Fisheries (Seabird Mitigation Measures—Bottom Longlines) Circular 2021 (Notice No. MPI 1366)
This circular is issued by the Chief Executive of the Ministry for Primary Industries under Regulation 58A of the Fisheries (Commercial Fishing) Regulations 2001.
This circular is the Fisheries (Seabird Mitigation Measures—Bottom Longlines) Circular 2021.
This circular comes into force on 1 October 2021.
This circular applies to the operator or master of a vessel whose responsibilities for compliance are described in regulation 58B of the Fisheries (Commercial Fishing) Regulations 2001.
In this circular, unless the context otherwise requires,—
Act means the Fisheries Act 1996.
aerial extent means the section of the streamer line backbone running from the vessel stern to where the backbone of the streamer line enters the water.
bottom longline means a line to which seven or more hooks (whether baited or not) are attached, and is sunk using weights.
hauling means the period from when line retrieval commences to when all the hooks are onboard.
hauling mitigation device is any device that physically deters or blocks seabirds from flying or swimming directly into the area where lines are being hauled, without causing harm to birds.
high risk period means during daylight hours (0.5 hours before nautical dawn and 0.5 hours after nautical dusk) or during a full moon and three days either side of a full moon.
nautical dawn means the time at sunrise when the centre of the sun is at a depression angle of 12 degrees below the ideal horizon for the location of fishing.
nautical dusk means the time at sunset when the centre of the sun is at a depression angle of 12 degrees below the ideal horizon for the location of fishing.
offal means parts of a fish that are usually discarded, including minced parts.
set, in relation to a bottom longline, means releasing the bottom longline into the water.
streamer line means a type of seabird-scaring device, also known as a tori line.
For the avoidance of doubt, if a term that is used in this circular is defined in the Act or Fisheries (Commercial Fishing) Regulations 2001, that term carries the same meaning as in those provisions.
Any vessel seven metres or greater in overall length using bottom longlines as a method of fishing must—
Vessels which exclusively use the method of Dahn lining are not required to carry a streamer line.
A streamer line must be used on vessels seven metres or greater in overall length during the setting of bottom longlines, in accordance with clause 6. Vessels using the method of Dahn lining are not required to use a streamer line.
1. For vessels utilizing automatic baiting machines, and those 20 metres or greater in overall length, the streamer line must meet the following specifications:
2. For vessels that are seven to 20 metres in overall length, the streamer line must meet the following specifications:
3. The specifications in subclauses (1) and (2) do not apply to additional or secondary seabird-scaring devices fishers may choose to use (such as a second tori or streamer line).
1. A bottom longline must not be set in New Zealand waters to take fish, aquatic life, or seaweed during high risk periods as defined under clause 3, unless line weighting is used in accordance with clause 8.
2. A bottom longline must not be set to take fish, aquatic life, or seaweed between 1 November and 31 May in FMA 6 unless using an integrated weighted line with a lead core of at least 50 grams per metre.
1. Bottom longlines must be weighted such that the slowest sinking hook can be demonstrably shown to reach a depth of five metres within the required aerial extent of the streamer line under clause 6.
2. Sink rates must be measured at regular intervals (at least once per calendar month or when gear setup significantly changes) via bottle tests or time-depth recorders and the results documented and retained on the vessel for a minimum of one year. These records must be made available to fisheries officers and observers upon request.
1. Offal or fish must not be discharged during setting of bottom longlines.
2. Offal or fish may be discharged during the hauling of bottom longlines, but only from the side of the vessel that is opposite to the side on which the hauling station is located.
3. Subclause (1) does not apply to—
4. Despite subclause (2), during the hauling of bottom longlines, —
The Fisheries (Seabird Mitigation Measures—Bottom Longlines) Circular 2020 (LI 2018/116) is revoked.
