Call to Observers On The 2021 update of the Global IUU Fishing Index by Francisco Blaha

Gilles Hosch figures a lot on my blogs, mainly for 2 reasons: he is my friend and I absolutely admire the integrity of his work. To be honest, I don’treally know in which order those two issues relate… but I have known him for over 20 years now… so it doesn’t really matter anymore.

Off for another trip, until 2019 we had over 2000 placements a year in the WCPO

Off for another trip, until 2019 we had over 2000 placements a year in the WCPO

He worked in 2018 on an IUU Fishing Index, that been cited quite substantially (see at the bottom).

I have to admit to a difficult relationship with indexes in general terms… basically, perhaps for personal reasons I never believed that as “one size does not fit all” concept, and is intrinsically hard for Indexes to capture the difficulties that developing countries have in terms of not only implementing MCS measures, how to measure the role of regional organizations like FFA here in the Pacific, but also the complexities of attracting and retaining good officers… one of the best officers I work with, in one of the busiest fisheries ports in the world earns around 21000 USD a year. On the other side, his equivalent in any European country would have less than half its workload, ridiculous amounts of resources, and make 5 to 6 times his income. How does an index capture the impact of this? And I have seen these issues in many indexes.

In any case, if I know about one person in this world that understands those (and the many other) challenges of indexes, and can bring equanimity into them, is Gilles. So I totally support his present work updating it. Furthermore, he is doing this work with Graeme Macfadyen who is another colleague I have also lots of respect for.

Of course, a great (and controversial) source of information are observers, and while the Index is based on more than 40 indicators, 2 of which are sourced directly from fisheries observer feedback – translating into roughly 5% of the Index as a whole.

Observer input into the Index is deemed crucial by my colleagues, in fact, Gilles has noted that “observers are the human eyes and ears of the global fisheries compliance framework, operating directly aboard fishing vessels. Observers see everything that is going on, and after a number of voyages aboard catchers and reefers, and entries into different ports, they start to understand exactly where the “magic” happens. And yet, their knowledge is generally under-leveraged. The Index allows us to overcome these dangers – and the associated code of silence – by eliciting observer feedback anonymously, and in a rather broad manner, in a way that their individual identities and contributions can be 100% shielded and anonymous.” 

Seeing the value of observer knowledge, I encourage all observers reading this blog to go to the survey and to provide their anonymous feedback. Basically, it is just about naming the flags and the ports with which they associate most weaknesses – and associated IUU activity. It should not take the average person more than 5 minutes to respond – but it may add a lot of Q-dos to the Index in terms of pointing the searchlights in the right direction.

The link to the survey is here: https://www.surveymonkey.com/r/GBR2NVY.


Here are some examples showing how and where the IUU Index was referenced in the recent past:

My take on: private certification of labour standards in fishing vessels by Francisco Blaha

This week I was sent two different new voluntary labour certification standards for fishers. The Fairness, Integrity, Safety and Health (FISH) Standard for Crew and the Responsible Fishing Vessel Standard (RFVS).

so you come for a couple of hours and board and then give the vessels owner a piece of paper that says that my worker rights are uphold for the rest of teh year… yeah right.

so you come for a couple of hours and board and then give the vessels owner a piece of paper that says that my worker rights are uphold for the rest of teh year… yeah right.

 I’m not going discuss the individual merits of each of them (I have more respect for the FISH one as there are people I know and respect involved in it, while I don't have much respect for the key people behind the other), but rather what my beef is with private certifications

It shouldn’t come as a surprise I have a very dim view on then for many of the same reasons I disagree with ecolabels or the food quality/safety ones  

While not a full-time specialist on labour on board issues (very few people are), but I been involved in the issue through my work in the development of the FAO guidelines for social responsibility, and unlike most people doing this, I been a commercial fisherman my self. 

 Yet in case of the labour certifications, it gets a bit worst for me personally… I see this as the new “gravy train”... for more consultants in rich countries to make money out poor peoples problems without providing real solutions, only just a "service" to fellow rich people. No idea what would be the cost of certification, surely more than the 350 USD a month a deckhand makes on a Purse Seiner… and I’m sure the companies will not recover it from their profit… but as usual from maintenance and crew payments 

Yes! flag and coastal states have a problem with labour issues onboard vessels they flag or fish in their waters, and these vessels are normally owned by countries that have enough money to have their vessels fishing in other countries (Distant Water Fishing Nations)... and don't be fooled to the fact that if a vessel flagged to Vanuatu, to Nauru (or even to the USA) is owned and crewed by people from that country.

In any case, if you have labour issues on those vessels as is well documented normally a small group of flag states and concerns usually citizen form cheap labour costs like Indonesia, Myanmar, Philippines, etc. For me, the most logical, democratic and cost-effective solution is to set up a programme to strengthen the institutions that are legally authorised to do that job in the country, standardise the systems, and controls under auditable standards and reward conformance in some way. In this case, we have an international convention ILO C188, that has obviously not been adopted by the most problematic flag states, even if those states are members of ILO… so the push to incorporate established internationally agreed standards should be at the flag state and support the capacity building and institutional strengthening necessary there.

What I would not do is to create a private parallel system without legal validity on top off (or to replace off) an already existing national system (there are no countries without labour and immigration departments). And that is what in my opinion private certifications do: they create a parallel system instead of supporting the organisations that are supposed to do the job.

As I said before, In my opinion, one of the biggest hurdles that we face in on this issue (as well as in sustainability) is that while we all want it, we don't what to pay for it and allow the underfunding of official institutions, pay labour, fisheries officers and fishers salaries that are way below mediocrity, but we expect excellence from all of them.

The private certification model was initially based on the ‘theory of change’, and the belief that a ‘market-based’ approach by non-governmental organisations (NGOs) frustrated with the perceived inability of regulators globally to mitigate problems will affect a change for the better. 

Yet even after so many years, there is, in fact, limited empirical evidence that substantial changes in consumer demand for sustainable and ethical seafood have occurred. Producers are also directly affected because they incur the costs of complying with different programmes aligned to different importing retailers and market. Incentives for compliance also remain unclear, given that there is little evidence that price signals are seen by producers, or that any changes in demand have resulted in substantial improvements. 

And it gets worse. Even if the origin of this movement is based on the assumption that fisheries and labour administrators (in particular those from developing countries) are not doing a good enough job, many times during my work with many fisheries administrations in the Pacific I have spent 2-3 days responding to the questions of the consultants that have come to ‘assess’ the fishery for certification… and it would be the same for these standards... so in effect, they come for data to the people and institutions that the ‘consumer’ does not trust! 

That irony for me is mind-blowing. If you really want to help, why not just support the official institutions in the countries whose job and whole existence is to deal with those issues.. 

Having said so, I would not mind these standards existence if they were based on a model pushed by consumers that want extra guarantees and are happy to pay for them. In this case, consumer associations donate to standards developers, or the certification companies themselves source funds from consumers. So if a flag state or an operator wants to be certified, they apply and go through the process with absolutely no conflict of interest. The way now is that they are offering a service to a client, and when the client pays, they want the results… this is just too murky for me.

FAO tell us that over 70% of the seafood consumed in developed countries comes from developing countries. Partly this is because the fisheries in developed countries have either collapsed, can’t keep up with local demand and they can’t find fisherman to do the jobs cheaply. Yet all of the ecolabels, private labour certifications, retailers and most of the consumers that require them are based in developed countries. This has led me to say that I see the whole private certification scene as hypocrisy in the best-case scenario, or neo-colonialism in the worst-case scenario.

Furthermore, I have worked in the past with the developer of one of those standards … until recently the company was in charge of whitewashing FIP for the Tunago fleet in Vanuatu that included the infamous Tunago 61… enough said?  

At least with the ecolabels, they developed some of the assessments points and standards, but these ones copy and paste the relevant guidelines and normative developed by international bodies (ILO, IMO,) for their own profit (since users of the certification pay to be assessed)… so does the owners of the certification scheme, intends to devolve part of their earnings to the referenced bodies that developed the work they are profiting from? Or at least to support the work of the official bodies at the flag and coastal states where the vessel in the UoC operates, that have statutory responsibility under ILO and IMO issues? Otherwise, the certification competes unfairly with usually the labour and maritime department in developing countries as it creates a separate body, and provides for certification holders to potentially say: why you ask me for that? I already have certification on this!

 I recently read in a post from the MSC, with all the fanfare that an Australian Toothfish longliner has been certified to the Responsible Fishing Vessel Standard; “an initiative which aims to improve labour conditions and crew welfare”. I know the vessel operators and they are a good company, the vessels are flagged to Australia, even if Australia is not a signatory of ILO C188 (of which that standard is pretty much a copy and paste) yet.  It has strong protections to fishers via the unions, and foreign crew have working visas... If those conditions are not present the vessels wouldn’t leave port, so it’s hard to see the improvement the standard made on the welfare of the crew... flag state responsibility is to be before private certifications.

Then you have the option to impose conditions as coastal state, NZ confronted with Indonesian crew abuse issues on board Korean flagged joint venture vessels fishing in NZ EEZ a few years ago, took the bold decision of only allow NZ flagged vessels that comply with NZ labour contracts, minimal NZ law remunerations and NZ working visas for foreign crew. The members of the Pacific Islands Fisheries Forum Agency included labour conditions based on ILO C188 as part of their harmonised licensing conditions to allow vessels on their waters, I wrote about this here.

Now check the list of countries that have ratified that convention, none of those countries have known issues with labour abuses on board, yet interesting the hypocrisy that most of retailers and consumers of the developed countries that require these private certifications are not signatories!  I don't see the USA, Australia, NZ, Germany, etc… so why instead of fostering a parallel industry of lucrative certifications marred in a conflict of interest, demand that the flag sates catching the fish your are going to buy (including your own country)  ratifies an agreement that countries as diverse as South Africa, Argentina and Bosnia Herzegovina manage to sign.

I also like to flag the powerful difference between the "human rights due diligence" approach that we worked within last year ("OECD framework") and the old school approach to seafood certification… as my friend Katrina Nakamura wrote 

Not to dismiss good work, as it's great to see initiative from industry, but it is pertinent to share here that the concern is that certification old school style is a failed approach for protecting people from forced labour in the workplace -- a right that is universally in force and backed, as you know, by minimum requirements in the workplace.  It can be hard to see the difference between a voluntary solely private-sector program to prevent forced labour and "human rights due diligence", which is the only approach outlined in the UN guiding principles on business and human rights, which of course responded to the widespread failure of social audits to prevent forced labour. The reason is a simple one. Old school certification has the effect of de-emphasizing and uncoupling the legal obligation of companies to respect rights in the workplace for all people, in ways that comply with the coupled duty of countries to uphold human rights which are universally in force. 

The problem there is awarding a checkmark to large companies for satisfying their legal obligation in high-level policy alone, and for externalizing the surveillance function for working conditions to consultants and away from governments. Both of the 2 new standards out this past week are "old school" that way.   

The fact is, human rights due diligence has landed. Europe is making it mandatory for imports and the US Department of Homeland Security is doing the same. DHS has halted trade on 4 seafood products over ties to forced labour so far and there is every reason to expect this will continue. Last week a major set of withhold release orders was issued for cotton goods and tomatoes made or processed in China. China makes 20% of US cotton so it's like halting trade.

https://www.natlawreview.com/article/united-states-bans-cotton-and-tomato-products-xinjiang-citing-human-rights
https://www.jdsupra.com/legalnews/cbp-begins-2021-with-expansive-new-8626788/

This strategy is going to put a fair amount of pressure on US importers and retailers this year over imports from China and, probably, Thailand, Vietnam, Ecuador and others which are cited by the US Departments of Labor and State for significant forced labour or illegal forms of child labour in seafood processing. Importers will need to show they have systems to trace conditions in facilities in regions that called out, and not only a policy and a code of conduct but a working chain of custody and due diligence to track conditions. There are good people involved in NFI's FISH standard and its timely. My hope is they will take up more of the full "human rights due diligence" agenda to release that pressure. That would land them ultimately right where the Hawaii longline fleet has with its crew management system and community-based grievance committee.

A INFOFISH interview on COVID Impacts, EU yellow cards, my disdain for ECOLABELS, subsidies, climate change and how liberating is to be seen as dumb fisherman. by Francisco Blaha

I have collaborated a lot with INFOFISH over the years, most recently on webinar with colleagues and friends in the Pacific. I like the crew there, there are really efficient, work hard, are friendly, and most importantly not pretentious. I consider the director Shirlene Maria Anthonysamy a friend, she knows my family and she has always been very supportive of my views, the same extents to Firoza Buranudeen the magazine editor and Apii Cokanasiga, their Trade Promotion Officer, just name few in their crew.

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So when they asked me for an interview for the magazine industry profiles section, I knew that is was sincere offer and they were after my personal and independent views, since normally they get more corporate oriented people, that have an agenda or try to sell something… and I’m very aware what a privilege it is to be an independent advisor

So if you are interested, wait for the magazine, download the pdf of the article from here, or read the text below that I paste from the original… is quite a varied interview, that I really enjoyed doing.

On 25 November, you were the Moderator for an INFOFISH-organised webinar ‘Tuna Fisheries in the Pacific Amidst COVID-19’ – thank you for doing such a great job in creating a warm and lively discourse amongst the speakers, which included frontliners in the industry. Would you like to highlight some of the points raised in that webinar, for the benefit of readers who may not have been able to participate?

That was a great opportunity that INFOFISH provided us, and a great opportunity for my Pacific Island colleagues to be delivering their own messages. Among the many issues raised, the one that struck me the most was the social impact COVID has had. I always insist that “Fisheries is People” and this situation has hit the local industries and economies much harder than the Distant Water Fishing Nations that fish in the Pacific.

The devastation caused in the longline industry that focuses on fresh (chilled) tuna for sashimi is sobering. While this segment is small in volume, it is significant in value, and unfortunately is one of the few that have purely Pacific Island domestic investment and employs the biggest number of locals. As fish is sent fresh via airfreight using in most cases, excess capacity on commercial flights, the abrupt ending of tourism has hit some of the islands very hard; jobs have collapsed, and so did this segment of the industry.

The extensive use of around 600 observers in the over 2000 annual deployments we had came to an almost full stop, so they, and the monitors who are generally on-board during transhipment, are now out of work and income. This is a harsh reality for observers in many countries in the region as it is their main source of income, the observer programme having inserted over US$4 million directly into Pacific Island societies. Furthermore, we are not sure how many may have found other sources of work and may not return to observer duties when boarding resumes. Obviously this is a worry, not just from the observers’ employment perspective, but also considering the level of uncertainty that the lack of data for this year (and perhaps years to come) brings to fisheries science and management decisions.

Yet I guess the message that impacted me the most was just the human side of this pandemic; everyone referred to their struggles around work, health, travels, and so on. Everyone acknowledged too, how tough it is for the crew of fishing vessels who cannot even stretch their legs on the wharves for now almost one year, cannot see their families and embrace loved ones. So, while a lot of focus has been on the logistics, supply, demand and corporate difficulties of COVID-19 in the tuna industry, for me the biggest impact is again on the people at the frontline - fishers, local fishing companies and operational officers.

One of the big problems of this pandemic in the Pacific (and elsewhere) is that fisheries observers are not stationed on vessels. An added problem is the relatively weak internet connectivity in the region. Are there any alternate ways in which harvests in the Pacific have been tracked and traced during this period?

Well, these are big and separated problems. The observers issue is one we can hopefully deal with as soon as flights resume and vaccines become available; yet it is one that affects mostly the purse seiner (PS) fleet in the WCPO (massive in volume but small in the number of vessels).

For the longline (LL) fleet, the usual level of coverage was only 5%, so the lack of observers does not affect it too much. Yet the LL fishery is the biggest one in terms of fleet size; furthermore it is the one which identifies as having the highest incidence of underreporting or misreporting. This is particularly true for the high seas fisheries, which normally is the one with the lesser number of observers. And while in principle the WCPFC CMM 2009-06 Regulation discourages transhipments at sea, it has an ‘impracticability’ exemption… yet how impracticability is determined, is not defined or explored. As a consequence, the number of at-sea longline transhipments within the WCPFC area increased by 165% in five years, from 554 in 2014 to 1472 in 2019 and as 2 November 2020, 61% of vessels on record were authorised to tranship in the high seas by their Flag States.

