My experience in designing ‘trawl corridors’

Unlike the Sea Change 2017 marine spatial plan that sought to phase out bottom impact fishing from the Hauraki Gulf Marine Park the governments response (Revitalising the Gulf 2021) was to create ‘trawl corridors’. Bottom trawlers do not have a public license to keep smashing the seafloor, a 2021 Horizon Research poll had 84% support for a banning the practice. I love the seafloor and volunteer for an organisation that restores damage done to it by bottom impact fishing. I’m completely opposed to trawling as a fishing method but I put my hand up to help limit its impact in the Gulf using a science based process by joining the Hauraki Gulf – Benthic Spatial Planning Advisory Group (HG-BSPAG).

This was my first experience in a collaborative decision making process run by the Government with industry representatives. I represented an environmental Non-Government Organisation (eNGO), there were three eNGO participants, everyone else was either from NIWA, central & local govt or the fishing industry. The process was chaired and controlled by Fisheries NZ. The other two eNGO participants were awesome and I learnt a lot from them.

I particularly liked the data first approach to marine spatial planning, Zonation is a great tool and I liked the way it starts by removing the human impacts then making an economic case for re-introducing them. Unfortunately some data that would have been useful was not quite complete.

Fisheries NZ controlled the outputs by defining what is in scope. Here is a list of requests that were disregarded:

  1. Ground truthing the modelling work (out of scope).
  2. Modelling the distribution of Unwanted Organisms (UOs) . We know from NIWA surveys that trawl nets catch UOs in the HGMP, transporting UOs is an offence under Section 52 of the Biosecurity Act 1993. By excluding UO’s from the study FNZ failed to protect native benthic habitats from UO’s which can be spread by bottom impact fishing (see appendix for more details).
  3. Infauna (animals that live in the sediments) that are sensitive to bottom impact fishing were excluded from the modelling due to technicalities.
  4. Mobile species that contribute biogenic habitat like tipa / scallops (see appendix) and burrowing animals like ghost shrimp and crabs were excluded because they were mobile which did not suit their definition of biogenic habitat. This is ridiculous as the smallest grid size is 250m and previously mentioned adult animals are unlikely to move more than 10m.
  5. Important habitats for fish (like spawning and nursery areas) were not considered (out of scope).
  6. The indirect effects of bottom impact fishing. Sediment plumes from bottom impact fishing choke and kill filter feeding animals and smother photosynthesising plants. These effects were not included but have been discussed at the end of the report.
  7. Climate change impacts (e.g. CO2 released from resuspending sediments and heart urchins moving deeper as water warms) also not included but have been discussed at the end of the report.
  8. Modelling the economic benefits of excluding bottom impact fishing to other fisheries that don’t impact the seafloor, this could have dramatically altered the findings (out of scope).
  9. Monitoring changes in the money made in an area over time during the transition from one fishing method to another, I think it’s critical this is done with any changes to bottom impact fishing.
  10. Using the regulations, not existing fishing effort, as the starting point for limiting Danish seining (see appendix on Danish seining regulations). Despite multiple requests FNZ would not even put the existing regulations on the maps.
  11. Protecting the deeper areas of the HGMP (see appendix).

We did not discuss substrate. Is it better to trawl on sand which emits a smaller plume but may transition to mud with intensified disturbance, or mud which has a larger sediment plume? We know repeated bottom impact fishing alters the chemistry of the seafloor.

The narrow scope of the project was frustrating because there is an aspiration for Ecosystem Based Management of the Hauraki Gulf Marine Park. Once all the environmental effects of bottom trawling and Danish seining are considered, the fishing methods should be banned everywhere.

I have some sympathy for fisheries managers, they have specific deliverables and get pushed around by industry. I did think their approach was often callous, in the face of uncertainty they often chose the status quo rather than taking a more precautionary approach. One member of the Hauraki Gulf Fisheries Management Plan Working Group HG-FMPWG that will finish the corridor design work has publicly criticised the process.

There were no opportunities for feedback on the corridors the scenarios produced. Final trawl corridor design will be Fisheries NZ’s responsibility and will get input from the HG-FMPWG. Other than the above I have no criticisms of the process, it just needs bigger budgets and managers who care more about te taio. I learnt a lot and am happy to volunteer my time again to use scientific modelling in a spatial planning process to protect the environment.