1. The Schedule provides further guidelines on the design and deployment of streamer lines as seabird-scaring devices.
2. The Schedule is not part of the specifications.
3. If there is any inconsistency between the guidelines in the Schedule and the specifications, the specifications prevail.
1. The streamer line needs to protect baited hooks from seabirds. This means that the streamer line should be positioned in such a way that streamers are flapping in an unpredictable fashion, above the area in which the baited hooks enter the sea, so that seabirds are deterred from attempting to take bait from the hooks. In order to achieve this even during cross-winds, it is expected an operator or master of a vessel will have to make adjustments to the configuration of the streamer line depending on the conditions.
2. It is generally recognised as best practice to maximise the aerial extent of the streamer line, because this maximises the area in which the baited hooks are protected from seabirds. Best practice would be to achieve an aerial extent of 100 metres or more. In order to maximise aerial extent, it is necessary to create tension in the streamer line. This can be achieved by—
3. In order to be effective at scaring seabirds away from the line of baited hooks, the streamer lines should not become tangled, either with each other or with the backbone. Each streamer shall be attached to the streamer line in a manner to prevent fouling of individual streamers with the streamer line, and to ensure individual streamers reach the waterline in the absence of wind or swell (except within the first 15 metres where streamers can be shortened). Swivels or a similar device can be placed in the streamer line in such a way as to prevent streamers being twisted around the streamer line. Each streamer may also have a swivel or other device at its attachment point to the streamer line to prevent fouling of individual streamers.
4. Streamers are to be spaced at five metre intervals along the aerial extent of the line. The total number of streamers in use will vary depending on how the line is configured. Streamers that are hanging in the water can be prone to tangling. Because the far end of the streamer line will frequently be in the water, it may not be desirable to have streamers the whole way down the line. However, it is important that streamers are present to deter birds from taking baited hooks all along the part of the line that remains above water, as outlined in the specifications.
5. To ensure streamers are visible to birds, they should stand out against the surroundings. Streamers should be made of brightly coloured fluorescent plastic tubing or other material. Bright colours such as red, yellow, orange, or pink are most effective during day setting. For night setting, the streamers should be of a colour that contrasts with the surroundings. Colours such as blue and green are less likely to be effective, because they are less likely to be highly visible to birds.
6. A complete additional streamer line should be carried as a spare.
7. When externally weighted gear is used, it is not necessary for all the weight specified to be applied at 60 metre intervals along the hook-bearing line. It is equally permissible for multiple weights of smaller sizes to be attached to the hook-bearing line at shorter intervals, as long as the sink rate of the hook-bearing line meets the requirement specified in clause 8.
Dated at Wellington this 27th day of July 2021.
EMMA TAYLOR, Director Fisheries Management, Ministry for Primary Industries
This note is not part of the circular, but is intended to indicate its general effect.
This circular, which comes into force on 1 October 2021, is made under Regulation 58A of the Fisheries (Commercial Fishing) Regulations 2001 (“Regulations”). It is made by the Director of Fisheries Management, of the Ministry for Primary Industries pursuant to an authority delegated under the Public Service Act 2020.
This circular revokes The Fisheries (Seabird Mitigation Measures—Bottom Longlines) Circular 2020 (Notice No. MPI 1174) (New Zealand Gazette, 8 June 2020, Notice No. 2020-go2290) and replaces it.
This circular sets out mandatory mitigation measures that apply to commercial fishers using the method of bottom longlining. The measures are designed to mitigate the effect of fishing-related seabird mortality. The circular requires that, when setting bottom longlines, commercial fishers—
Streamer lines meeting the requirements of this circular are approved seabird-scaring devices for the purposes of Regulation 58(1) of the Regulations. The Schedule sets out best practice guidelines for—
The guidelines do not form part of the specifications set under Regulation 58A of the Regulations and do not have the force of law. In the event of any inconsistency with the specifications set out in clauses 6–8, the specifications prevail.
This circular also imposes restrictions on the discharge of offal or fish while setting and hauling bottom longlines.