All these transhipments are authorised based on the ‘impracticability’ of going to port but there is no oversight on how that decision is reached by the Flag States involved. In descending order, these vessels are flagged to Taiwan, China, Vanuatu and Republic of Korea, as well as (also in descending order) carriers are flagged to Taiwan, Panama, Korea, Liberia, China and Vanuatu. With this in consideration, the issue of not having observers has impacted more the observers themselves, rather than the actual fisheries. In fact, some units of certification for ecolabels that rely on observers’ oversight have continued even with no observers on board, so that says a lot.

If we had a functioning Catch Documentation Scheme (CDS) across all the fishing nations, an integrated Electronic Monitoring System (EMS) and an integrated electronic reporting system on top of our already very comprehensive Vessel Monitoring System (VMS, it would be fantastic; but if Flag States would just comply with the commitments they made and live up to the expectations of their best performance, that would be a great start!

In terms of the internet, it is getting better, fibre optic cable is arriving at many of the Islands States so it is a matter of time.

You’ve been instrumental in assisting a number of Pacific Island countries in getting their yellow cards lifted, the latest being Kiribati albeit being the longest process. Can you share with readers a glimpse of what has been involved in this process with the countries? What has been the real challenge?

I would never say I was instrumental!! The officers in all the yellow-carded countries I was fortunate to work with are the instrumental ones, I was just lucky to walk a small part of the road with them and share some lessons learned, but that is all. There were two common components in the EU expectations of the carded countries – one was related to legislation/policy while the other was to do with operational and systems… I worked supporting the latter.

For me, the biggest challenge was for countries to understand what the EU wanted from them, particularly in terms of the EU catch certification scheme. The EU did a couple of interpretative flip-flops during the process over a system that had some intrinsic design failures. It became at the end, an export certificate instead of a catch certificate - this meant that non-EU countries had to validate the information on landings or transhipment events that happened months (or even years) before. Hence, if we wanted to set up something that was more than just signing a piece of paper, countries had to set up a system and structure around the catch certificate system that allowed them to run the equivalent of a business accountancy system (but for fish). For countries that are small developing Island States with very limited IT capacities and operational budgets, this was (and still is) a challenge… one that they gallantly confront every day.

For me, two images of the process will stay forever in my mind. During the first visit of the EU inspectors to Papua New Guinea, the lady heading the delegation was asking all these questions and the local officers were trying to understand what she wanted and were not sure what to say. A year later when she came back the same officers were talking over each other as they all wanted to give her the answers she needed! Later on, she told us that not even in many European countries did they have a system like the one in PNG. I always will be incredibly proud of what they achieved there.

As you know, there is growing international market pressure in developed countries (driven supposedly by ‘what the consumer wants’) on fishers and exporters to have an ecolabel placed on their catches/products. However, in a few of your blog posts you have expressed a strong dislike for ecolabels. If we adopt the position that ecolabels are here to stay, what are some suggestions that you could make for producing countries faced with the dilemma of either working towards making their fisheries sustainable, or investing in acquiring an ecolabel?

This is an interesting and contentious one! My objections on the business of ecolabels (and private certifications in general) arise from various angles that are important to me; some are almost philosophical while others technical.

Let me use a parable to explain: in most countries of the world, to drive a car, you need to go through a process of getting a driver’s license run by an official institution in that country. Once you have that licence, you can legally get on the road and drive a car. How good that system is depends on a varied number of reasons such as human resources, cultural values, the rule of law, transparency, etc. Obviously, there would be countries that are better han others at this. So let’s say that a country has a bad rate of accidents by licensed drivers, in comparison with other countries. So what you do?

For me, the most logical, democratic and cost-effective solution is to set up a programme to strengthen the institution that is legally authorised to do that job in the country, standardise the licensing systems, exams and controls under auditable standards and reward conformance in some way.

What I would not do is to create a private parallel system on top of the already existing national system. Hence I, as a driver need to get through the hurdles of the official systems, and then contract a foreign private assessor and go over a whole set of new exams and tests (at my cost) to prove to people in rich countries that I know how to drive in a way they consider ‘safe’. And that is what in my opinion private certifications do: they create a parallel system instead of supporting the organisations that are supposed to do the job.

In my opinion, one of the biggest hurdles that we face in sustainability is that while we want it, we allow the underfunding of official institutions and pay fisheries officers and fishers salaries that are way below mediocrity, but we expect excellence from all of them.

The ecolabels model was initially based on the ‘theory of change’, and the belief that a ‘market-based’ approach by non-governmental organisations (NGOs) frustrated with the perceived inability of fisheries regulators globally to mitigate overfishing, will effect a change for the better. Yet even after so many years, there is, in fact, limited empirical evidence that substantial changes in consumer demand for sustainable seafood have occurred. Producers are also directly affected because they incur the costs of complying with different seafood programmes aligned to different importing markets. Incentives for compliance also remain unclear, given that there is little evidence that price signals are seen by producers, or that any changes in demand have resulted in substantial environmental improvements.

And it gets worse. Even if the origin of this movement is based on the assumption that fisheries administrators in particular those from developing countries) are not doing a good enough job, during my work with many fisheries administrations in the Pacific I have spent 2-3 days responding to the questions of the consultants that have come to ‘assess’ the fishery for certification…so in effect, they come for data to the people and institutions that the ‘consumer’ does not trust! That irony for me is mind-blowing. If you really want to help, why not just support the official institutions in the countries whose job and whole existence is to manage fisheries in a sustainable way?.

The idea that a certified product may get a price premium is not a golden rule; furthermore, the logic of that assumption is flawed. In New Zealand we have argued that the industry should not even expect a price premium for certification noting that: “No plausible case can be made for a premium for ‘sustainable seafood’. If anything, a well-managed fishery should also be a cheaper fishery to harvest as the fish should be more abundant and easier to catch!”

As per the alleged consumer preference, when I was working with FAO GLOBEFISH in 2009, I already had the feeling that we were being told about ‘consumer’ requirements, when it actually seemed that it was more a retailer imposition to create a ‘firewall’ around them by saying that “we sell fish with ecolabels so it should be good!” Personally I see it as a model for retailers offloading ‘due diligence’ to an ecolabel brand their decision-making capacity and expecting producers to pay the bill.

For example, I work a lot in the transhipment hub of Majuro, and I have been many times in situations where I see very similar purse seiners transhipping to the same carrier - both fishing vessels catch the same tuna species, using the same methods, under the same management system, from stocks evaluated by the same institutions, with the same regional controls over the activities, yet fish from vessel ‘A’ that does not pay for the ecolabel process, therefore as the narrative goes, is not sustainable? While fish from vessel ‘B’ that pays, is?

Having said so, I would not mind their existence if they were based on a model pushed by consumers that want extra guarantees and are happy to pay for them. In this case, consumer associations donate to ecolabels, or ecolabels themselves source funds from consumers. So if a fishery or an operator wants to be certified, they apply and go through the process with absolutely no conflict of interest. The way now is that they (ecolabels) are offering a service to a client, and when the client pays, they want the results… this is just too murky for me.

Furthermore, and coming back to the consumer principle, the reality is that 71% of the world’s population live below US$10 a day, of which 45% exist on below US$2 dollars a day. So it is the rich consumer that can afford to have a choice. I work very close to countries where for example, a locally based and owned industry was developed by using their own funds, and they have successfully achieved an ecolabel certification at the cost of almost US$180 000, yet the government budget for malaria and dengue in the province where their operations are, is around US$60 000. I find that shocking - imagine the difference that money could have made at the local hospital! Yet the local company has been almost forced by corporate clients and distributors in developed countries that buy their products, to go through the certification process in order to maintain their supply preference and price.

FAO tell us that over 70% of the seafood consumed in developed countries comes from developing countries. Partly this is because the fisheries in developed countries have either collapsed or can’t keep up with local demand. Yet all of the ecolabels, private certifications, retailers and most of the consumers that require them are based in developed countries. This has led me to say that I see the whole private certification scene as hypocrisy in the best-case scenario, or neo-colonialism in the worst-case scenario.

I also have a lot of technical issues which I have problems with, such as compartmentalisation of catches, the use of observers for commercial interest, their ignorance of subsidies, the reliance on compliance data offered only by the clients, and so on … that would also take a while, and you can read about them in my blog (www.franciscoblaha.info).

This is perhaps another contentious question. The debate on subsidies for fishing has been raging for many years, and there are also many nations (both developing and developed) which have sent their fleets out to the EEZs of other countries where they operate under various agreements. What is your position on subsidies (or programmes which have the same impact as subsidies), their effect on fishery resources, markets, and fishing communities?

Yeah… I always said that if I find the fisheries genie, I’ll ask him for three fisheries wishes: increased transparency, elimination of subsidies, and an income structure for fishers and fisheries officers that reflect the money accrued from their work! But yeah, I doubt I will get to do it!

Of the three wishes, subsidies should be the easier one to fix and even so, there have been negotiations on them at the WTO for over 20 years! This is beyond ridiculous. There has been well-documented evidence for years now that fisheries subsidies contribute to economic losses in the fisheries sector, create serious distortions in global fish markets and push fisheries beyond their realistic economic (and biological) models. They also have serious impacts on food security and livelihoods, particularly in developing countries.

While I’m really against fisheries subsidies, I am aware that their disappearance will not be the magic panacea that will fix all fisheries issues, but at least it would even out the economic playfield, and that would be of massive help.

I always believe that the key redeeming factor of commercial fishing is in the fact that it should be commercial, hence if you don’t make money from fishing, you should not fish... end of story…. subsidies don’t allow that process of natural selection to exist. I also know that there are some so-called ‘beneficial subsidies’ around enhancing management capabilities, R&D, surveillance and enforcement, small scale fisheries support, etc.… I see all that as part of what government responsibilities re, and to be covered by national taxes. Yet, so far the ‘harmful’ subsidies (fuel, fleet support, capacity enhancement, shore operations, etc.) get way more money than the ‘beneficial’ ones… so it is just hypocrisy to promote the belief that the’ beneficial’ subsidies justify the existence of the ‘harmful’ ones.

Even if you think only a little bit about it, is ridiculous that while FAO tells us that 60% of the world’s marine fish stocks are now fully exploited and 33% overfished, governments still pay out an estimated US$35 billion (2018 estimate) on fisheries subsidies, of which an estimated US$20 billion contribute directly to overfishing by allowing fleets to continue fishing beyond the break-even point.

But it also upsets me that they are used for geopolitical issues beyond just fishing – noticeably the biggest subsidisers are the Distant Water Fishing Nations (i.e. China, Taiwan, Korea, Russia, Japan, USA, EU, etc.). These subsidies are not only used for supporting vessels but also many joint ventures including shore-based operations that were never planned to make money, but for foreign companies to have the excuse of being a ‘domestic’ operator. While these companies provide promises on job creation, they gain major tax concessions and cheap fishing rights. After catching the fish, they find some initial excuses such as low labour productivity, high cost of services, etc. Then over time, these become permanent excuses, and they send the raw materials for processing back home or somewhere else.

So there is absolutely nothing good coming from subsidies for those that are not direct beneficiaries of the schemes… and that is most of us.

On to another issue which is of deep (and very real) concern to islands, let’s talk about climate change and its effect on tuna resources in the Pacific Islands region. If, as many studies have suggested, there may be an eastern redistribution in the biomass of skipjack and yellowfin tuna by 2050, most of the islands will see significant decreases in the tuna stocks in their waters. What are your thoughts on how the islands could reduce their vulnerability to climate change? What role could the WCPFC play in this process?

That is a real big one, and the hardest issue we face. Last year the Pacific Island Fisheries Forum Agency introduced a resolution to the WCPFC urging the Commission to:

  • Fully recognise the impacts of climate change; in particular on the fisheries, food security, and livelihoods of small islands developing states and territories

  • Take into account in its deliberations - including in the development of conservation and management measures - the impacts of climate change on target stocks, non-target species, and species belonging to the same ecosystem or dependent or associated with the target stocks

  • Estimate the carbon footprint of fishing and related activities in the Convention area for fish stocks managed by the Commission, and develop appropriate measures to reduce such footprint

  • Develop options such as carbon offsets to decrease the collective carbon footprint associated with meetings of the Commission and its subsidiary bodies.

Which is all very good but this does not stop the impacts we already see. When you read a scientific paper by the leading scientists in the region that the combined catch of skipjack and yellowfin is projected to decrease by 10–40% by 2050 in the Exclusive Economic Zones of Federated States of Micronesia, Marshall Islands, Nauru, Palau, Papua New Guinea, Solomon Islands, Tokelau and Tuvalu… this is hard to swallow... I spend half my years in those countries working there with friends. Tuna is the lifeline for these countries, but the balance of benefits is entirely skewed, in a way that has not moved far from the era of colonialism which is still very recent in this region. A giant country like PNG is ten years younger than me!

And this is an issue of overarching importance for the region since competing interests are impacting tuna sustainability. Also, there is a fundamental (and perhaps unbridgeable) difference; as clearly expressed to me by a friend a few years ago: “for non-PICs and DWFNs the issue of sustainability of catches is one of long-term financial benefit. However, for Pacific Islands Countries (PICs) it is also an identity and food security issue, one that DWFNs have less trouble with as they can leave…but we in the PICs cannot”.

Personally, the issue infuriates me a lot - the Pacific and its tuna gave me a new and good life when I came here in the early 90s, escaping far from my origins and my struggles. The Pacific gave me more opportunities than my own country of birth without expecting from me anything other than honesty and respect. But most importantly it gave me many good friends and an extended family in places that barely figure on maps, yet there is more ‘humanity’ here than in countries whose ‘empires’ cover the earth. So for me it is heart-breaking… the Pacific Islands are the least contributing region to climate change, yet are the ones receiving with full force its impacts, and that is so unfair.

And on a final note, you have had an interesting career in fisheries, from your beginnings in the industry as a crew member on a fishing trawler in your native Argentina; and now as an international fisheries consultant, a trainer in areas such as regulatory compliance, and a well-known operator in the Pacific Islands. What are some lessons you have learned from all the experiences you have had through the years?

That is kind of deep… and I’m not sure I have an answer… I’ve been in fishing for most of my life, started at 18 and I’m 55 now, and I am still learning every day from my (and others’) mistakes, on things that I see working and those that don’t.

I grew up under difficult family circumstances, during turbulent times of social unrest, political violence and war, these it made my relationship with authority a challenging one. Also, being dyslexic, which at the time was seen as being dumb, didn’t help either. And even if I had grown up in a farming area, I always loved the ocean, so while fisheries felt natural to me, I was also an outsider to it. Therefore, in reality, no one had any expectations about my life (nor even me!), so failure seemed inevitable. Yet on the other hand, this was totally liberating as it opened me up to trying new things without pretending to be anything else other than whom and whatever I am.

I have always been very fortunate and thankful to have found people along my way that were kind enough to offer me the one thing I could not get by myself... an opportunity. So I always try to stick to three principles in life: don’t be pretentious, be grateful, and provide people with opportunities if you can.

I’m also very aware and conscious of the privileges I have by being the almost stereotypical looking man for fisheries - a big, bulky and bearded man with skin looking like leather - , of partly European ancestry and the chance to have had an education… surely these factors influenced many of the opportunities given to me. But then this also makes me very adamant in terms of providing for equality and equity in fishing. If my gender, age and background represent the only way to do things, then how come we are facing the problems we have? How hypocritical would it be of me to not bring new voices, new perspectives, new ways to do things! The fact that we have more diversity now than ever before (even if we have a long way to go) is what keeps me optimistic.

So I don’t know if I have lessons to share! Other than to try to do your best and don’t let others be the limit to your hopes, whomever and wherever you are.

Finally, I always quote Noam Chomsky’s words: “We have two choices: to abandon hope and ensure that the worst will happen; or to make use of the opportunities that exist and contribute to a better world. It is not a very difficult choice.”