One difficulty I had was proposing trawl corridors. I decided not to volunteer a low impact scenario because the process had already generated a near zero impact scenario which I thought was reasonable (Similar to Figure 14C in the published report – 90% of recovery potential habitat and current trawl footprint & current/proposed protected areas and 100% of current distribution of biogenic habitat (minimising impacts on trawl fishery.) This meant I was left very unhappy with the scale of the proposed scenarios. It was obvious that the scenarios would need work before Fisheries NZ could designate corridors, however I may end up regretting that decision.

I hope Fisheries NZ will monitor recovery (which may take centuries) the data gained could help ground truth this model and develop more robust models in future.

You can read the published report on the design process here: Exploring the use of spatial decision support tools to identify trawl corridors in the Hauraki Gulf Marine Park

Advice for the Hauraki Gulf Fisheries Management Plan Working Group

The outputs of the process will be used by the Hauraki Gulf Fisheries Management Plan Working Group to design bottom trawling corridors in the marine park. Here are some key points they should be aware of:

  • Because the process is not ground truthed and does not account for secondary impacts, important habitats for fish or climate change impacts a precautionary approach should be taken. (I suggested massive buffers but they were deemed out of scope).
  • Danish seining impacts have not been included in the model. This skews the impacts, recovery in areas where this fishing method is practiced has been understated.
  • The corridors should be much deeper (further from the coast) to avoid the illegal transport of Unwanted Organisms.
  • Consider the existing Danish regulations as the starting point, not the area where the fishing method is currently practiced.
  • Protect the deeper areas of the Gulf because they are included in the Hauraki Gulf Marine Park (see appendix).
  • Include monitoring (fisheries method transition) in any recommendations.
  • Take special note of the sediment resuspension impacts detailed on page 68 of the report which were excluded from the study.

Appendix

Avoiding tipa / scallop beds

Running heavy trawl gear over tipa / scallop beds is incredibly damaging and foolish behaviour. It not only damages the tipa including juveniles, but also the settlement substrates the tipa use as part of their lifecycle. The Review of Sustainability Measures for New Zealand scallops (SCA 1 & SCA CS) for 2022/23. 3.1.18 states that:

“Within the Hauraki Gulf Marine Park, overlap between trawl activity and scallop beds will be considered as part of the proposal to establish defined ‘trawl corridors’ that will limit the areas where bottom trawling can continue to operate. With the introduction of electronic reporting and Global Position Reporting (GPR) on commercial fishing vessels, Fisheries New Zealand has the ability, through fine scale data, to monitor any notable overlap between fisheries and methods.”

It was frustrating that even though tipa are the most surveyed biogenic habitat in the Gulf the fisheries scientists decided that instead of identifying them they would just model their associated habitats. In the paper they literally say they ‘hope’ that this would mean the beds would be avoided rather than just mapping them out. Only the small beds that remained open at the time of the study (the fishery has since collapsed with bottom impact fishing implicated as a key stressor) were removed from the study area.

The rationale for the exclusion of tipa was that they are very mobile. This is ridiculous given the grid size of the study is 250m. Adult tipa and burrowing animals are unlikely to move more than 10m in their lifetime. For adult tipa mobility see Morrison, M. A. (1999). Population dynamics of the scallop Pecten novaezelandiae in the Hauraki Gulf (Doctoral dissertation, ResearchSpace@ Auckland).

Danish seining regulations

The restrictions prescribed in fisheries regulations for Danish seining define a different area than what is currently applied by Fisheries NZ. The State of our Gulf 2020 quotes Fisheries  NZ as ‘committed to reviewing this discrepancy as part of management actions put forward in a fisheries plan for the Hauraki Gulf’. The discrepancy is not recorded in the final report.

Protecting the deeper areas of the HGMP

The deeper areas of the HGMP were excluded from the final scenarios. I asked that they be protected because:

  1. The edges of continental shelves are biodiversity hots spots. Predicted diversity along the depth incline is one of the reasons for excluding the area from the model.
  2. This process was designed to protect biodiversity.
  3. This is the only deep water area in a marine park in New Zealand.

