates Omaha Bay from Kawau Bay and is approximately 90km north of Auckland City (Figure 1). The marine park abuts and complements Tawharanui Regional Park, which is managed by the Auckland Regional Council.
The Auckland Regional Authority established the Tawharanui Marine Park in 1981. The park was promulgated using regulations under the Fisheries Regulations and the Harbours Act 1950. It was the first marine park established under this legislative regime.
The Fisheries Regulations were used to protect all marine life within the park. They do so by prohibiting the taking of marine life. The Harbours Act was used to control activities and structures. The Grant of Control ceased to exist in 1991 with the enactment of the Resource Management Act.
After the success of the Tawharanui Marine Park a number of other marine parks were established including Mimiwhangata Marine Park on the north-east coast north of Whangarei and the Sugar Loaf Island Marine Park near New Plymouth.
2.3 Description and Values
The Tawharanui Marine Park protects all marine life from mean high water mark to one half a nautical mile offshore along three kilometers of coastline. A map showing the existing boundaries of the Marine Park is given in Figure 1.
The geology of the marine park mimics that of the adjacent Tawharanui Regional Park. The western end of the marine park is characterised by exposed beaches overlying greywacke bedrock. Low unmodified dunes back the beaches. The dunes are colonised by a typical array of sand dune plant species including pingao, a regionally rare native sand sedge. This area is also a nesting site for the rare New Zealand dotterel, the threatened variable oystercatcher, and pipits.
The beaches support populations of a fauna typical of exposed beaches, tuatua bed occur near the lower tide mark and scallop beds are found in deeper offshore areas. The beaches are broken by two rocky reef areas referred to as “Comets Rocks” and “Phoenix Reef”. These reefs hold numerous rock pools which support a range of inter-tidal organisms.
To the east of the beach area, the inter-tidal platform becomes more extensive, and unstable boulder beaches occur. Caves and archways feature on this part of the coast. An interesting feature of the park is that the greywacke bedrock contains an abundance of marine fossil deposits (Sporli and Grant-Mackie 1976).
This rocky area is characterised by inter-tidal and sub-tidal reef communities typical of exposed northland environments. Forty species of fish have been recorded within the marine park, including eagle ray, yellow moray eel, longsnout pipefish, red banded perch, butterfly perch, kingfish, silver drummer, blue maomao, banded wrasse, leather jacket and red moki. A summary of the fish species observed in the marine park is given in Table 1. Crayfish (spiny lobster) are common in rocky areas and cetaceans, in particular dolphins, are commonly observed within the park.
Table 1: Fish species of the Tawharanui Peninsula
KEY A = abundant (seen in schools) C = common (seen in small numbers)
F = frequent (often seen singly or in pairs) O = occasional
R = rare (not often seen)
||Two spot demoiselle
||Oblique swimming triplefin
|Long -tailed stingray
|Northern conger eel
|Red banded perch
||Blue eyed triplefin
2.4 Relationship with Tawharanui Regional Park
The Tawharanui Regional Park (588ha) is owned and managed by the Auckland Regional Council. The Regional Council has committed to manage the regional park as a “Mainland Island”. This involves the removal of all exotic pests – rats, hedgehogs, ferrets, stoats, weasels and possums, and the establishment of a predator proof fence to stop recolonisation. This purpose of the mainland island is to manage the area in a predator free state, thereby enabling the re-establishment of populations of endangered species, currently largely confined to predator free offshore islands.
The change in status from marine park to a marine reserve will complement this management regime by creating an area of minimal intervention both above and below mean high water springs. The Tawharanui Peninsular will become one of a few areas in New Zealand where both the mainland and the adjacent marine area are managed in as close to a “pre-human” situation as is possible.
Tawharanui Regional Park is very popular, with visitor numbers of around 160,000 per year. Of these approximately 65% come from the Auckland urban area (Auckland Regional Council and National Research Bureau 2000). Walking and beach related pursuits, including surfing, are the most common activities. The park offers excellent diving and snorkelling experiences. Fishing is provided for outside the marine park on the eastern tip and south coast of the Tawharanui Peninsula. Surfcasters also use the western edge of Ocean Beach.
The marine park forms part of the education and interpretation programme for the Tawharanui Regional Park. An ecology trail for the park incorporates both terrestrial and marine components. An interpretive display within the Regional Park buildings promotes the conservation of marine life. Park Rangers also take visitors for guided walks and include discussion of the marine park.