AIS and labour abuses on board by Francisco Blaha

A recent paper was done by a group of academics in the University of Santa Barbara and people I know from Global Fishing Watch publish (and promoted quite substantially) a paper named “Satellites can reveal the global extent of forced labour in the world’s fishing fleet”.

realities on bard ain’t like what you think at university sometimes

realities on bard ain’t like what you think at university sometimes

Let start with the name hat quite “eye-catching” I guess… I find it always difficult to digest generalizations based on extrapolations.

Don’t get me wrong, the paper has some very good points and I like that explore a different take on the issue of labour rights on board… which is a very complex area to deal with as I wrote many times before.

I was quite keen to see the methodology and how they got their “indicators”  both from the ILO definition of forced labour and vessels behaviours, which is the only thing you can assess from satellite data in reality.

The bit that disappointed me from start is that, as usual with my former colleagues in academia (yes I’m also a proud scientist with 2 Masters in different sciences 10 years apart) is that they did not seem to speak to fisherman or to inspectors directly… which to me would be the logic first point of call: you start with the stakeholders… yet they seem to only have contacted opinion holders. The methodology says:

  • “We next conducted informal phone interviews with experts from several nongovernmental organizations (NGOs) working in this field, during which we asked interviewees what observable vessel behaviours they would look for if they wanted to identify suspicious activity…”

  • “NGO experts and investigative journalism suggest that gaps in AIS transmission, port avoidance, transshipment, and extended time at sea may indicate the presence of forced labor…”

Fisherman will tell you things from the inside, so I will take that role and provide some humble constructive criticism on features and descriptions they use for the model features used for training data (is in the supplementary information annexe)

Average daily fishing hours on days when fishing.

Has to be related to the gear…

  • Longline is the most time-consuming gear and is directly related to the length of the set and weather. 

  • Squid jiggers fish only at night, so it needs to be weighed against latitude and season in the winter night in the 40-50 S (or N) last over 12 hrs, while in summer is 6 to 8. 

  • Trawlers totally depend if they process onboard, what species which determine depth they are targeting… if you aiming deep-sea species like orange roughie setting at 500m means that you have at least 1500 of cable on the winches, so the trawl with a net during fishing of 1-2 hours setting and hauling may 3-4 hrs either side… and once the net in on sinking and fishing you don't need the whole crew on deck… so are they working? Furthermore, once the net is on deck… the vessels are not fishing…. But then is when you really work! either by processing or just freezing and even in the simplest of cases icing… 

There are sooo many variables according to gear… that I don’t know how can you standardize this as to be a useful indicator.

That also applies to Vessel Engine Power, which they have a top 5 predictor of human labour abuses… to the same length of a fishing vessel, trawlers need proportionally way more engine power than a squid jigger or a longliner of the same size (or even tonnage). Just think the physics of trawling as an active gear where the boat has to drag a massive and increasing dead weight behind and below, vs LL or Jiggers where the engine is just used to bet the vessel in position and to move fishing grounds and port…. so I assume they would be some sort of correction factor by type of gear (I could not find it)

These next 3 assumptions, unfortunately I see them permeating in many papers these days:

Number of suspected transshipment events with other vessels. Suspected transshipment events are defined by events when two vessels are within 500 meters of each other, traveling less than 2 knots, and for a minimum duration of 2 hours. These suspected transshipment events may represent transshipment, refueling, or transfer of supplies or crew

Average suspected transshipment event duration (hours): Average duration of suspected transshipment events with other vessels. Suspected transshipment events are defined as events when two vessels are within 500 meters of each other, traveling less than 2 knots, and for a minimum duration of 2 hours. These suspected transshipment events may represent transshipment, refueling, or transfer of supplies or crew 

Average loitering duration (hours): Average duration of loitering events. Loitering events are defined when a vessel is traveling less than 2 knots, at least 1 kilometer from shore, for at least one hour. These events may represent suspected transshipment events if the second vessel is not broadcasting AIS. 

Operationally there are many valid reasons for which a carrier and a Fishing Vessel (or two fishing vessels) can get alongside that do not imply transhipment as defined in the CMM, passing food, gear, crew, parts, salt, oil, etc. name it… it happens! In one case I remember we received the ashes of the captain’s dad who wanted to be spread in the high seas.

Also honestly it takes the best of one hour to tied up securely two vessels at sea, a PS can tranship anything from 700 to 1.3 tons at the time, depending on the made and shape of the hatches (read here if interested) and they could be doing 6 to 10 per hr… so in the best case scenario we are talking 10 tons in one hour… absolutely not worth to use 30 tons as a base… 

This logic can be also applied to Jiggers and Trawlers that tranship with nets from the carrier's winches... yet in their case the fish is boxed or frozen in plastic bags so it is transferred over some sort of pallet structure, yet as i said the size of the hatch is the key limiting factors (other than weather)

For longliners never been on transhipment that took less than 10 hours…. I recently peer review over 20 observer reports on longline carriers and the range was 11 to 50 hrs! so really what can you do in two hrs of which one is just getting the vessels next to each other and then away… 4 to 7 hrs (weather dependent) would be my absolute minimum…

So by having such a narrow description of what is suspected as transhipment you are expanding the risk model to genuine interactions that do not reflect at all the issues at hand. Further, I object the assumption that transferring parts or crew is to be categorised as transhipment, that has relatively clear fisheries definition (see here)

As per transferring crew at sea, while we all agree is not the best, yet depending where you want to fly in crew to transfer, you may face the issue of transit visas... for most of the North Pacific they have to go via Honolulu, for the south Australia or NZ, all of them require transit visa (yes even if you don't leave the airport) for Indonesian, Myanmar, Philippines... In the region had some hope that Air Niugini (PNG) and FIJI airways maintain their Asia flights as there more logical visa restrictions was very positive for foreign crew...at least they had a passport and rcords of travel.... Thailand has pot some better condition on passengers on carriers which is the most common way to transfer crew on purseiners... but for Chinese and Vanuatu flagged (that operate from TW or China) carriers is not really an option.

Finally and under loitering: Loitering events are defined when a vessel is travelling less than 2 knots, at least 1 kilometer from shore, for at least one hour. So this will include what happens with vessels coming in with the 2 pilots we have in Majuro o Tarawa entering the vessels to the lagoon

Flies flag of convenience: A boolean for whether or not a vessel flies a flag of convenience 

Again… take the usual outs (i.e. Panama. Liberia, Vanuatu, etc) you could argue that in terms of labour CN, TW, Korea and the US, for example, act as FoCs by having a crew on board without the protections of labour conditions that would apply to their own citizens, nor the minimum immigration requirements that will apply to foreign workers coming to work in their land for example… which is the case for vessels flagged on those in principle non-FoCs nations.

Maximum distance from port (km): Maximum distance from any port. 

That would be biased against any port in the pacific as it is the biggest ocean and with the lesser # of fishing ports around.

I also have a big issue with the total generalization this one: 

Number of visits to ports of convenience: Number of visits to ports in countries that had not ratified the Port State Measures Agreement (PSMA) at the time of port visit. 

There are many reasons why a country may choose not to sign PSMA while still provide for best standards in PSM (for example RMI, PNG, Tuvalu just to name a few) on the other side of the coin. Countries like Uruguay who has been documented receive vessels that have fished illegally in the south Atlantic was one of the 1st ones to sign PSMA, Vanuatu, a country with an abysmal record of labour infringements on board, is a signatory… furthermore, and as I wrote many times as fisheries inspector I can’t do anything in terms of labour, only since this year, and so far as the only place in the world, for the FFA member countries fishing access and labour issues are associated. In the rest of the world… I can refer the vessels to the labour agency of the port state… but unless I can prove any issues related to IUU fishing, I cannot stop the vessel from departing

So yeah, again, I’m not taking a cheap shot to the crew that wrote this paper, as they are ALL so much better qualified than me... I'm absolutely no one... But I like to think their numbers could be way more accurate if they were to adjust some of the assumptions they made. I think the better ground truthing of the methodology, the more reliable the results would be and the better the tool you trying to use.

My point is that while this paper brings very useful points, yet those could be more accurate and provide a much more realistic figures of the issues… facing that between 2,300 and 4,200 unique vessels were high- risk and between 57,000 and 100,000 crew members were working on these boats and thus potential victims of forced labour, can be quite daunting in terms of the scope of the problem to challenge, yet adjusted numbers can be more manageable with the tools and instruments we have now and this is a start on the real size problem we need to work out. 

As with the book I wrote for FAO on Blockchain, it worries me when the current media discourse that seems to pin the solution to multifaceted seafood value chain problems on one tool – as AIS is. This risks hyper-inflating expectations on what this technology can offer, with potential users then walking away because it does not deliver on the hype built around it.

I hope the authors and my friends at GFW take any of these comments as nasty criticisms, is absolutely not my intention.

The WCPO tuna fishery: 2019 overview and status of stocks by Francisco Blaha

As every year at this time before the WCPFC meeting, the good people of SPC releases this jewel of a report that present the overview of the tuna fishery of the last years and the status of the stock.

The Pacific Community (SPC) is the principal scientific and technical organisation in the Pacific region, owned and governed by the 26 country and territory members in the pacific. In pursuit of sustainable development to benefit Pacific people. The Fisheries, Aquaculture and Marine Ecosystems (FAME) Division includes the Oceanic Fisheries Programme (OFP) and Coastal Fisheries Programme (CFP). The goal of the OFP is to ensure fisheries that exploit the region’s resources of tuna, billfish and related species are managed for economic and ecological sustainability using the best available scientific information. In pursuing this goal, the OFP provides scientific support for the management of fisheries for tuna and associated species, with a strong focus on stock assessment and modelling, fisheries and ecosystem monitoring and analysis and data management. The OFP works closely with member countries and territories, the WCPFC, FFA and PNA, so it does this work as the science provider for the WCPFC.

So if you want to know what is the situation of the tuna fishery in the region, this report is the ultimate reference, is good, concise, well illustrated, and has many reference to further research. (I wish articles like this one in the otherwise quite reputable “the conversation” website were use it as reference)

Majuro plot stock status summary for the four WCPO target tuna stocks, the grid median value is shown as a large dot, the ellipses closely approximate the distribution of values from grid models

Majuro plot stock status summary for the four WCPO target tuna stocks, the grid median value is shown as a large dot, the ellipses closely approximate the distribution of values from grid models

So here is snapshot of the situation

Bigeye and yellowfin tuna stocks were assessed in 2020, the skipjack tuna stock was assessed in 2019, and the South Pacific albacore stock was assessed in 2018. Due to uncertainty in the fisheries data for the most recent year due to COVID, data from the year immediately preceding the assessment year is not included in the bigeye, yellowfin and albacore assessments. Thus, the bigeye and yellowfin tuna assessments include data through 2018, while South Pacific albacore currently includes data through 2016. Skipjack, with its shorter lifespan and importance of young fish to the fishery, includes the most recent year of data; thus the 2019 assessment included fisheries data through 2018.

Summary across target tuna stocks

To summarise the most recent stock assessments for the four target tuna stocks, stock status for all four species are plotted together on a single Majuro plot, along with grid model uncertainties. All four are considered to be in a healthy, sustainable status as none are considered to be overfished. Yellowfin, skipjack and albacore are estimated to have a 0% probability of currently experiencing overfishing, while bigeye is estimated to have a 12.5% probability. To place these results in context, a summary of stock status for these same four stocks assessed in other ocean basins by the three other tuna Regional Fisheries Management Organizations (RFMOs) are illustrated in in the figure below. As most of the other tuna RFMOs report stock status relative to MSY-based reference points (i.e., SB/SBMSY and F/FMSY ), we based the WCPFC status on the same criteria.

comparison of stock status for the same four tuna species in the other major ocean basins

comparison of stock status for the same four tuna species in the other major ocean basins

And while the status of the tuna stock os good (the best of all tuna fisheries in the world), the situation for sharks is bad, and particularly for the oceanic whitetip

Catch and status of billfish and sharks

The status of silky and oceanic whitetip sharks is of concern as assessments have shown that stocks are subject to overfishing and, in the case of oceanic whitetip, severely overfished. A WCPFC ban on the use of either shark lines or wire traces in longline sets is in place, which is hoped will reduce the catch of silky and oceanic whitetip sharks. Over the past several years stock assessments have been undertaken for several billfish and shark species, in addition to the main tuna species. The SC recommendations to the WCPFC are broadly outlined below.

Stabilise stock size or catch/ensure no increase in fishing pressure

  • Southwest Pacific swordfish

  • Pacific blue marlin

Reduce catch and/or rebuild the stock and/or reduce effort and/or enhance data collection efforts

  • Pacific bluefin tuna

  • Southwest Pacific striped marlin

  • Western and central north Pacific striped marlin

  • Blue shark

  • Silky shark

  • Oceanic whitetip shark

Two shark (oceanic whitetip and sillky) and two billfish (Southwest Pacific striped marlin and Southwest Pacific swordfish) species have been assessed by SPC staff in recent years (Figure 18). Stock status for these species is based on the Kobe plot, where overfished status is judged relative to spawning stock size at MSY3. There is considerable uncertainty in the estimates of F/FMSY and SB/SBMSY for all four species. Based on the assessment model grid medians, Southwest Pacific striped marlin and oceanic whitetip are likely in an overfished state, while overfishing is likely occurring for silky shark as well as oceanic whitetip.

Kobe plot stock status summary for four species of billfishes and sharks assessed at SPC over the past decade and for which stock status has been determined. Note that this plot differs from that presented for the target tuna (the \Majuro" plot), be…

Kobe plot stock status summary for four species of billfishes and sharks assessed at SPC over the past decade and for which stock status has been determined. Note that this plot differs from that presented for the target tuna (the \Majuro" plot), because the WCPFC has not yet decided on LRPs for these species and therefore MSY-based reference points are used as a default.

The other worry is of course climate change…

The historical simulations reflect key features of the ecology and behaviour of the four tunaspecies and match the total historical catch in terms of both weight and size frequency distributions. The projections show an eastern shift in the biomass of skipjack and yellowfin tuna over time, with a large and increasing uncertainty for the second half of the century, especially for skipjack tuna. The impact is weaker for bigeye tuna and albacore, which predicts a wider and warmer range of favorable spawning habitat. For albacore, a strong sensitivity to sub-surface oxygen conditions resulted in a very wide range of projected stock sizes. Historical fishing pressure was estimated to have reduced the adult stocks of all four tuna species by 30-55% by the end of 2010. The effects of fishing on biomass strongly outweighed the decreases attributed to climate change in the short- to medium-term. Thus, fishing pressure is expected to be the dominant driver of tuna population status until the mid-century. The projected changes in abundance and redistribution of these tuna associated with climate change could have significant implications for the economic development of Pacific Island countries and territories, and the management of tuna resources, at basin scale. In particular, larger proportions of the catch of each species is increasingly expected to be made in international waters.

A closer look on... Transhipments: a closer look by Francisco Blaha

I have always been a fan of FAO work, their publications helped me lot trough my fisherman life and later on during my consulting career. I’m immensely proud of having been an FAO Fishery Officer, and having my name as an author for one of their “green books” was one of the proudest days of my life, I have done 2 more since then (and doing another two at the present!). Yet for 1st time in all my life, I find myself at odds with one part of the contents in one of their publications.

Fish should not be unloaded until proven legal by the catcher… simple.

Fish should not be unloaded until proven legal by the catcher… simple.

Transhipment: a closer look, is the product of  “The In-depth Study on Transshipment” that was been carried out with the assistance of the European Union (and this will become important later on), and while I was aware of the consultation I was not involved (never asked to be involved either). (Full document here)

As someone that works and specialises on the topic, I had an immediate interest on it… nicely produced and illustrated. But then when I started reading their “definition” of transhipment:

Transshipment” – meaning the transfer of catch (i.e. fish and fish products) from one fishing vessel to another fishing vessel or other vessel either directly or indirectly through other vessels, (so far so good for me! but then…) vehicles, points, containers, installations, facilities or premises used for the carriage, storage or facilitating the transfer or transit of such catch prior to the landing – is a widely practised fishing-related activity in all regions of the world and in various fisheries. I was dismayed…

Furthermore, the publication has an illustrated example of a vessel landing and then loading fish into a container… I just totally disagree with that being called transhipment… Not that it really matters as I’m just an ex fisherman and I’m sure that the people involved in this publication are very well known fisheries administrators and academics.