Unwanted organisms discussion document

Here is the discussion document on an unwanted organism (Mediteranean fanworm) I prepared for the working group, similar logic could have been applied to other species including the two recently introduced Caulerpa species.

Omissions

The report details protection measures proposed by Sea Change 2017 but omits the most important benthic protection measure, “the phase out of all bottom trawling, Danish seining and scallop dredging from the Hauraki Gulf, with all such methods excluded by 2025” It’s a strange omission that reads like an attempt to exclude the measure from the history books.

Northern New Zealand dotterel productivity rates

Northern New Zealand dotterel are classified as a Conservation Dependent species, this means that without human help they will go extinct (usually because of predation from introduced predators like rats & cats). So how do you know if your local dotterel are going extinct or not?

Well first you need to work out their productivity rate. Productivity is measured by the average number of chicks fledged per breeding pair (per season). Fledglings divided by pairs. So if you had two pairs and they fledged one chick you can say the site averaged half a fledgling (0.5) per pair.

1 fledgling / 2 pairs = 0.5 productivity

0 fledgling / 2 pairs = 0 productivity

1 fledgling / 3 pairs = 0.33 productivity

Management is considered effective if productivity values are greater than 0.5 for three consecutive years or longer (Dowding & Davis, 2007).

I help manage dotterel at three sites, I can not claim effective management and any of them. This means that over time these sites are a population sink. It’s important to track and share this metric to help conserve the species.

Update April 2025:

New research published by (Dowding & Chamberlin 2025) has found that Variable Oystercatcher have higher survival rates than Northern New Zealand dotterel, so they require a lower productivity rate—0.22 chicks fledged per pair per year or more—for the population to be sustainable and management to be considered effective.

Seaweek fanart

More experiments with AI generated art. I used multiple tools all built on Stable Diffusion, however I am still refining everything in Procreate and compositing with Photoshop.

Protected species bycatch in the wider Hauraki Gulf region 2019-2020

This OIA request for photos of bycatch by observers on commercial fishing boats was sent August 2022 and answered 24 February 2023 due to technical issues.

Please supply the following information under the Official Information Act (OIA):

1. All photos of the two black petrel caught by snapper longline fisheries between 2019-20 in this map. There are no photos of these captures as the birds were released alive. The priority is to release live birds as quickly as is possible and there may not have been time to take photos. This part of your request is therefore declined pursuant to section 18(e) of the OIA.

2. All photos of the seven flesh-footed shearwater caught by snapper longline fisheries between 2019-20 in this map.

3. All photos of the flesh-footed shearwater caught by minor bottom longline fisheries between 2019-20 in this map.

Only one individual shearwater was captured and only one photo was taken of the capture.

4. All photos of the white pointer shark caught by snapper longline fisheries between 2019-20 in this map.

5. All photos of the leatherback turtle caught by bigeye longline fisheries between 2019-20 in this map.

The leatherback turtle was released alive

6. All photos of the green turtle caught by southern bluefin longline fisheries between 2019-20 in this map.

Please report set nets in the Tāmaki Estuary

I made this sign to help the Tāmaki Estuary Protection Society enforce the set net ban. I am uploading it here so that the map in particular is easily found on the internet.

Set nets are banned in the Tāmaki Estuary. Set nets indiscriminately catch non- target fish species; birds and mammals. There has been a recent increase in illegal set netting in the Tāmaki Estuary, please help protect our fisheries and other wildlife.

If you see a set net within the banned area:

  • Please urgently contact 0800 4 POACHER (0800 47 6224)
  • Please report the set net location details and any vehicle license plate. Photos and details can be emailed to poacher@mpi.govt.nz

Your kaitiakitanga will be appreciated by generations to come, kia kaha!

Here is the link to a PDF of the sign.

Bottom trawling graphics

I recently took part in a science led process to limit the impacts of bottom trawling & Danish seining in the Hauraki Gulf Marine Park. I found the narrow scope of the work quite frustrating. The fishing industry knows it has a social license issue with bottom trawling and made a video to address it. The cartoons don’t tackle key concerns with the fishing method. I have made some graphics to point out the key issues focusing on the smaller (<20m) bottom trawlers that scrape the seafloor of the Hauraki Gulf Marine Park.