2.7 Scientific Investigations
The area of the Tawharanui Marine Park has been subject to significant biological monitoring. Monitoring commenced prior to the establishment of the marine park in 1977 and was continued annually until 1983 (Grace, 1978, 1979, 1980, 1981, 1982,1983). Monitoring was also undertaken in 1989, 1991 1994, and 1996 (Grace 1989, 1991, Marine and Environmental Research 1994, Nuthall and Russell 1996). A study of spiny lobster movement within the marine park has also been undertaken (Kelly 1996).
Monitoring has demonstrated that there has been a dramatic increase in the number and size of spiny lobster. Kina density also appears to have increased. There has, however, been little change in fish numbers since 1977. Although in 1996 red moki numbers were three times more common inside the marine park than outside, there has been a general decline in red moki numbers inside the marine park and a lack of large fish despite nearly twenty years of protection. Since red moki are highly territorial, this suggests the impacts of fishing pressure or other external environmental changes have not enabled the population to increase. An alternative theory, which is not highly supported, is that that moki are migrating outside the marine park.
3.0. TAWHARANUI MARINE RESERVE PROPOSAL
3.1 Marine Reserves
Marine reserves are areas of foreshore and sea that have been set aside under the Marine Reserves Act 1971 to preserve habitats in their natural state.
Section 3(1) of the Act states that marine reserves are established:
“.. for the purpose of preserving, as marine reserves for the scientific study of marine life, areas of New Zealand that contain underwater scenery, natural features, or marine life, of such distinctive quality, or so typical, or beautiful, or unique, that their continued preservation is in the national interest.”
In addition to the main purpose of preserving areas in their natural state for scientific study, a number of other benefits accrue from marine reserve status. These include the recognition and protection of marine habitats and organisms for their intrinsic worth, educational opportunities, new opportunities for recreation and tourism, potential refuge, feeding and nursery areas for fish and other organisms and potential “yard sticks” for assessing the impacts or management of adjacent terrestrial and marine resources.
The Marine Reserves Act is administered by the Department of Conservation. The Department has a mandate to conserve and protect the natural resources of New Zealand, and in accordance with this, a network of marine reserves continues to be established in suitable areas around the country. There are currently sixteen marine reserves as of February 2003.
Within the larger Auckland area, there are three marine reserves. These are the Cape Rodney to Okakari Point Marine Reserve (commonly referred to as the Leigh Marine Reserve), the Long Bay – Okura Marine Reserve, and the Motu Manawa (Pollen Island) Marine Reserve. A fourth area is the subject of an application – Te Matuku Bay at Waiheke Island. The Department of Conservation has significant experience in managing marine reserves, and has staff and resources dedicated to this task.
There is before a Select Committee, the new Marine Reserves Bill. This Bill has as its purpose:
…to conserve indigenous marine biodiversity in New Zealand’s foreshore, internal waters, territorial sea and exclusive economic zone for current and future generations, by preserving and protecting within marine reserves –
(a) representative examples of the full range of marine communities and ecosystems that are common or widespread; and
(b) outstanding, rare, distinctive or internationally or nationally important marine communities and ecosystems; and
(c) natural features that are part of the biological and physical processes of the marine communities and ecosystems referred to in paragraphs (a) and 9b), in particular those natural features that are outstanding, rare, unique, beautiful, or important.
3.2 RATIONALE FOR THE PROPOSED CHANGE IN STATUS
Currently there are a number of marine parks in existence. Each of these marine parks has its own protection regime.
The Tawharanui Marine Park is a “no take” marine park, similar to a marine reserve. The Mimiwhangata Marine Park principally protects reef fish species, and does not protect benthic organisms such as spiny lobster and green lipped mussels. Line fishing is allowed at the Mimiwhangata Marine Park provided non-weighted lines are used. At the other extreme, the recently established Hauraki Gulf Marine Park Act which establishes the Hauraki Gulf Marine Park contains no specific protection mechanisms.
Given the range in level of protection afforded by various marine parks it is likely that people are confused as to what level of protection Tawharanui Marine Park affords.
In order for the Tawharanui Marine Park to be successful, people must exhibit different behaviours inside the park compared to outside. As the sea contains no clearly definable boundaries that can be relied upon, the boundaries of the park must be clear. The northern boundary of the park, near Takatu Point, is clearly marked by twin triangular in-line special marks. Similar markers at the southern boundary near Pukenihinihi Point are poorly positioned and are difficult to see from the water. The seaward boundary of the marine park is set at 0.5 nautical miles from mean high water mark. This boundary undulates in and out with the coast and, without the aid of expensive navigation equipment, is very difficult to identify. The public must be able to clearly identify the boundaries of the marine park in order to change their behaviour.