But just because I was a fisherman… I’ll make a point of my opinion being expressed.

This is not transhipment in my opinion.

This is not transhipment in my opinion.

Ok, let go by parts… English is not my 1st language… but in these aspects I like it: 

Transhipment – in between two ships… easy. Landing: something touches land… simple

But no… the document somehow defines the term “landing” in this context means a process through which a shipment or cargo of catch is documented or declared to have been subjected to the prescribed process of entry into a country or to have been cleared as an import by customs or the competent authority of the port state.

Sorry, but how come a vessel is authorised to unload (either transhipment or landing) without the catch being “documented or declared to have been subjected to the prescribed process of entry into a country”.

You see (in my humble opinion) this is wrong.

Reality is that by definition of most RFMOs (and the EU IUU regulation) transhipment "is the transfer of fish in between two vessels"

points in case: 

  • Transhipment is defined in the WCPFC Convention as meaning “the unloading of all or any of the fish on board a fishing vessel to another fishing vessel at sea or in port"

  • for the EU 1005/200810:‘transhipment’ means the unloading of all or any fishery products onboard a fishing vessel to another fishing vessel; (the EU IUU reg specifically mention that container vessels don fit into the fishing vessel category!)

  • IOTC defines around transhipment conditions for donor and carrier vessels, but not for container vessels... 

  •  and so on

My take is that when fish is landed as per FAO PSMA (or just PSMA best practices) it falls under the PSM responsibilities of the country that is hosting that landing... even if the fish was just landed to be put in a container. The exporter, in this case, is not the vessel, but the entity that is exporting the containers

We had issue already in the pacific with EU catch certificates because fish landed and put in containers in Kosrae (FSM) was sent to EU as it was transhipped, when in reality it wasn't. Furthermore from the sanitary side, as on as the fish is landed in a country that is not authorised by the EU as equivalent in terms of seafood safety, that fish loses eligibility for the EU (that is the reasons RMI is trying to become an EU authorised country), so fish can be landed, sorted and containerised for export and still eligible for the EU, even if processed in Thailand or Vietnam.

We get a lot of slack from Chinese and Taiwanese operators for not signing section 7 (transhipment in port) in the EU Catch Certificate since the operation of unloading to the wharf, sorting and containerization does not fit the definition of transhipment in the EU regulation, and we don’t want more yellow cards. So now those operators are pointing to this illustration and saying you guys are wrong…

In fact, since Thailand got hard on PSM the increase of fish arriving in container skyrocketed as a way to go around PSM controls, as that fish fall out of PSMA since it was lander before. 

I also interacted with one of the authors on this and he raised the following valid points (in italics, to which I answer in normal text)

Landing is not defined in any the legislations and RFMOs. 

But for me, the fact that landing is not defined, while a worry, can be seen as an advantage because transhipment is defined... i.e. vessels to vessels... so any other stuff that happens we can argue what to name it: landing, wharfing, whatever... but is not transhipment... which is exactly my point!

In various regions where the catch is directly offloaded from catching vessels to containers which are then almost immediately loaded onto a container vessel – without oversight or involvement of any authority – fisheries, customs or otherwise, especially when this activity takes place in what is considered “private” ports – where the only documentation of what is going on is potentially only from the vessels themselves or their agents and that this practice continues to grow. There are some that do not consider these instances to be a “landing” and instead just a movement of the catch from one vessel to another while in port.

I've seen that in a few countries, yet those containers are never in a container vessel (you need sorting/handling space which is not available in the deck of a container vessel). Furthermore, container vessels are on very tight port schedules, it can take over 48 hrs -non-stop- to unload a PS based on hatches sizes, for example, a day or more for a Longliner as fish comes out 1 by one… Hence containers are on the wharf and will be moved around by a vehicle and will be kept refrigerated via electricity mains that are powered from the land, not the vessel. So whatever we call that... it is not transhipment as defined in the legislation (and again that is what I'm driving here).

To add to this point… is that those unloading operations from the vessels, the loading of the containers etc is to be authorised and monitored by fisheries and surely customs, otherwise imagine all the "other stuff” you could load in.

The global reefer fleet is really not getting bigger and they are not really building new reefers to take the place of the ageing ones, the world is moving more and more towards containerization – and the movement of goods by container which includes an increasing fleet of container vessels so, the case of the same catcher vessel coming into the same port but this time, instead of a reefer being there, there is a container vessel if the catcher vessel direct offloads to a container which is then directly unloaded to the container vessel, there are some that may view that as a transhipment rather than a landing – the transfer of catch was driven by a logistics choice…i.e. the availability of a container vessel and containers vice an actual reefer.

Interestingly, not long time ago I wrote about this recently. I believe that COVID would encourage refitting of the present fleet and potentially some new vessels. In any case again...the schedule of container vessels is much tighter than the schedule of fishing boats... so the logistics angle may play to the fact that you may unload faster the fishing vessel as to load to a container, and the container will be hoisted to the container vessels and plugged there. yet for container vessel to accept a container it needs the "Bill of Lading" for the consignment, otherwise, it will not accept them for reasons ranging from due diligence to cargo insurance. Different container handlers have variations on the maximum weight of fish in containers (20 to 25 tons) so these need to be weighed in somewhere and crosschecked with the Bill of Lading...

Also, no fisherman on earth will let go of its fish without a document with the weight of the fish he is passing off... at any unloading you'll have a crew representative checking the weights (that is why captains are really keen on the scales we were using during transhipments). Point is that there would be always some sort of paperwork (official or not) going on when fish gets into a container... So from the operational and logistics side is a matter of fisheries and customs to join in, because the paperwork is happening even if purely only from the commercial side 

Yet again as per the definition this process is not strictly vessel to vessel... and I don't think that nor WCPFC, IOTC, EU, etc include container vessels in the definition of "fishing or support vessels" definitively PSMA does not either, which also a corollary of the "vessel to vessel" definition. 

when various Conventions such as WCPFC and IOTC were agreed, the use of containers for moving catch was not a dominant activity where the activity occurred at a level where there might have been a need to actually define “landing” in the list of definitions so that it could clearly capture the requirements of the activity of a “landing” if and when it occurred, especially through direct offloads to containers. 

Yeah, that is true... and containerisation is (as I wrote in the blog above) a really attractive option that needs deeper analysis. Yet for example, our very simple PSM SOPs that I was involved in implementing in RMI, PNG and Noro (Solomons) include the process of authorisation of port use (which includes the unloading of fish) based on the analysis of identity, licensing and operations of the vessels prior arrival, then monitoring of unloading either landing or transhipment, and the if landed irrelevant if goes to a container or to a cool store is all tallied, and then an export authorisation is given either as whole fish or as processed if it went to factory... So is not too hard, can be done and is consistent with PSMA

I guess I agree to disagree with this publication on this aspect… and I worry that if some people associate landing, sorting and containerisation as part of transhipment we going back in the advances we made already.

The whole point of PSM is that if the catching vessels cannot prove that the fish was caught in compliance with the licensing conditions port use is denied… end of the story.

Already Transhipment in the HS is a loophole to this… but at least is more identified. Now I find it weird that we could this way allow a vessel to get their potentially IUU catches into the value chain by calling the landing a transhipment to which you cannot do much until the fish gets to the destination via the realm of the custom oversight (fisheries rarely gets involved with containers)… at least in the specific transhipment definition (vessels to vessels) fisheries is to be involved the same way that fish to land… and again doesn't matter if it gets to a container to be sent away or to the factory to be processed and then send away.

Fish does not become IUU along the value chain, fish Is caught IUU and should not come out of the boat until its proven no IUU. 

the abuse of the impracticability exemption for at sea transhipments of the WCPO longline fleet by Francisco Blaha

I have been quite slack with the blogging, lately… in what use to be my “normal” job until February I’ll be all day away doing stuff, getting n baits, working on VMS analysis, and so ion… so to read something and write things other than the end of mission report was great…. Now I’m struggling to get away from a screen! 

Actually Mola-mola are quite practical to tranship

Actually Mola-mola are quite practical to tranship

But also I feel I keep recycling things like the issues of transhipments in the HS at the WCPFC… In 2018, WCPFC15 recognised the need to review how transhipment is managed and monitored by forming an inter-sessional working group (IWG) to study the effectiveness of CMM 2009-06.

So interested I’m that I was asked by my colleagues in MIMRA (Marshalls) to be their nominee to replace the departing co-chair in the IWG (my friend Sam Lanwi that is now the 2nd in command at the RMI embassy to WTO and UN bodies in Geneva).

Unfortunately, even if I’m operationally a MIMRA “officer” I get paid by the NZ government, and that put me in a weird situation as a rep of another country… anyway… I’m heavily involved as a technical officer in the working group.

The situation is a mess… In principle the CMM discourages transhipments at sea (TS) with an impracticability exemption… yet how impracticability is determined, is not defined or explored… as consequence the number at-sea Longline Transhipments within the WCPFC Area increased 165% in 5 years, from 554 in 2014 to 1472 in 2019 and as 2 Nov 2020, 61% of vessels on the record were authorized to tranship in the High Seas by their flag State.

All these transhipments are authorised based on the "impracticability" to go to port. They correspond in descending order to longliners flagged in Taiwan, China, Vanuatu & Korea, and go (also in descending order) to Carriers flagged in Taiwan, Panama, Korea, Liberia, China & Vanuatu.

obviously long lining is getting way more impractical.

obviously long lining is getting way more impractical.

This is just not good enough… on top of that with the COVID situation, the very few observers and at-sea inspections have been cut to limit the potential exposure of fishers, observers, and inspectors to the virus. While these steps are necessary, they also increase the urgency of updating and strengthening WCFPFC’s transhipment measure to ensure proper monitoring and reporting.

And I focus here on Longline only…because is, in my opinion, they are of more risk… I depart substantially of the opinions in this recent paper “Toward transparent governance of transboundary fisheries: The case of Pacific tuna transhipment”, that focuses on Purse Seiner. While their approach is to call (based on a prior paper of 2018“potential transhipment, is defined as any occurrence in which a reefer and a purse seine vessel are fewer than 500 m from each other for more than 2 h, while located more than 10 km from any port” 

Operationally there are many valid reasons for which a carrier and a PS can get alongside that do not imply transhipment as defined in the CMM, passing food, gear, crew, parts, salt, oil, etc. name it… it happens! In one case I remember we received the ashes of the captain’s dad who wanted to be spread in the high seas.

Also honestly it takes the best of one hour to tied up securely two vessels at sea, a PS can tranship anything from 700 to 1.3 tons at the time, depending on the made and shape of the hatches (read here if interested) and they could be doing 6 to 10 per hr… so in the best case scenario we are talking 10 tons in one hour… absolutely not worth.

Anything implying transhipment for me is from 4 hrs up, and that is the measure we use in Majuro when we detect vessels proximity while at sea for more than 4 hrs… we go and check the temperature records of the wells and dry lockers to see if they got open (ergo temperature spikes) during the time aside… the only time we found something was  that they have received frozen pigs to distribute with other vessels for Chinese new years :-)

Furthermore, it assumes a total silence by the observers… of which PS have 100% coverage, and while I may believe that you can induce the silence of a few, definitively not of all… for what? 100-200 tons in a 1000 tons vessel…. Yeah...Nah. I reckon is good to have a fisherman reviewing the drafts of the papers before setting hard limits. 

Anyway… back to operational issues…  I’ll like to define over some basic issues like to clarify what “impracticability” really looks like... as to potentially identify a certain number of parameters may need to be accounted as to claim "impracticability"  

For example position at the time of requesting authorisation, distance to ports at that moment vs distance to rendezvous place with a carrier, distance travelled by the donor vessels to the carrier in function of the carrier being based at the nearest port... and so on

While on the other side, legitimate impracticability reasons such as weather conditions in a way to closest port, bunkers distribution, fuel consumption - just as some examples are also to be considered.

I believe that an important outcome of the info required is to provide information that facilitates the way to a future agreement for of a standardised procedural process to be followed by flag states and/or coastal states before authorisation to tranship in the HS is given, and that the burden of proof for "impracticability" needs to be demonstrated through due diligence prior to the transhipment to be approved...

Particularly because the crosscutting issues that the "impracticability" exemption needs to be leveraged against... as there are a lot of other WCPFC CMMs that pivot to a different extent on this impracticability.

  • Under and Misreporting

  • Observer Coverage

  • EM

  • Labour issues

  • Safety at sea

  • MARPOL

In the meantime, inside the present framework of the CMM, there are some issues that can be much better of what they are now

Observer reporting forms and submission requirements need to be improved

In 2017, the Secretariat reported at the 13th Technical and Compliance Committee (TCC13) meeting that they had received only one observer report for the 958 high seas transshipping events that were reported to have occurred in the Convention Area in 2016. Since then there have not been any other apparent observer report submissions to the Secretariat, so it appears that the Secretariat has received only one observer report for the 4,931 transhipment events that occurred between 2016 and 2019.

While most other tuna RFMO Secretariats have access to transhipment observer reports, the lack of access for the WCPFC Secretariat undermines its ability to independently verify the information reported by transshipping vessels.

There is insufficient sharing of data on transhipment operations between WCPFC, IATTC, and NPFC

A recent geospatial report published by The Pew Charitable Trusts (Pew) cross-referenced satellite AIS data track histories of carrier vessels and movement patterns consistent with transhipment behavior against publicly available information on carrier vessels and transshipments reported by the WCPFC Secretariat and Commission members. The report found that in 2016 there were high concentrations of carrier vessel activity and potential unreported transshipments in two WCPFC overlap areas —the IATTC/ WCPFC overlap area and where the NPFC Convention Area spans part of the WCPFC high seas area off Japan. These three RFMOs all have different reporting and observer carriage requirements, making it difficult to determine which RFMO rules and procedures a carrier vessel is, or should be, operating under in dually managed waters at any given time. As a result, the amount and type of species transshipped by a carrier vessel in such waters may go unreported to the appropriate RFMO authorities.

 Discrepancies exist in transhipment reporting within WCPFC

The 2020 WCPFC Annual Report on Transshipment reveals discrepancies in notifications and declarations received from offloading and receiving vessels. For instance, Panama reportedly received 380 transshipments yet provided only 318 notifications and 377 declarations for the 2019 reporting period. Other members and cooperating nonmembers have similar inconsistencies, with only China and Liberia meeting the notification and reporting requirements for all transshipments. In total, 95 notifications and 4 declarations were not submitted by CCM carrier vessels, and 57 advanced notifications and 17 declarations were not submitted by CCM fishing vessels that transshipped in 2019

 Additional sources of information are needed to effectively verify reported transhipment operations

According to the 2019 WCPFC Annual Report on Transshipment, the Secretariat undertook an analysis of VMS data to attempt to detect potential transhipment events. The Secretariat specified that an incident would be counted as an event when “…the reported WCPFC VMS positions related to two fishing vessels, are estimated to be within a distance of 250 metres, over a time period of at least 4 hours.” Overall, the VMS system only detected 23%t of the over 3,200 transhipment events that were reported to the Secretariat during the time period of interest. In order to improve the accuracy of the tool, and consider AIS data analysis. This is another useful tool for increasing the transparency of transhipment activity. Given that the VMS polling rate for longliners is once every four hours, supplemental use of AIS data could be used to gain a better understanding of the length of time a transshipment at sea takes place within the WCPFC Convention Area

A review of CMM-2009-06 found key areas that need improvement

WCPFC is one of the only RFMOs that allows at sea transhipment exemptions for small scale purse seine vessels, purse seine vessels operating exclusively in-zone, for troll, longline, pole and line vessels, etc. These exemptions and ambiguity make implementation inconsistent and allow for even more transshipments to occur than initially envisioned when Article 29 of the Convention was drafted. The WCPFC transhipment resolution also differs from those in many other tRFMOs in that it does not apply to the whole Convention Area.

As we discussed earlier… the present system ain working… no is no… so if you don’t like it go fish somewhere else.