Bottom trawling is a problem for much of New Zealand’s EEZ and beyond. Feel free to download and use the graphics, let me know if you want them at a higher resolution.

Fisheries New Zealand (2022). Aquatic Environment and Biodiversity Annual Review 2021. Compiled by the Aquatic Environment Team, Fisheries Science and Information, Fisheries New Zealand, Wellington New Zealand.
Jones, E.G., MacGibbon, D.J., Baird, S.J., Hurst, R.. (2021). Gear use in New Zealand inshore trawl fisheries. New Zealand Fisheries Assessment Report 2021/30. ISBN 978-1-99-100927-2
Mormede, S.; Sharp, B.; Roux, M.J.; Parker, S. (2017). Methods development for spatially-explicit bottom fishing impact evaluation within SPRFMO: 1. Fishery footprint estimation. SC5-DW06. 5th Meeting of the Scientific Committee Shanghai, China, 23 – 28 September 2017.

Sim-Smith, C., Kelly, S., Lee, S., Kirikiri, R. (2020). State of our Gulf 2020. Hauraki Gulf Forum.


Eayrs S. Craig T. Short K. (2020). Mitigation techniques to reduce benthic impacts of trawling. Report prepared for the Department of Conservation. Wellington, New Zealand: Terra Moana

Calculation: 7,658 Trawls 2016-19. 7,658*13.5km (12-15km per trawl) = 103,383kms / 3years = 34,461kms PA. Length of NZ = 1,600km. 34,461km / 1,600km = 21.5. 21 times the length of Aotearoa.
Management Action 1.1.1 in the draft Fisheries Management Plan promised to “Exclude bottom trawling and Danish seining from the Hauraki Gulf Marine Park (HGMP). Designate corridors suitable for bottom trawling and Danish seining and create exemptions from the ban for these corridors.” This has been changed to “Exclude bottom trawling and Danish seining from the Hauraki Gulf except within defined areas or ‘corridors’.”
Ferdinand K.J. Oberle, Curt D. Storlazzi, Till J.J. Hanebuth. What a drag: Quantifying the global impact of chronic bottom trawling on continental shelf sediment. Journal of Marine Systems.Volume 159, 2016. ISSN 0924-7963

Pilskaln, C. H., Churchill, J. H., & Mayer, L. M. (1998). Resuspension of Sediment by Bottom Trawling in the Gulf of Maine and Potential Geochemical Consequences. Conservation Biology, 12(6), 1223–1229.
MacDiarmid, A., McKenzie, A., Sturman, J., Beaumont, J., Mikaloff-Fletcher, S., Dunne, J. (2012). Assessment of anthropogenic threats to New Zealand marine habitats. New Zealand Aquatic Environment and Biodiversity Report No. 93
Sala, E., Mayorga, J., Bradley, D. et al. Protecting the global ocean for biodiversity, food and climate. Nature 592, 397–402 (2021).

Please sign this petition.

My op-ed on bottom trawling in the Gulf published in Newsroom

Dredged to death

Fridays closure of the last two tipa / scallop beds in Aotearoa / New zealand will mark an historic moment for our fisheries. It signals the collapse of more than a fishery but an entire ecosystem. 

The last commercial mussel was dredged out of the Hauraki Gulf in 1966, after 56 years there are no signs of recovery. We don’t yet know what the fate will be for tipa. The fishery at the top of the South Island has been closed since 2017. If the tipa beds do not recover it will be the best evidence of ecocide in Aotearoa / New Zealand this century.

We need to change our ways. Both recreational and commercial dredging must be banned as per the Hauraki Gulf 2017 marine spatial plan that the government has still not acted on. These fishing methods damage the habitat that the animals grow in.

The result is:

  • Dead and damaged non target species and juvenile tipa
  • Lost biodiversity and water clearing animals
  • Lost habitats for fish especially juvenile fish
  • Long term changes to seafloor chemistry

The same impacts are created by other bottom impact fishing methods like bottom trawling and Danish seining which were also to be banned in the marine spatial plan. Short term fisheries closures are not good enough, we need a total ban on these methods.

Central government management actions to date have been irresponsible. Auckland Council did not take action when it was asked.

If the tipa beds do not recover naturally who will pay to restore them?