Given that the level of protection afforded to the Tawharanui Marine Park is similar to that of a marine reserve, and that people in the Region are well conversed with rules associated with a marine reserve, it is considered beneficial to change the status of the area from a marine park to a marine reserve. In making this change, it is opportune to re-adjust the boundaries to simplify them for the public.
Tawharanui Marine Park has been in place for almost 22 years and has been widely accepted. The park management plan has been reviewed twice since then and there has been general support with no objections to the protection status (“no take”) of the marine park area. The respondents to a questionnaire in 1998, which sought comment on issues for the new draft management plan due in 2000, supported the upgrading of the marine park to a marine reserve (Auckland Regional Council & National Research Bureau 2000).
In 1995/ 1996 the ARC consulted with a variety of parties over the proposed change in status. The following is a summary of the outcome of this consultation:
|CONSULTATION ON THE PROPOSAL TO CHANGE THE TAWHARANUI MARINE PARK TO A MARINE RESERVE
|Rodney District Counci
|Ministry of Fisheries
||Reduce public confusion
|NZ Fishing Industry Board
||Area is properly established, and managed as a no-take marine reserve, with adequate compliance/law enforcement
|Ngatiwai Trust Board
||Co-management, retention of customary fishing rights
|Kawerau A Maki Trust
||Prefer rahui, mataitai or taiapure reserve. Wish to continue to exercise harvesting rights
|Leigh Fisherman’s Association
||Do not support individual applications, wish DOC to produce a comprehensive plan for marine reserves in the Hauraki Gulf.
3.4 Tawharanui Marine Park Meets the Test of Section 3(1) of the Marine Reserves Act
The Tawharanui Marine Park is one of only four marine protected areas within the Auckland Region. Extractive uses within the marine park have been prohibited for 22 years. Only the Cape Rodney to Okakari Point (Leigh) Marine Reserve has been in existence longer. The Tawharanui Marine Park was the third marine protected area in New Zealand, following the Cape Rodney to Okakari Point Marine Reserve and the Poor Knights Islands Marine Reserve. As discussed previously, whilst the park has not achieved all the ecological benefits it was thought it would achieve, the ecology of the park is significantly enhanced over the adjacent non-protected area.
The value of the Tawharanui Marine Park is recognised in the Proposed Auckland Regional Plan: Coastal which classifies the Marine Park as a Coastal Protection Area 1. Coastal Protection Area 1 sites are afforded the highest protection in the Proposed Plan. Coastal Protection Area 1 sites are of regional, national or international significance and are considered vulnerable to the adverse effects of subdivision, use and development. The proposed plan identifies the values of the park as:
The northern side (82b) and the tip (82a) of the peninsula are the best examples of open rocky intertidal and subtidal marine habitats on the coast of the Outer Hauraki Gulf. Here is found a small geological exposure of fossils in Jurassic rocks (82c). This is a very rare occurrence in Northland and consequently the exposure is of national importance and has been selected by the Department of Conservation as an Area of Significant Conservation Value (ASCV). The open sandy beaches (82b) are also important as the mobile sands are an important New Zealand dotterel breeding area as well as being a threatened plant habitat. The majority of this area (82b) is included within the marine protected area associated with the Tawharanui Regional Park.
Given the above, it is clear that the marine park meets the criteria of Section 3(1) of the Marine Reserves Act. The marine park would also meet the purpose of the Marine Reserves Bill, as it is currently written.
3.5 Boundary Changes
With regard to the boundaries marine park, the eastern and western boundaries are marked by “special marks”, being red and white triangular in-line markers. As stated in Section 3.2 some the existing boundaries of the marine park are not well situated. The following is an account of the proposed changes.
3.5.1 Existing Boundaries
The existing eastern boundary, near Takatu Point, is due north from a prominent headland, and is currently marked by two large triangles (white and red) in-line special marks. When the triangles are aligned the boundary line is true. The seaward is defined out to one half of a nautical mile (972m) from mean high water (MHW )(36?21.3’s, 174?51.7’e). . These markers are well located and are easily seen from the sea.