Webinar on Tuna Fisheries in the Western and Central Pacific amidst COVID 19 by Francisco Blaha

A while ago the great crew of INFOFISH asked me if I could help to organise and moderate a 2 hr webinar on the impact of COVID in the pacific tuna fishery. As I know them well, I said I will agree with two conditions:

  1. we should only have people from the pacific, front liners, young people and equal gender representation as much as possible if possible, and

  2. no private certifications trying to sell us their products

And I loved when they agreed! In fact, I also wanted to pass the role of moderator to one of my pacific colleagues, but they told me I should keep it as I know everyone involved personally, I been to everyone’s house, many have been to mine and we trust each other… which is a very important thing.  

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If I could, I'll organise it as if we were around a bowl of Kava on a big traditional canoe floating somewhere, just chatting like the friends we are… I’m not one for the over formality and pomposity of some of these events, you still can be totally professional, without having to be stiff. So join us by registering for free!

 One of the things I’m excited about is the opportunity of having a small panel chat with front liners in the region, these are the young woman and men at the face of the fishery in the vessels, wharves and factories, in some cases doing the boarding, or remote compliance, dealing with the disruptions in processing, and the logistics of running fishing boats in these strange days

As I insisted many times… Fishing is people, and people in the pacific is families... so I will be trying to make it a relaxed conversation among colleagues on our region, I like to hear not just the "institutional" views but also personal impacts… in fishing people are not part of the jobs, they are their jobs 

The keynote speech will be by my good friend Pamela Maru, now the boss at the Ministry of Marine Resources  Cook Islands. Pam and I go a long time, when she was still an officer in the Cooks, then she became a powerful engine at FFA, she one of the people that understand the working intricacies of the WCPFC better than anyone. She has been to my place, knows my family (is an honorary godmother to my daughter Kika), I been to her place many times, know her family… shell is one of the people I have the biggest amount of professional and personal respect in the fishing world. I’m totally honoured to have it on board.  

Then Dr. Transform Aqorau, will be giving some of his insights… (if you have an interest in Tuna and don't know Transform… then you need to go back to learn bout Tuna in the pacific). I was honoured to illustrate with my pictures his recent book on PNA. Again, we go back a long time. I have been his guest and he is taking good steering on the eNoro project, something that is very close to my heart. 

Then is the front liner panel with some of my younger colleagues and friends…

  • Saurara from Fiji whom I know for over 15 years now since I first trained her and now we are consulting colleagues in many projects, and I have passed her all the opportunities that arrive at my desk on in regards processing, CA. EU market access and so on.  She is amazing, we worked together in for a few years in Kiribati, and besides doing a stellar job, she did her MBA, while being a mother two the two great kids she has, I got to also meet her awesome husband that is such a great and supportive guy.

  • Then is Beau Bigler whom we work a lot in RMI, besides being one the most driven and smarter fisheries officer I work with he is total waterman, so far the only officer I have worked with that we surf, paddle and fish together and also the only one I have cycled to work!

  • I”m hoping to have also Kikiva “Slota” Tepaia from Rabaul in PNG, one of the few places in the region where boarding still happens, so his insights of working during COVID will be amazing. He is a total character, devoted to his works, and very good photographer, as well.

  •  Finally, I’m hoping to have  Cynthia Wickham, who also is family to me! She is part of one of the coolest fishing families in the world, and the fleet manager for NFD In Noro, the place that for me represent what fishing should be in the pacific, she is frontline, right at the wharf while being the mother of a young child. I’m soo looking forwards to her views.

While everyone talks about the lack of observers in the vessels, no many are talking about what is happening to the around 800 observers in the regions that haven’t worked since February! So I wanted to bring that reality to the front… and who better than two former observers that have moved to really senior positions in different institutions 

  • First would be Sifa Fukufuka, Training Coordinator of SPC’s Observer Programme. Sifa was f the 1st generation of observers in the region and a trainer to everyone after him, his view on the observer world, their training and their reality are unique… I’m totally looking forwards to listen to him.

  • Then is my friend Glen Joseph, who is at the same my boos as the director of the Marshall Islands Marine Resources Authority and the Chair of the Parties of the Nauru Agreement (PNA). He actually was an observer himself and got to his position based on being trailblazer and someone that is always creating the paths others will follow. He has been a great supporter of my work and my respect for him is up there with Pam and Transform 

To finish we have my friend and fellow former fisherman Brett Haywood, that knows harder than anyone the impact that COVID has had in the fresh longline sector… he will be speaking on his role as the Chairman - Pacific Islands Tuna Industry Association, but also the manager of Seaquest a company in Fiji that was ahead of its time with blockchain-based traceability I reported in the past

So yeah a packed agenda to go through, and a time frame that does not make any justice to the capacities and experiences of the people on board

But please join us by clicking here, love to see you having some kava with us.

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On being part of the Waiheke Marine Future Search Hui by Francisco Blaha

As I wrote before, it has been weird to be working as I’m working now. The last time I was out of NZ was in February... so these 8 months have been my longest period at home in the last 20 years! And also the longest I have not been on a fishing boat since I was 18 years old!!! At a personal level, I'm missing a bit of “my reality”... my personal and professional life are every intertwined so having some sort of small island routine ( as I live in one!) it gets repetitive sometimes

Another type of fish :-)

Another type of fish :-)

On the other side... my running, swimming, canoeing, surfing, and cycling km logging have been excellent! and it has been good to be home for the veggie garden and to rebuild stuff with my wife. Work-wise has been also good, lots of small jobs of the type I don't really like much, writing, policy analysis, seminars. 

Yet interestingly it gave me the chance to reconnect a bit with NZ fisheries, a part of my life I left partly behind but I always care for.

 As part of that relationship (and the fact that I’m here), I’ve been invited to be part of Future Search Hui (Maori term for an assembly) organized by the Waiheke Marine Project among some of its activities. 

Future Search is a globally utilised, large scale planning event which brings the ‘whole system’ into the room. It is an action based, facilitated, programme to find common ground across diverse voices.

This multi-day Future Search event is starting this Friday 30 October and will run for 3 days, it will bring together approximately 70+ people to dialogue, reach common ground and agree on action to protect and regenerate the marine environment of Waiheke Island.  

The Future Search planning group of diverse voices selected the 70+ Future Search participants after a period of ‘casting the net wide’ for voices from mana whenua, fishers & boaties, scientists, marine commercial operators, land interests, youth, conservationists, agencies & politicians and Waiheke locals.

And I have to say I’m quite impressed with the quality of some of the people coming, I’ve known a few professionally and personally and I’m looking forwards to meet some others I know about, but never meet personally

 The outcomes will contribute to an eventual presentation to the Ministers of Conservation and Fisheries and the Ministerial Advisory Committee of Sea Change targeted in December 2020. After that, the Waiheke Marine Project will change form into one that supports the collaborative actions generated by the Waiheke Community to protect and regenerate the seas around Waiheke Island.

What do I bring to the table? 

Well… I’m an ocean person, it is my life… and it has been since I was a 12 years old cadet in the navy. My job and my recreation are based there…. I'm a long-distance ocean swimmer, a surfer, a paddler, a sailor, a spear-fisher, and also do some fishing with lures out of my waka -ama (outrigger canoe) either rowing or sailing. I’m quite committed to non-motorized fishing, I’m against the recreational use of combustion engines on land and sea (even if I’m a big visible man I've been run over by a cars while cycling and running and by a boat, while swimming, in all cases recreational users at the wheel, and have some bad scars to prove it, unfortunately)

Professionally, I’ve done the range from a commercial fisher, a fisheries technician/observer, a fisheries scientist, a fisheries officer for the UN FAO, a trainer of fisheries officer, an intelligence analyst for fisheries organisations, and a compliance specialist for quite a few international agencies and governments,

And if that wasn’t enough, I’m an immigrant!…hence I can be everyone’s friend or enemy… depending where you stand.

 So yeah… I may have something to collaborate with, and while my position is clear in my head (wrote about it here) I’m going to listen to others over the 3 days. 

I’m actually looking forwards… hui and long conversations to achieve consensus are a staple in the guarani culture I grew up, and in the pacific cultures I live and work. 

Honestly, I have no idea if it will work and have an impact after... yet I would know even less staying from the outside without listening to what is said.

Are you a specialist on Plastic Waste Disposal Practices? by Francisco Blaha

If you read my blogs, you may be aware of my interest in issues around plastics at sea, particularly when they come from fishing, goes back in time. and here is a potential consulting opportunity for someone with the right background to join me on a tender for a job assessing plastic waste disposal options and practices for FV in the central and western pacific. You bring your experience and I add my one on fishing and the region.

lots of it

lots of it

Read below and if you still keen, get in touch!

The adoption of the WCPFC Conservation Management Measure (CMM) 17/04 on Marine Pollution, (championed by the Republic of the Marshall Islands) coming into effect on 1 January 2019m was a big win for the pacific island countries

 Clause 2 of the CMM specifically states: 

CCMs shall prohibit their fishing vessels operating in the WCPFC Convention area from discharging any plastic (including plastic packaging, items containing plastic and polystyrene) but not including fishing gear.   

As of January 1, 2019, all fishing vessels operating in the WCPFC Convention Area are explicitly prohibited from dumping any plastics into the ocean. This is potentially an excellent step towards curbing drastic levels of plastic marine pollution. However, the reality of current plastic disposal methods is in stark contrast to the intention of the measure. 

As I wrote beforeA typical tuna longline vessel will set around 3000 hooks per set.  The hooks are baited via 10-kilogram boxes which contain 100 – 120 pieces of bait. The boxes are waxed cardboard and each has a plastic liner to contain the bait and two plastic straps to seal the box. Therefore, with each set using around 30 boxes of bait for each set of 3000 hooks there are 90 pieces of plastic generated, to make numbers easier let’s assume only 1000 longliners setting every day (in reality there are more than that), that represents conservatively 90,000 pieces of plastic per day or 630,000 pieces of plastic per week and 2,520,000 per month, as well as 30+ pieces of waxed cardboard overboard for each vessel each day!

 As far as has currently been ascertained, outside of Australia and New Zealand, only Fiji has licensing provisions that require the retention of plastic waste on board locally based and licensed vessels for disposal onshore.  

 It can only be concluded that a considerable number of high seas longline vessels dump plastic waste from bait boxes in the ocean every day. Furthermore, plastic pollution from fishing vessels, particularly plastic strapping from bait boxes, is implicated in direct impacts on numerous endangered, threatened, or protected species.  

The problem of plastic waste disposal at sea is not limited to just longline vessels. FFA/SPC recently coordinated a focused Observer trip on board a Vanuatu Flagged Taiwanese Carrier vessel undertaking transshipment with longline vessels operating on the high seas. The subsequent trip report noted as follows:  

“Unfortunately, pollution incidents were common. MARPOL signage was abundant, but plastics were continuously thrown into the sea. There were properly marked bins on deck, but they were not emptied when we were in port. A poignant moment was watching three juvenile oceanic whitetip sharks chewing on the kitchen waste, which included plastics”.  

With the exception of clause 2, the majority of the language in the measure is well-intentioned, but light in the use of directive terminology, using terms such as “CCMs are encouraged” or “shall encourage” and “CCMs are requested.” In addition, the measure lacks a clause to define enforcement of clause 2 such as inclusion in any compliance monitoring scenario beyond flag state reporting.  

For pacific island countries, we can potentially utilise license conditions or regulatory inclusion of text in support of clause 2 of the measure or consider the adoption of clause 2 enforcement as an addition to Harmonised Minimum Terms and Conditions (HMTCs) we all share.  

However, this does not account for high seas operations unless DWFN CCMs also move to adopt mechanisms to enforce clause 2. It would be an imbalance to place restrictions on domestic based vessels, which do not apply to the high seas.  

The standard argument against this is likely to be that there is just no means for high seas vessels to dispose of plastic bait box waste other than into the ocean. However, in reality, this is potentially not the case.  

In the case of domestic-based vessels, waste can possibly either be disposed of on return from sea or prior to departure. Consider the scenario where bait boxes are emptied into bins (such as are standard storage containers on most vessels), then these bins can be stored with 3 boxes of bait per bin and stowed in the freezer to be used as required. 

There would also seem to be potential for this to apply to carrier vessels loading bait for delivery to longline vessels, but this could involve the large plastic bins commonly utilised for fish holding on vessels and in ports.  Significantly, this could also provide additional leverage to improve observer coverage and reporting on transshipment or carrier vessels as well. 

In another scenario, the suppliers of bait boxes could be encouraged to use waxed paper box liners and bind boxes with twine or tape which can be more easily stowed on board with the bait boxes and liners being burnt

The job:

The aims of the study at hand are to undertake research, investigation, and consultation to provide a detailed analysis of the following:    

  • An estimate of the amounts of plastic waste generated on a per vessel basis by vessel type and operation.

  •  A summary of current fishing vessel plastic waste disposal practices in FFA Member Countries and adjacent high seas areas.

  • An estimate of the volumes of fishing vessel plastic waste that is being directly dumped into the ocean and a review of the potential impacts of this practice.

  • A summary of the range of mechanisms for plastic waste disposal from fishing vessels other than oceanic dumping and how these could potentially be applied.

  • Consideration and recommendation of practices that could be adopted to mitigate oceanic plastic waste disposal from fishing vessels, the associated costs, and how these practices might be applied.

  • In considering mitigation practices, take account of the current and potential impact on port waste disposal infrastructure using three examples of high fishing vessel traffic ports such as Suva, Noro, Majuro or Pohnpei.

  • Provide consideration as to possible strategies and actions that could be taken at both national and regional levels to eliminate all plastic waste disposal at sea.

 

The output  will be a detailed technical report and associated appendices 

We will be required to submit a draft report for comment and review, and take account of comments before compiling the final report.

 So yea… if you keen… Let me know


 

On being a operational fisheries guy stuck behind a computer by Francisco Blaha

I assume I’m not saying anything new around the fact that this has been a very crazy year… that affected everything in my professional and personal life… not as much as on what I do, but also on how I do my job.

a computer based consultant with a outdoor routine

a computer based consultant with a outdoor routine

Let’s start by being clear that I’m well, I’m healthy… which is an incredible privilege, as I personally knew quite a few fisheries colleagues outside the Pacific that are not alive anymore.

Personally, I’m incredibly thankful to my clients since I found my self with way more work than I ever expected for someone that is normally involved in operational projects... and this is soo good... 

At the moment I’m working on: 

  • An FAO study on the identification Critical Tracking Events (CTEs) and Key Data Elements (KDEs) along the seafood value chain (for both wild capture and aquaculture)

  • An FAO study on Current technologies for recording information on-board deep-sea fishing vessels

  • The 2020 update of the FFA IUU quantification study with MRAG

  • Writing an Inspection manual for officers in west African flag states

  • Continuing with my role as Offshore Fisheries Advisor for MIMRA (RMI)

  • Providing technical support to PEW and Stanford University

  • A transparency enhancement projects with WWF and a major NZ fishing company

  • Support to FFA on PSM, CDS and IUU NPOAs

  • A contract with UNPD supporting the potential creation of Joint Management Area in the Indian Ocean

  • Plus 3 proposals for different jobs on the social side of fishing that are on the pipeline

Working from home, sitting in front of a computer with innumerable zoom calls and writing technical documents… is not what I normally do (nor what I do best). Normally my work plan is calendar-based: 20 days in some country, a couple of weeks home, 1 month on another country, home… and so on… not 10 jobs at once, doing small bits every day.

So I really miss my old reality... my personal and professional life are every intertwined, so my present life with its routine it gets repetitive and lonely sometimes. 

Last time I was out of NZ was in February... so these 8 months have been my longest period at home in the last 20 years! And the longest I have not been on a fishing boat since I was 18 years old!!!

On the other side...  it was very useful to reset things at home with my family, have my veggie garden very productive, and furthermore, my running, swimming, surfing and cycling distance logging has been excellent!

So yeah… but I’m very conscious on how privileged I am, and that as many in rich countries I can afford to evaluate about how COVID has impacted our lives, yet for an immense (and mostly invisible to us) majority of people in the world, shitty or no jobs and hunger was, is and will continue to be their only reality. 

And on that note, I salute with my full respect my colleagues at the World Food Programme for their totally deserved recognition with the Nobel price

Effect of pelagic longline bait type on species selectivity by Francisco Blaha

As I wrote before, for my 2nd thesis (2000) I developed a bait for the longline fishery of snapper in NZ (that later became this paper), and had to get deep into the science of longlining and got to interact with the guru of this gear Dr Svein Løkkeborg, that still is, in my opinion, the person that understand at best the complicated events that have to happen from the moment that you set to the moment that you haul your fish on deck.

that was me once upon a time…

that was me once upon a time…

I based my thesis on the development of a bait for the longlining fishery of snapper (Pagrus auratus), using different proportions of industry surplus Greenshell™ Mussel (Perna canaliculus) and gurnard (Chelodinichthys kumu), which are known to be part of the snapper diet.

Both these species contain large amounts of glycine and alanine, which are known to stimulate feeding behaviour in snapper, and are substantial part of processing residues in the NZ industry, so I did the whole research diving into environmental chemoreception by fish, baiting technology and sausage-making process (best way to store bait), then tested the baits in a Snapper farm and working on small demersal longliners of the east coast of NZ.

I compared the results for 1000 hooks of my bait against the same quantity of hooks baited with control squid bait. And squid was 83.93% more effective compared to my bait… so that wasn't very good… although the catches with my bait were low, the selectivity for snapper over the standard mix of species with squid) was 29.25 % higher, which was very encouraging.

Since them… among my way too many interests are the chemistry, effectiveness, handling and price of bait (see here) but in particular against squid as bait… that it seems is mostly caught to then be used to catch more expensive fish. 

So when this paper “Effect of pelagic longline bait type on species selectivity: a global synthesis of evidence” by Eric Gillman and other researchers came trough my screen, interest was immediate. And while the article does not dwell on the topics I did, it touches close to the aim of my thesis, even if I aimed at a demersal species:

No studies were identified that found an artificial bait to be economically viable for use in pelagic longline fisheries. Developing an artificial pelagic longline bait that retains acceptable catch rates of market species but reduces catch risk of species of conservation concern warrants investment in research and development.

Furthermore, it does raise a key issue… catching more of all, or catching less but more specific?

They say: 

A related research priority is to investigate potential socioeconomic effects on pelagic longline fisheries from changing bait type. For instance, would it be economically viable for an artisanal fishery that currently catches squid to use as longline bait to replace this quasi-free bait source with purchased fish bait, and would the change in catch rates of market species caused by this change in bait type be viable? Understanding the ecological effects on the stock status of forage fish species, and socioeconomic effects on food security, from increased demand for these species for use as bait by longline fisheries, and estimating the conservation gains to species of conservation concern from reduced longline fishing mortality that could be achieved from changes in bait type, are additional research priorities.

Here is the abstract … yet read the original!

Fisheries can profoundly affect bycatch species with ‘slow’ life history traits. Managing bait type offers one tool to control species selectivity. Different species and sizes of marine predators have different prey, and hence bait, preferences. This preference is a function of a bait’s chemical, visual, acoustic and textural characteristics and size, and for seabirds the effect on hook sink rate is also important. We conducted a global meta-analysis of existing estimates of the relative risk of capture on different pelagic longline baits. We applied a Bayesian random effects meta-analytic regression modelling approach to estimate overall expected bait-specific catch rates. For blue shark and marine turtles, there were 34% (95% HDI: 4–59%) and 60% (95% HDI: 44–76%) significantly lower relative risks of capture on forage fish bait than squid bait, respectively. Overall estimates of bait-specific relative risk were not significantly different for seven other assessed taxa. The lack of a significant overall estimate of relative capture risk for pelagic shark species combined but significant effect for blue sharks suggests there is species-specific variability in bait-specific catch risk within this group. A qualitative literature review suggests that tunas and istiophorid billfishes may have higher catch rates on squid than fish bait, which conflicts with reducing marine turtle and blue shark catch rates. The findings from this synthesis of quantitative and qualitative evidence support identifying economically viable bycatch management measures with acceptable tradeoffs when multispecies conflicts are unavoidable, and highlight research priorities for global pelagic longline fisheries.

 

 

Not all is fisheries work in Majuro by Francisco Blaha

I miss being in Majuro… not been there for over 9 months, and is my 2nd home in the Pacific. I’m part of a community there, with work colleagues, my host family, and a bunch of water misfits that I got to know there: fishers, sailors, surfers and spear-fishers.

Yet as keen ocean paddler and swimmer, it really struck me that in one of the most beautiful and protected lagoons in the Pacific…. there weren’t any outrigger paddling canoes in the country to get out there enjoy the ocean and meet people after of before work, and compete in the Pacific Games.

So i decided to change that, and with the amazing support of some of my misfits friends and the support of the NZ Ministry of Foreign Affairs Northern Pacific Development Fund, we got it done!

Sadly I will not be there for the rigging and blessing of the canoes (Waka Ama as we call it in NZ), but I can wait to go back and get out there.

This article from the Marshall Islands Journal tell the story of the newly formed Majuro Ocean Sports Club

MIJ Sep 18 20 P15.jpg
we even have a logo

we even have a logo

Fisheries Observers and discards by Francisco Blaha

A classic by line we always had here in the pacific to suggest that is a good idea for longline vessels owners to increase observer coverage, is that observers are good luck on board, because observed trips consistently produced higher reported catches than non-observed, so when an observer is onboard, the vessel catches more fish!

Off to be very observant

Off to be very observant

This recent paper by Hunter T Snyder and James T Erbaugh on discards in artic fisheries seems to confirm the universality of that concept! 

The last paragraph of their discussion (read the original!) puts it quite clearly: 

 In Greenland, in a region with world-class fisheries enforcement, the underreporting of discards is extensive. Our findings that underreporting exists—be it intentional or accidental—underscores the need for fisheries managers and enforcement entities worldwide to understand the extent and the origins of underreporting. Improved understanding of how discards are produced is an important next step for minimizing discards and conserving marine resources. While command-and-control enforcement with fishery observers significantly alters catch reporting behavior, it is time to develop more inclusive, transparent, and collaborative approaches to deal with fishing fleets' waste of living marine resources.

This paper makes me reflect on something that has been lingering on the back of my head during these times of limited observer coverage due to COVID… while we can potentially assess statistically the estimated level of underreporting that does take place during these times (in comparison to other years)… I hope the level of uncertainty being caused does get reflected in the management measures being decided at the present.

Even if the whole set up seems to (falsely) assume that observers do not range along the spectrum of humans that go from the really moral ones at one end to the bluntly dishonest at the other... 

As an ex observer and a professional that has more than 30 years of interaction with observers, I’ve seen and experienced the best and the worst of the professional and personal attributes they have... yet is statistically indisputable that their presence on board increases compliance and in this paper proves it for reporting accuracy as well!

A schematic illustration of how skippers fish and report catches.

A schematic illustration of how skippers fish and report catches.

The “back end” needs of cameras on board (EM) by Francisco Blaha

I have been working on the side-lines of EM in the Pacific and writing about it for a while now… and I say EM (Electronic Monitoring) as it is more than just a camera like the ones in the dash of a car… is a combination of cameras, computers, GPS and gear sensors on vessels, and a lot more of systems inland as to provide data to help managers, scientists and vessel owners effectively manage fisheries.

With the suppression of observer coverage in the WCPO and politics in NZ, a lot is being written about EM internationally and nationally

this is the set up for 6 vessels that take 2-3 weeks trips each… it take in avg a 5 to 7 days to “observe” a full trip.

this is the set up for 6 vessels that take 2-3 weeks trips each… it take in avg a 5 to 7 days to “observe” a full trip.

The cameras onboard are just the visible tip of the iceberg when it comes to EM, this blog is just to explore some of the other key infrastructure and services that are needed for cameras/sensors on board to work as a solution. As with other technologies, I fear that the hyping in the current media discourse pinning them as the solution to multifaceted seafood value chain problems (from IUU fishing, birds/sea mammals conservation, labour issues and maritime crime) risks hyperinflating expectations on what his EM can offer, with potential operators then walking away because it does not deliver on the hype built around it.

Don't get me wrong EM is a great tool, is the next step in a road started by ER (electronic reporting) less than a decade ago and it would be ubiquitous in the next decade. Yet, to rush EM into the vessels at the present with all the logistic challenges we have is pushing the advances made by EM so far into the risk of failure and losing a lot of the good ground gained so far.

EMonitoring should be seen as what it is, one of a range of tools that can be used to monitor commercial fishing activities, in addition to onboard observers, port state measures, CDS, E-Reporting and the lot. A tool box full of different tools helps governments collect a wider range of data to help make informed decisions and combat illegal, unregulated and unreported (IUU) fishing.

What are we talking about?

A camera e-monitoring system usually consists of wide-angle digital cameras, a GPS receiver, gear usage sensors, storage and processing devices, and a display screen. Sensors can collect data about boat locations and when fishing gear is being used. Cameras record imagery that can be analysed for determining the effort (number of sets, hooks or baskets), the total catch (species, approximate length, life status and fate) and other noticeable events (e.g. transhipments, crew behaviours). They are “closed systems” that do not allow for manual input or changes to data that is stored.

image by Archipelago Marine Research Ltd

image by Archipelago Marine Research Ltd

Sensor data can be sent in real-time via satellite to national Review Centres, and to regional databases, yet normally footage from cameras is stored on a removable storage device that are provided to a Review Centre once the vessel returns to port. There is flexibility around whether analysis is conducted at the national level and then provided to regional agencies or vice versa. 

image by FFA/WWF

image by FFA/WWF

A feedback report can be sent to the captain of the vessel, to ensure that they keep the systems maintained with cameras and sensors operating effectively. A trip report is sent to the fishery manager and compliance officers to alert them of any issues.

Where are we in the WCPO terms of EM?

Trials of EM systems for monitoring the activities of longline fishing vessels licenced to operate in the Pacific Island Countries and Territories began in 2014. There are now 73 longline vessels equipped with EM systems. The table below summarises the number of longline vessels per country equipped with an E- Monitoring System, the number of EM analysts trained and working, the number of review computers available and the number of analysed sets received in the EM database at SPC.

WCPFC-SC16-2020/ST-IP-08

WCPFC-SC16-2020/ST-IP-08

The EM records are mainly analysed by national fisheries authorities and sometimes by EM providers. Some of the resulting EM data (vessel, catch, set, haul and location details) have been sent to SPC and are available for its member countries to query and report on using the online tool DORADO.

 Currently for FIMS data is being received from a provider to the FIMS EM module. The EM data received is then displayed in FIMS and available for review. At this time the data does not relate to the video footage.

Standardised calibration and use of digital measuring tools are needed towards being able to use EM data (species and length) in stock assessments. These needs can be addressed through the establishment of an EM certification programme detailed further below

The EM application in the region focuses on identifying many activities. Cameras may identify interactions with bycatch species, and are especially useful when recording bycatches of protected species. The viewed data can also provide a secondary source of data, for example, to validate catch and bycatch logsheets.

The goal of EM is to provide a cost-effective monitoring solution capable of collecting data for scientific, management, and compliance purposes. Surveillance cameras installed on vessels have proven to be effective at recording crew and fishing activities, which can be checked for compliance with fisheries regulations. As such, camera monitoring that is integrated with Electronic fisheries information solutions (EFIS) can provide a useful means of validating vessel catch and gear reporting (hook numbers, use of wire tracers on longliners or FAD deployment and setting on FADs during the prohibition period).

The sensor data is especially useful in identifying steaming, setting and hauling. Sensors may also be inserted into hooks, or added to brails to weigh the fish on transhipment.

Cameras can also be an effective tool to monitor Health and Safety issues. A skipper can monitor crew activity from the deck. It may also be possible to detect any possible threat to observers, noting the loss of life of three PNG observers in the past four years.

EM has certain limitations and cannot replace the roles of other data gathering techniques entirely. For example, current camera technology does not offer an affordable and reliable means of identifying the sex, age and species composition of a catch sample. Some observations are difficult to make from camera footage/images, even with human input and specialist knowledge. Furthermore, camera setups (unless extremely elaborate) will generally have ‘blind-spots,' where the crew could discard bycatch, hide interactions with TEP species, or perform other IUU activities which could then go unreported.

As a result, while some see camera monitoring as a viable alternative to onboard human observers, others feel that on-board observers will remain necessary for the foreseeable future, at minimum to perform biological sampling and compliance monitoring where cameras are insufficient. The reality is that EM systems can complement the role of human observers and enhance overall observer coverage most particularly in the longline fishery.

Comparability of data EM vs Human

Lot of work has been one in the region by comparing the data obtained from the cameras with the data from traditional observers working in the same boat, and as my friend Malo Hosken (the SPC researcher on this topic) said: very few differences were noted between the overall species composition of the main tuna species between the two observer types indicating that the E-Monitoring footage is providing sufficient information for identification to the species level. There are several examples where it is evident that the species identification and catch coverage from the E-Monitoring video analysis are better than the on-board observer data.

One benefit of E-Monitoring is that it provides a means of reviewing footage of the video repetitively and by a number of people (e.g. including experts in species identification). With more time, further review of the data compiled from these trials could be undertaken to resolve differences between the on-board observer's record and the original E-Monitoring video analysis record to determine where the problem lies.

Furthermore, substantial advances are being made at the present regarding software tools that cannot only identify length but as well species, opening the door for fully automated analysis of video data. In these cases, the human observer analysing the footage comes only to resolve the events that the software hasn't. This technology has the potential of speeding up the analysis massively, allowing verified to enter the databases in near real-time at some stage.

EM service providers have been researching and developing software to use Artificial Intelligence (AI) solutions to aid in the analysis of EM records. Given that it is expected that more longline vessels will be equipped with EM systems, the need for efficient analysis of a growing volume of EM records means the use of AI software will be essential. However, for EM service providers to develop AI software which meet members’ needs, a large volume of EM records and corresponding EM data are needed. For example, if AI is going to be used in aiding the identification of species, at least 5000 images for each species are needed (at minimum).

These EM records and EM data are currently available and belong to the respective members who have produced them. There needs to be a discussion on how, collectively, members can benefit from ensuring EM service providers gain the records and data they need to pursue AI developments (which will result in proprietary software).

The Nature Conservancy (TNC) has launched an open library of training data to accelerate the implementation of AI in fisheries. For further details please go to: https://www.fishnet.ai/home

In early 2020, one EM service provider and one member country began trials of a Machine Learning Server. Equipped with an Artificial Intelligence algorithm, the Machine Learning Server points the EM analyst towards the start and end of setting and hauling operations as well as when a catch event occurs. This removes the need for the EM analyst to review video records where no activities are taking place, in turn augmenting the analysis rate.

A further challenge is environmental variability, which can make visual recognition difficult. Conditions at sea are particularly challenging – variable light, splash and spray, different vessel and background configurations. Similarly, fish may be in different orientations or stacked on top of each other – presenting additional challenges for accurate classification. This may make the use of AI more likely on belts and chutes as the technology is rolled out.

Finally, the market for EM systems is currently small, which makes it difficult for an EM vendor to make a large investment in research and development when AI may only have applicability to a small number of systems. And in cases when someone else is doing the video review (e.g., in a government center), the vendors have a little financial incentive to invest in AI development.

Despite these challenges, there is a lot of ongoing effort to advance AI for EM video analysis. While the hope is that it will eventually enable complete capture of species, length, and volume data, the next steps are going to advance in AI-assisted review (e.g., identifying key events). 

This all exciting stuff but it comes at a huge cost, since a lot of this technology is proprietary and system providers sell you the systems and the software but then you have to pay for updates, or they sell you the subscription… and you tied up to a continuous budget for it that can change… is not so easy

Footage delivery logistics

Live video footage through satellite transmission is not cost-effective at present, so footage is stored on a hard drive and sent monthly, or after each trip, to the provider for analysis. The Marine Instruments e-eye system does provide for an integrated Iridium modem, which allows for real-time data transfer. This also allows for less HD space needed for photos and longer periods at sea.

While there is provision for this facility in most systems, the cost of transmitting still frames, as opposed to live footage is still prohibitively expensive, and quite impractical because of the high volume required for transmission. 