The existing western marine park boundary is 650m east of Pukenihinihi Point and is marked by two large triangular in-line special marks located in the sand dunes (36?21.4’s, 174?49.56’e). These markers are not well sited, and as a consequence are not clearly visible from the sea.
The seaward boundary is depicted by a line half a nautical mile from Mean High Water Mark. This boundary therefore follows the convolutions of the coast and is very difficult to follow without the aid of complex electronic navigation equipment.
3.5.2 Proposed Boundaries
In order to alleviate these issues it is proposed to amend the existing boundaries.
It is proposed to move the western boundary approximately 100m to the west so that it sits 550m east of Pukenihinihi Point. This will enable the special marks to be located on the crest of a large dune which is backed by a prominent land contour. This will allow easier siting of the two special marks from the sea. The boundary will extend in a true northerly direction from these marks.
The current seaward boundary is 0.5 nautical miles from mean high water springs. The Department of Conservation promotes straight line boundaries as they are easier to locate on marine charts and can be marked with buoys. It is therefore proposed to straight line the seaward boundary of the reserve. It is proposed to increase the length of the western boundary from 0.5 nautical mile (920m) to 1000m, with the seaward boundary extending in a true East - West direction. This will extend the length of the eastern boundary to 1.1 km. The resultant seaward boundary will be approximately 3.72 km long.
A map showing the proposed marine reserve boundaries is given in Figure 2.
3.6 Monitoring/ Research
The Auckland Regional Council has to date supported research within the Tawharanui Marine Park. The Council will continue to support research at Tawharanui Marine Reserve by encouraging projects especially in partnership with tertiary institutions.
3.7 Steering Committee and Compliance and Enforcement
Section 10 of the Marine Reserves Act provides for the establishment of a Steering Committee to provide direction for the management of the reserve. Given that the proposed marine reserve will abut the Tawharanui Regional Park it is appropriate that a steering committee be formed to assist with integrated management between the marine reserve and Tawharanui Regional Park. It is therefore recommended that such a committee be established.
4.0 WHAT DO THE CHANGES MEAN TO THE PUBLIC
In terms of the public, the proposed change from a marine park to a marine reserve will have little effect. Similar rules will apply to that part of the marine reserve which is currently within the marine park boundaries.
The main effects will result from the adjustments to the western and seaward boundaries, and the resultant incorporation of a section of sea not currently subject to the marine park protection. People will no longer be able to harvest marine life from the newly incorporated area. However, as the area is relatively small it is considered that this change is not significant.
The proposed realignment of the boundaries will enable people to clearly identify the boundaries of the marine reserve and provide the public with greater certainty.
The public and the reserve will also benefit from improved compliance and law enforcement, thereby ensuring the purpose of the marine reserve is better achieved.
6.0 MINISTER OF CONSERVATION’S EVALUATION CRITERIA
In evaluating a marine reserve application, the Minister of Conservation is required by Section 5(6)(a) to (e) of the Marine Reserves Act to consider the following:
(a) Interfere unduly with any estate or interest in land in or adjoining the proposed marine reserve;
(b) Interfere unduly with any existing rights of navigation;
(c) Interfere unduly with commercial fishing;
(d) Interfere unduly with or adversely affect any existing usage of the area for recreational purposes;
(e) Otherwise be contrary to the public interest
The following responses are made with respect to these matters:
(a) The proposed marine reserve abuts the Tawharanui Regional Park which is owned and managed by the ARC. There is no private land adjoining the proposed Marine Reserve. The ARC has consulted the adjacent land owner who has indicated support for the proposal.
(b) The proposed marine reserve is largely based on the Tawharanui Marine Park with the exceptions of a small westward movement of the western boundary and the seaward movement of the seaward boundary. The area surrounding the proposed reserve is open coast with no designated or recognised navigation routes. The proposed classification does not restrict navigation through the reserve. It is concluded that it will not have any effect on navigation.
(c) All marine life within the Tawharanui Marine Park is protected under the Fisheries Regulations. Accordingly it is unlawful to undertake commercial, recreational or traditional fishing activities within its bounds. The proposed change in status of the area to a marine reserve will not affect any commercial activity with the area that was occupied by the Park.
Of issue however, is the effect of the boundary adjustments proposed in the application. The area proposed to be incorporated is the reserve that is west and seaward of the existing marine park will result in commercial fishing activities being prohibited from this area. The boundary adjustments are minor, and it is considered that the effect is not undue. It is also considered that the any adverse effects are off-set by the benefits of having more clearly defined reserve boundaries.