Due to the size requirements of video footage, large on-board data storage facilities are required. Cameras film at 5 frames per second (24-30fps is movie standard), and use between 60 and 100 MB per hour of footage. A four-camera setup requires 240 to 400 MB per hour, which results in around 6 to 10 GB for each full day of recording. 1280x720 @ 24FPS on board (HD quality) and minimum recording capacity of the system is 13-14 weeks. 

Due to these dataset sizes, video surveillance footage cannot feasibly be sent in real-time via a satellite feed. Instead, it is usually transferred directly from the hard drive after retrieval. The HDDs are changed very easily onboard and can be examined at the control centre. Videos are stored onboard and encrypted. Videos are extracted locally from the encrypted HDD for analysis ashore by the owner or the Observer Program.

The process of hard drive data retrieval and footage review and analysis is currently relatively slow, taking a few days for dispatch, forensic recording, and then data viewing (~ 3-6 hours) depending on the recording requirements.

Since hard drive exchange is the most trailed option, it is the primary model being considered for video retrieval for current EM development efforts any form of EM implementation can expect complex logistics associated with this option due to the many ports across multiple countries with varying degrees of infrastructure visited by thousands of participating vessels.

For the EM system to work effectively, vessel owners and operators who submit the hard drive should have confidence that the data seen by the reviewer accurately reflects what was recorded on the vessel, as confirmed by a reliable chain of custody and supported by data encryption. 

In a place like NZ, this could be worked out, vessels could turn over hard drives to a dedicated collector stationed at each major port. These collectors could be trained staff affiliated with MPI or a 3rd party observer program.  

The collector should be able to meet vessels, swap hard drives, and upload video in a local office to transmit via Wi-Fi or physically pass off the hard drives to the appropriate centralized video review office. A locker system could also be used so that pickups and drop-offs would not require a person to be available the moment a vessel comes into port.

Hard drive retrieval methods do not limit the risks associated with mailing physical hard drives from remote ports with limited infrastructure.

There is a challenge for FFA or WCPFC secretariat to determine whether hard drives can be sent through certified mail services or via courier throughout the entire region. But even for papers this present challenge in the WCPFC, in COVID times without flights, this option is not available for most ports

Furthermore, vessels fishing in the HS that may not come to port for periods longer than a year would depend on the various carriers at sea to interchange HD, which is not realistic at the present.

Footage review

The time it takes to analyse footage is dependent on various variables. A present estimate (with the present level; of AI/Machine Learning capabilities is 1:15 (1 hour takes 15 mins to view/analyse), assuming the analyst is someone that knows how to operate the proprietary software and has a good understanding of the licence conditions, fish and species of special interest ID and fishing operations. Reality is that It takes time even in the best of cases…

At the present in the pacific, we have reviewers from third-party vendor and government fishery agencies.

Government Fisheries Agency video review has been undertaken by the fisheries with the support of external funding. This option can be attractive to states that prefer to maintain control of the video footage from fishing in their waters, and it can generate jobs for the local economy. This review option may also be attractive for at-sea observers who would be strong candidates to become EM analysts ashore in a review centre, although the jobs are quite different.

A data review centre is a complex operational system. Establishing such a centre will require countries to increase budgets, purchase review stations, hire and train staff, to review a huge volume of video particularly if it is centralised

If not centralised, there are inefficiencies to having different ports or regions set up their own review centre instead of consolidating the review process. Experience from pilots in the pacific has demonstrated the challenges of building efficient in-country review capacity, with cases of long backlogs, and difficulty getting local reviewers to meet the same level of review efficiency as third-party vendors. EM pilots have also shown a wide variation in the performance of national review centres, and this type of variability across a state or worst across RFMO member states could be detrimental to an EM program. 

The draft FFA Longline EM Policy commits the FFA Secretariat, SPC, and Parties to the Nauru Agreement (PNA) to collaborate to provide technical support and training to EM review centres, a signal that there is a recognition of the challenge of building and operating these centres and that many countries will need assistance. One possibility to mitigate the cited difficulties is to create sub-regional review centres.

Third-Party Review – Other countries contract the service through a third party. This could be a commercial EM vendor or a quasi-governmental agency. Under this model, the government or industry contracts with a third-party entity to review the video and deliver processed data that meets the set of specified standards (e.g., data fields, quality, timing, review rates) (we have that at the WCPFC). This can be a more efficient way to handle the review of data as the government can act solely as a contract manager instead of building its own capacity to review EM video from scratch. If local jobs are an important concern, it may be possible to structure contracts to require the hiring of in-country reviewers. For low wage countries, the third-party approach could be more expensive than analysing the data themselves, but the start-up costs and inefficiency of building a review centre from scratch could limit the cost savings

Costs

To date, most of the costs for EM programs in tuna fisheries have been paid by NGOs and international organizations, but this model will not continue forever. Currently, much of the enthusiasm by coastal states for EM is related to the idea that in the future, industry will be responsible for paying most, or all, of the costs. The draft Regional Longline Fisheries Electronic Monitoring Policy formulated by FFA member countries states as a guiding principle: “User pays - full cost recovery as a default.” Many segments of the fishing industry feel that costs could be high and are also uncertain about how an EM program will affect their business. As the group that will be most impacted, they may believe that it is unfair for them to be entirely responsible for funding an EM program. This difference of opinion on who should pay for EM is seen by many as the most significant impasse for EM implementation.

Many reports on EM state that a major advantage of EM is its cost relative to human observers. However, human observers can have a cost advantage where observer wages are low (e.g., in Pacific Island countries national observer programs).

The costs of EM are also quite clear and immediate, while the benefits of EM can be more uncertain and diffuse. For example, there are costs of inadequate knowledge of fishing activity (e.g., depleted fisheries) but those costs are not very clear, especially in fisheries with limited data. 

EM costs fall into four categories:

  • Type 1: On vessel costs. These costs are associated with the installation and operation of EM hardware and supporting systems on board fishing vessels.

  • Type 2: Program administration and operational costs. These costs are associated with the administration and operation of the EM program, usually undertaken by national (or regional) fisheries administrations. These costs typically form the ‘core’ of the annual EM program budget, and would be a main focus for cost recovery.

  • Type 3: Policy and regulatory development costs. These costs are associated with the establishment of relevant regulatory and policy arrangements to support effective EM systems.

  • Type 4: Analytical costs. These costs are associated with the analysis of EM generated information to produce outputs in support of the administration and management of fisheries by national fisheries administrations (e.g., production of reports analyzing annual trends in EM information).

For example: the EM pilot project funded by FAO for the 50 tuna longliners based in Fiji operated for three years (2015- 2018). The total fixed and variable costs for the three years were US$986,575, which came out to US$6,577 per vessel per year. The pilot was able to review approximately only 44 % of the EM trips over the pilot’s duration.

Servicing EM Hardware Systems

The experience from EM pilots and fully implemented programs has contributed to improved reliability of EM hardware. Nevertheless, EM hardware may break or malfunction, so it is essential to have a good servicing plan in place that clearly articulates responsibilities and minimum levels of service. 

In the EM pilots, major repairs were often undertaken by EM technicians who needed to fly to the repair site – a time consuming and expensive approach. Even when only a phone consultation was needed, time zone differences between the vessel location and the EM vendor could result in significant delays.

With these challenges in mind, EM programs will need to set clear service expectations with the EM vendor, and ensure that maintenance issues are promptly addressed. EM vendors can use a variety of approaches to meet these requirements, such as training local capacity (e.g., marine electronic technicians), engineers, or deck crew to undertake common repairs, placing EM technicians in-region, or providing 24/7 remote consultation. 

Given the length and remoteness of many fishing trips in the region, empowering captains and crew to make EM repairs at sea will be important. This will include supplying spare parts, providing additional training on certain maintenance functions, and establishing communication protocols for technical support at sea. 

Equally important to creating a servicing plan is setting the obligations for vessels that experience equipment malfunctions. Vessel operators should be required to perform basic functions to keep EM hardware in working order at sea, such as ensuring that the lenses remain clean and that camera views remain unobstructed. If a system malfunction, operators should be required to report it immediately to management authorities. The vessel would then need to follow an agreed procedure when the EM system malfunctions. 

The strictest option would be to require vessels to return to port immediately. This would be a strong deterrent for intentional sabotage of EM systems, but could also place significant economic burdens on the fleet, and could potentially be a disincentive for fleets and flag states to participate in an EM program. 

Other options could include a risk-based approach, where vessels that have demonstrated strong compliance may be allowed to continue fishing, while less compliant vessels would be required to return to port. 

A limited number of exemptions for malfunctions may also be considered (e.g., a vessel can keep fishing for the first malfunction in a calendar year).

With some vessels taking trips several months in length and far away from port, the decision of how vessels need to respond to a malfunctioning EM system is likely to have a larger impact in the WCPO than in other EM programs in which trips are typically shorter and closer to shore.

EM Policy

The importance of policy cannot be underestimated, as you need to compare apples with apples, be able to define for what purpose the data is going to be used. Know the limitations you have with it, particularly if you going used for compliance! Do the fisheries law have the needed strength to deal with this type of e evidence?  Do we need to think what ty[pe of prosecutable offences may not be covered by EM? I imagine based on some of the very hardcore lawyers I know from my fishing days, that they could drag prosecution for months based on technical issues if there was to be some crystallized sea salt in the lens particularly when it comes to undersize fish… and so on.

In October 2019, a regional workshop was held at FFA to draft the Regional Longline Fisheries Electronic Monitoring Policy. The policy was drafted with inputs from members, secretariats, industry and NGOs. The draft policy was presented at the 2020 MCS WG and FFC meetings and was adopted on 19 June 2020. The purpose of this EM Policy is to describe a regional framework that, inter alia: 

  1. supports collective action at a strategic level; 

  2. promotes a level playing field in relation to the implementation of EM and mitigates against market distortions; and 

  3. facilitates economies of scale for national and regional benefit.

EM minimum data field standards and training of analysts/observers

The adoption by WCPFC of ER and EM standards is expected to support and accommodate those CCMs that have commenced implementation of a range of EM and ER technologies in their fisheries and will ensure that the Commission's databases and systems are ready to exchange electronic data in an orderly and efficient manner.

The SPC/FFA/PNAO Data Collection Committee met in February 2020 to revise the draft DCC Longline EM minimum data fields standards. These standards are proposed for member countries to use when embarking on trials or implementation of E-Monitoring (EM) for longline vessels licensed to operate in members’ EEZs (and adjacent waters). These standards should be provided to the EM technical provider to ensure the minimum data fields specified within are generated from the EM system, according to the EM Protocol notes provided. These standards are in draft format and will be presented to the WCPFC Scientific Committee (SC16-ST-IP-07) and ER and EM Working Group meetings in 2020.

Standards for the training, assessment and certification of EM Analysts and observers using E-Reporting tools

Units of competencies for EM analysts and observers using ER tools were presented to the PIRFO Certification Management Committee in 2018 and subsequently adopted by FFC in 2018. To build on these, Members have identified that there is a need to develop curricula to guide the training, assessment and certification of EM Analysts (staff responsible for analysing EM records) and of observers using ER tools. Building from the success of the Pacific Islands Regional Fisheries Observer (PIRFO) competency development programme, SPC and FFA members support the concept that a training and development programme for EM Analysts and observers using ER tools be established within PIRFO programme.

Strengths, Challenges, and Opportunities for EM Tuna Fisheries

There have been numerous trials and fully implemented EM programs in the region. These trials have covered both longline and purse seine fisheries. From these trials, some general conclusions can be reached about the efficacy of EM as a monitoring and compliance tool

Strengths of EM

  1. Provides accurate data on the location and time of fishing activity.

  2. Accurately assesses the set type in purse seine fisheries.

  3. Accurately estimates total catch per set in purse seine fisheries.

  4. Provides good estimates of the catch of main target species in longline and purse seine fisheries.

  5.  Identifies most Endangered, Threatened, or Protected (ETP) species interactions.

  6. Incentivizes more accurate reporting of data in logbooks.

  7. Covers multiple views of the vessel at the same time, does not require breaks, and video can be reviewed multiple times.

  8. Is less prone to intimidation, bribery, or interference in order to falsify reported data.

  9. Review of much of the fishing activity can happen at high speed (e.g., >8x speed).

  10. A space efficient solution for longline vessels with limited room for a human observer.

  11. Can sometimes provide cost savings relative to human observers.

  12. Helps document conformity with management measures and international obligations.

  13. Scalable option to implement on various vessels with different gear types.

Challenges of EM

  1. Accurate estimates of non-target species in purse seine and longline fisheries can be challenging with EM depending on catch-handling techniques and camera placement

  2.  Identification of ETP species may only be accurate at higher taxonomic levels (e.g., shark or turtle, but not at the species level). However, additional or higher resolution cameras may be a solution.

  3. Accurate identification of juvenile tuna (e.g., small yellowfin and bigeye) is difficult, although this is similarly difficult for human observers.

  4. EM systems are not linked to fish aggregating device (FAD) buoy identification systems.

  5. EM is not currently suitable for biological data collection (e.g., sex identification, otolith measurement), which could be addressed by complementing EM with dockside sample collection.

  6. EM cannot be used to accurately assess the condition or life status of fish.

  7. Hard Drive Collection logistics are very complex and will hamper the application on HS vessels.

  8. Fisheries Legislation may need to be changed as to incorporate new forms of electronic evidence and even types if fisheries offences where EM evidence can be used.

Emerging Opportunities of EM

  1. EM has been explored to monitor labour practices onboard vessels, but no results of comprehensive studies have been published in the literature.

  2. EM is being explored as a tool to monitor transhipments.

In general, it is easier to extract detailed information about catch in longline fisheries where the catch is brought on board one fish at a time, but EM has proven successful in purse seine fisheries as well. In some cases where EM has not been able to match reported data from human observers (e.g., species-level identification of non-target catch), changes in catch handling procedures or additional camera views may be able to overcome these challenges.

Many of the design choices are operational or technical in nature (e.g., what hardware should be selected, how much footage should be reviewed), but perhaps the most important lesson from the development of other programs is that “[getting an EM program adopted] is a people challenge not a technical challenge.

The reality is that, like most new solutions, there will be opposition along the way. Industry members will likely have concerns about additional monitoring, privacy, the costs of the program, and a general fear of the unknown. Fisheries managers may be concerned about the cost and complexity of the program and whether they will be able to effectively manage it. These concerns are legitimate and have emerged in the development of most, if not every, EM program. These issues cannot be sidestepped, and stakeholders need to be integrated into the design process so that their concerns are recognized and addressed. In particular, the industry needs to be involved as they will be the ones most impacted and their acceptance of the program will be critical to its success.

There are real challenges to developing an EM program, and the characteristics of particular fisheries can make this a bit more complex, but these are solvable challenges. Yet, to rush EM into the vessels at the present with all the logistic challenges we have is pushing the advances made by EM into the risk of failure. 


References:

Roadmap for Electronic Monitoring in RFMOs by Mark Michelin, Nicole M. Sarto, Robert Gillett

Analysis of the costs and benefits of electronic tracking, monitoring and reporting systems applied in FFA countries and identification of the required legislative, regulatory and policy supporting requirements. Banks R, Muldoon G and Fernandes V.

 

NPOA-IUU and their roles by Francisco Blaha

I have been dealing with National Plans of Action to Prevent, Deter and Eliminate Illegal, Unreported and Unregulated Fishing (NPOA-IUU) for a while now… 

let me see that plan

let me see that plan

I started in 2003 and 2004 when I participated while I was still working with industry in the consultations for New Zealand’s NPOA-IUU, one of the first ones prepared worldwide. During 2009/10, when serving as a Fishery Officer at FAO in Rome, among other tasks, he was involved in the evaluation of the operational impacts of the deposited IUU-NPOAs. During 2012-14 as part of his work for FFA’s Devfish II, I got involved in the development of various NPOA-IUU in the region as I worked across all aspects of fisheries MCS and regulatory compliance delivery, strengthening the operational aspects in EU yellow-carded countries, including capacity building in intelligence analysis, and the development of SOPs to assist with boardings, inspections and investigations. 