(d) The proposed marine reserve does not restrict recreational activities apart from extractive uses such as recreational fishing.
As with the commercial fishing, the proposed marine reserve will not change or alter the recreational activities able to be undertaken within the area of the existing Tawharanui Marine Park. The proposed boundary adjustments will however prohibit recreational fishing from the newly incorporated area.
In proposing the new western boundary, it has been located such that recreational fishing can be undertaken on a small section of beach between the boundary and Pukenihinihi Point. This avoids the need for people to use private land to access fishing areas at high tide.
In terms of the seaward boundary, this will displace recreational fishers between 100m and 300m seaward. There will remain significant areas of Omaha Bay available for recreation fishing in water of a similar level of exposure. It is therefore concluded that the proposed reserve is unlikely to result in any undue adverse effect on recreational fishing.
As with commercial fishers, recreational fishers will benefits from more clearly defined boundaries thereby having more certainty as to the legality of their activities.
(e) In terms of (e), previous consultation with Ngatiwai and the Kawerau A Maki Trust have raised issues of traditional fishing. The current marine park prohibits all forms of fishing, including traditional fishing. The proposed boundary adjustments will extend this prohibition over a larger area, however this area is not significantly greater, and the proposed boundary changes will result in greater certainty as to the location of the reserve boundaries. This greater certainty is a significant positive benefit. However, it is recognised that rights under the Treaty of Waitangi and traditional fishing will be of issue.
The proposal to change the status of the Tawharanui Marine Park to a marine reserve will in itself cause little effect on users of the area as the rules of the existing marine park are similar to those of a marine reserve.
In applying for the marine reserve classification the opportunity has been taken to rationalise the boundaries of the proposal. The resiting of the western boundary and the straight-lining of the seaward boundary results in a slight increase in the area of the reserve. It is considered that this increase in area is not significant and will not result in the failure of the proposal to pass the test of Section 5(6)(a) to (e) of the Marine Reserves Act.
Auckland Regional Council, 1992. Tawharanui Management Plan. ARC Parks Service.
Auckland Regional Council & National Research Bureau, 2000. Auckland Regional Parks: Park Users Satisfaction Study, January 2000
Department of Conservation, 1994. Marine Reserves, A Guide for Prospective Applicants.
Department of Conservation and Ministry of the Environment, 2000. The New Zealand Biodiversity Strategy: “Our Chance to Turn the Tide” Whakakohukihukitia Te Tai Roroku Ki Te Tai Oranga, February 2000
Grace, R. V. 1978. Tawharanui marine monitoring programme. Report on first year. Unpublished report prepared for the Auckland Regional Authority.
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Grace, R. V. 1980. Tawharanui marine monitoring programme. Report on progress. Unpublished report prepared for the Auckland Regional Authority.
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Grace, R. V. 1982. Tawharanui marine monitoring programme. Report on progress. Unpublished report prepared for the Auckland Regional Authority.
Grace, R. V. 1983. Tawharanui marine monitoring programme. Report on progress. Unpublished report prepared for the Auckland Regional Authority.
Grace, R. V. 1989. Tawharanui marine report. Unpublished report prepared for the Auckland Regional Authority.
Grace, R. V. 1991. Tawharanui marine report. Unpublished report prepared for the Auckland Regional Council.
Kelly, S. 1996. Lobster movement within the Tawharanui marine park. File 8/1/1/7, Auckland Regional Council. 5pp.
Kelly, S. 1998a. Tawharanui Marine Monitoring programme: Part I: A review and critique of methodologies and results. Report prepared by Coastal and Aquatic Systems Ltd for the Auckland Regional Council.
Kelly, S. 1998b. Tawharanui Marine Monitoring programme: Part II: Proposed changes to the existing scheme. Report prepared by Coastal and Aquatic Systems Ltd for the Auckland Regional Council.
Marine Environmental Research, 1994. Tawharanui Marine Monitoring Programme. Report on progress 1994. Unpublished report for the Auckland Regional Council. 30pp.
Nuthall, S. & Russell, A. 1996. Tawharanui Regional Park Marine Survey. Unpublished report for the Auckland Regional Council. 30pp.
Sporli, K. B. & Grant-Mackie. 1976. Upper Jurassic fossils from the Waipapa Group of Tawharanui peninsula, north Auckland, New Zealand. New Zealand Journal of Geology and Geophysics 19(1) 21-34.