And even after all this, I still wonder what their real role in the operational side is… 

Let go through their “reason of being”… 

National Plans of Action to Prevent, Deter and Eliminate Illegal, Unreported and Unregulated Fishing (NPOA-IUU) are developed following the International Plan of Action to prevent, deter and eliminate IUU fishing (IPOA-IUU) adopted in 2001 by the Committee on Fisheries of the Food and Agriculture Organisation of the United Nations (FAO). 

The IPOA-IUU is a voluntary instrument and is one of four IPOAs (Seabirds, Sharks, Fishing Capacity and IUU) that fit within the framework of the FAO Code of Conduct for Responsible Fisheries, also adopted by COFI in 1995, and it describes the broadly accepted principles and measures to prevent and counter IUU fishing at the level of states, regional economic integration organisations and regional fisheries management organisations (RFMOs).

In light of the already existing measures to combat IUU fishing (i.e. policy, laws, institutional setup, working processes and law enforcement framework), and on the basis of principles and measures articulated in the IPOA-IUU, the objective of all NPOA-IUU is to formulate pertinent and achievable, additional measures, necessary to close gaps in the existing framework addressing IUU fishing, and to reduce in a planned and concerted manner the incidence of marine IUU fishing in a county to a minimum.

Which is all good… yet in all these years I’ve seen them gathering dust and not really being used by the frontline people… so they always fill to me as one of those things that you need to have because is expected that if you have one you a mature fishing nation… but the reality is that most of the ones I’ve seen are way too “wordy” and overcommit.

My experience is that no one really reads a report that is more than 30 pages or has the capacity to implement more than 15 recommendations in the short term.

And from my industry days, I’m very aware that: “there is only one thing worst than not having a piece of paper and is having one that you don't comply with”… so if you go overboard because is what is expected to be done… you are putting yourself to fail

NPOA-IUU have a long history in the Pacific, yet their presence has not always been noticeable. In 2005 the late Colin Brown (a good man gone to early) authored the FAO document “Model plan for a Pacific Island country - National Plan of Action to Prevent, Deter and Eliminate Illegal, Unreported and Unregulated Fishing”. 

This “Model Plan” for the elaboration of an NPOA-IUU was designed to assist Pacific Island States to give effect to the IPOA-IUU. The model incorporated the essential aspects and features of the IPOA-IUU, demonstrating how an NPOA-IUU might be drafted.

In seeking to address IUU fishing the model provides an introduction (with an important focus on the fisheries situation in the model country) followed by measures that might be adopted under the headings of all State responsibilities at the time (Flag, Coastal and State) as well as internationally agreed market-related measures, research, regional fisheries management organizations and the special requirements of developing countries. Many FFA members date their NPOA-IUU back to that document.

Then in between 2012 to 2014 and as a consequence of the EU Yellow Cards, FFA’s DevFISH II programme supported the update and redevelopment of many of these early NPOA-IUU, as to be able to facilitate FFA members to respond when questioned by the EU. 

Yet, while the earlier versions lacked depth in coverage of key MCS issues and capacities we have today, the newer versions are voluminous (i.e. 60 pages 38 action points for example), user-unfriendly and very complex, which turned off the target user groups from using it regularly. As a consequence, the documents stayed unused by officers in the compliance section, whom in principle should be using it as a working reference document.

These problems were exemplified in the words of a good friend and fisheries officer, saying that their NPOA-IUU seems to have been designed “more to be read by other countries, than to be used by us”.  

So as part of my work with MIMRA in RMI, I have re-structured their “old” NPOA-IUU, as to produce a more user-friendly document adapted to the needs and capacities of the operational users while incorporating the most updated information on the prevalence and extent of IUU in the region and our high level of collaboration with FFA, plus our cooperation with SPC, PNA, WCPFC market states and industry organisations.

So our new one has 30 pages and 15 action points while maintaining full compliance with the internationally accepted minimal components and format of FAO’s IPOA-IUU.

I personally live up to maxim that “the perfect should not get on the way of the good” and is better to start with 15 that you know you can achieve and not 38 that you can’t… once we get this 15 done, let’s bring the next 15. 

That more modest approach helped us with PSM… so let me tell you in a couple of years how with did with this one!!!

Another Vanuatu flagged longliner on a US Customs detention order for forced labor by Francisco Blaha

09279.jpg

Not long ago a I wrote about the US Custom and Border Protection Agency (CBP) withhold release order against tuna and tuna products from the Tunago No. 61 based on information obtained by CBP indicating tuna is harvested with the use of forced labour, including physical violence, debt bondage, withholding of wages, and abusive living and working conditions.

From the 18 august a 2nd Vanuatu flagged vessel, the “Da Wang” has now also been added… so far Vanuatu is the only flag state that is in that list. 

Thankfully none of the vessels is in the FFA list of good standing, yet they still in the WCPFO registry

While the vessels are Taiwan owned and operated, the factual reality is that what happens on those vessels competes to the flag state authority… the capacities of Vanuatu or their development status, are no excuse when it comes to flag state responsibility.

As I was told in the navy and the fishing boats many times… if you cannot live up to a responsibility don’t take it...

Vanuatu had already one of the 1st EU yellow cards, which was based substantially on the failures as a flag state (see the decision- last country).

One thing to keep clear is that Vanuatu is not a small player in fishing… it runs an open registry (with over an estimated -no one really knows exactly- of 100 vessels among fishing vessels and carriers). Furthermore, they are a contracting Member of IATTC, WCPFC, IOTC, ICCAT and cooperating non-Contracting Party to CCAMLR… hence their fleets is all over the world. Yet the last commercial landing in Port Vila was in 2014 and maybe a couple of pretending ones since then… but the vessels don come there… many of them use Suva as their port.

I helped with the removal of the Yellow card… yet I’m not sure how come they got away, to be honest… I remember they had a very smooth ambassador to the EU that obviously was doing a good job there… they got lots of money to develop their competent authority to gain EU market access… yet they never did much with that. They got to host an EU workshop on the impact t of ecolabels… even if they don't qualify to access to the EU. they signed PSMA, but haven done anything about it… and “hosted” a workshop wjhere nobody came after the 2nd day… and the list goes on

In any case, the EU was supposed to go back to visit them, on the back of the reissue of the yellow card they reissued to Panama… a country that shares many flag state (i)responsibilities issues with them.

While this issue relates to crew… something I feel very strongly about and I’m working on… I find it sadly ironic because Vanuatu very stringent on immigration when you arrive by plane and come to work for a couple of weeks at the request of their own goiverment and they charge over 300USD for a visa and ask you for a lot of papers…. Somehow you can go and work on a Vanuatu flag fishing boat without any paperwork or being accounted (or unaccounted) for…

As a member of FFA, they should be incorporating labour issues as part of their licensing procedures as explained here

In any case… they are also a key player in the of the biggest fisheries headaches we have in the region… transhipments at sea.

While the WCPF Convention expressly prohibits transhipment at sea (on the high seas and in a WCPFC Member’s territorial sea and exclusive economic zone) by purse seine. For longliners and other vessels, however, the WCPF Convention only requires CCMs to “encourage their vessels, to the extent practicable, to conduct transhipment in port”. Furthermore, through a binding conservation and management measure (CMM 2009-06 the WCPFC prohibits longliners and other vessels from transhipping on the high seas except where CCM has determined that “it is impracticable for certain vessels . . . to operate without being able to tranship on the high seas.” 

CMM 2009–06 requires WCPFC Members to make vessel-specific determinations as to impracticability and submit a plan detailing the steps being taken to encourage transhipment in port.  And that is not happening…. In fact, over the last two years, just 3 CCMs—China, Chinese Taipei, and Vanuatu—accounted for 84% and 89% of those transhipments in 2015 and 2016, respectively and we are talking over 100 transhipments a year… I wrote about all this before. 

Anyway if we get hold on the transhipments situation, many collateral benefits associated with port transhipment come into game:

  • Under and Misreporting: FFA’s IUU quantification report identified “Unreported” as the main IUU issue in the region, having transhipment in port, under similar conditions of that PPS and with the use of scales will be a massive step towards compliance 

  • Observer Coverage: having LL coming to port is key to increase the agreed percentages of Observer Coverage

  • Electronic Monitoring: the main limitation for the HS vessels are maintenance of the equipment and the delivery of the footage ((hard drive based) to the national observer. Using carriers provides big delays and compromises the CoC for the hardware

  • Labour issues: these could be dealt in much more depth trough having the vessels coming to port

  • Safety: transhipment at the port are fasted and safer than at seas as a port are more protected to whether and swell

  • MARPOL: longliners coming top port can easily comply with their MARPOL obligations

So yeah… this is bad news for all of us in the region… and I wish there was something that could be done with Vanuatu ton rail them into better flag state performance and changing their stand on High seas transhipment…

 

The future of food from the sea by Francisco Blaha

There is an ambitious title for a paper!

One that will require quite a lot of credible authors to pull it off unscathed, particularly when is in the Nature journal. yet when you read many well-known names in the impressive list of 22 authors spanning the globe, you know that is the kind of effort needed to live up to the challenge of the title. Particularly when the results challenge the narrative that is all doom and as we still get bombarded with, they will not be fish in 2048!

the present of food of the sea

the present of food of the sea

I’m way to low in the trophic and brain capacity scale as to have a valid opinion on the accuracy of the conclusions, but I liked what I read and how they angled the premises of the paper.

I just quote parts of it, yet my usual recommendation is to read the original.

The abstract sets the paper in motion:

Abstract

Global food demand is rising, and serious questions remain about whether supply can increase sustainably1. Land-based expansion is possible but may exacerbate climate change and biodiversity loss, and compromise the delivery of other ecosystem services. As food from the sea represents only 17% of the current production of edible meat, we ask how much food we can expect the ocean to sustainably produce by 2050. Here we examine the main food-producing sectors in the ocean—wild fisheries, finfish mariculture and bivalve mariculture—to estimate ‘sustainable supply curves’ that account for ecological, economic, regulatory and technological constraints. We overlay these supply curves with demand scenarios to estimate future seafood production. We find that under our estimated demand shifts and supply scenarios (which account for policy reform and technology improvements), edible food from the sea could increase by 21–44 million tonnes by 2050, a 36–74% increase compared to current yields. This represents 12–25% of the estimated increase in all meat needed to feed 9.8 billion people by 2050. Increases in all three sectors are likely but are most pronounced for mariculture. Whether these production potentials are realized sustainably will depend on factors such as policy reforms, technological innovation and the extent of future shifts in demand.

The main part describes well the challenges and the approach 

Main

Human population growth, rising incomes and preference shifts will considerably increase global demand for nutritious food in the coming decades. Malnutrition and hunger still plague many countries and projections of population and income by 2050 suggest a future need for more than 500 megatonnes (Mt) of meat per year for human consumption. Scaling up the production of land-derived food crops is challenging, because of declining yield rates and competition for scarce land and water resources. Land-derived seafood (freshwater aquaculture and inland capture fisheries; we use seafood to denote any aquatic food resource, and food from the sea for marine resources specifically) has an important role in food security and global supply, but its expansion is also constrained. Similar to other land-based production, the expansion of land-based aquaculture has resulted in substantial environmental externalities that affect water, soil, biodiversity and climate, and which compromise the ability of the environment to produce food.

Despite the importance of terrestrial aquaculture in seafood production (Supplementary Fig. 3), many countries—notably China, the largest inland-aquaculture producer—have restricted the use of land and public waters for this purpose, which constrains expansion Although inland capture fisheries are important for food security, their contribution to total global seafood production is limited (Supplementary Table 1) and expansion is hampered by ecosystem constraints. Thus, to meet future needs (and recognizing that land-based sources of fish and other foods are also part of the solution), we ask whether the sustainable production of food from the sea has an important role in future supply.

Food from the sea is produced from wild fisheries and species farmed in the ocean (mariculture), and currently accounts for 17% of the global production of edible meat (Supplementary Information section 1.1, Supplementary Tables 13). In addition to protein, food from the sea contains bioavailable micronutrients and essential fatty acids that are not easily found in land-based foods, and is thus uniquely poised to contribute to global food and nutrition security.

Widely publicized reports about climate change, overfishing, pollution and unsustainable mariculture give the impression that sustainably increasing the supply of food from the sea is impossible. On the other hand, unsustainable practices, regulatory barriers, perverse incentives and other constraints may be limiting seafood production, and shifts in policies and practices could support both food provisioning and conservation goals.

In this study, we investigate the potential of expanding the economically and environmentally sustainable production of food from the sea for meeting global food demand in 2050. We do so by estimating the extent to which food from the sea could plausibly increase under a range of scenarios, including demand scenarios under which land-based fish act as market substitutes.

The future contribution of food from the sea to global food supply will depend on a range of ecological, economic, policy and technological factors. Estimates based solely on ecological capacity are useful, but do not capture the responses of producers to incentives and do not account for changes in demand, input costs or technology.

To account for these realities, we construct global supply curves of food from the sea that explicitly account for economic feasibility and feed constraints. We first derive the conceptual pathways through which food could be increased in wild fisheries and in mariculture sectors. We then empirically derive the magnitudes of these pathways to estimate the sustainable supply of food from each seafood sector at any given price21. Finally, we match these supply curves with future demand scenarios to estimate the likely future production of sustainable seafood at the global level.

I particularly like the four pathways they see as to sustainably increase food from the sea: 

  1. improving the management of wild fisheries;

  2. implementing policy reforms of mariculture;

  3. advancing feed technologies for fed mariculture; and

  4. shifting demand, which affects the quantity supplied from all three production sectors.

The analysis from these bases is quite deep and interesting, I recommend you follow it, otherwise here are the conclusions 

Conclusions

Global food demand is rising, and expanding land-based production is fraught with environmental and health concerns. Because seafood is nutritionally diverse and avoids or lessens many of the environmental burdens of terrestrial food production, it is uniquely positioned to contribute to both food provision and future global food and nutrition security. Our estimated sustainable supply curves of food from the sea suggest substantial possibilities for future expansion in both wild fisheries and mariculture.

The potential for increased global production from wild fisheries hinges on maintaining fish populations near their most-productive levels. For underutilized stocks, this will require expanding existing markets. For overfished stocks, this will require adopting or improving management practices that prevent overfishing and allow depleted stocks to rebuild.

Effective management practices commonly involve setting and enforcing science-based limits on catch or fishing effort, but appropriate interventions will depend on the biological, socioeconomic, cultural and governance contexts of individual fisheries.

Effective management will be further challenged by climate change, species composition changes in marine ecosystems and illegal fishing. Directing resources away from subsidies that enhance fishing capacity towards building institutional and technical capacity for fisheries research, management and enforcement will help to meet these challenges.

Increased mariculture production will require management practices and policies that allow for environmentally sustainable expansion, while balancing the associated trade-offs to the greatest extent possible; this principle underpins the entire analysis. We find that substantial expansion is realistic, given the costs of production and the likely future increase in demand.

We have identified a variety of ways that sustainable supply curves can shift outward. These shifts interact with future demand to determine the plausible future equilibrium quantity of food produced from the sea. We find that although supply could increase to more than six times the current level (primarily via expanded mariculture), the demand shift required to engage this level of supply is unlikely. Under more realistic demand scenarios and appropriate reforms of the supply, we find that food from the sea could increase in all three sectors (wild fisheries, finfish mariculture and bivalve mariculture) to a total of 80–103 Mt of food in 2050 versus 59 Mt at present (in live-weight equivalents, 159–227 Mt compared to 102 Mt at present).

When combined with projected inland production, this represents an 18–44% per decade increase in live-weight production, which is somewhat higher than the 14% increase that the Organisation for Economic Co-operation and Development (OECD) and the FAO project for total fish production during the next decade.

Under some scenarios, future production could represent a disproportionate fraction of the estimated total increase in global food production that will be required to feed 9.8 billion people by 2050. Substantial growth in mariculture will rely partly on public perceptions. Although there is some evidence of a negative public perception of aquaculture, it is highly variable by region and by context, and certifications and the provision of other information can help to alleviate concerns and expand demand.

These global projections will not have uniform implications around the world. For example, improved policies that shift the supply curve outward will decrease prices, but income-induced demand shifts will increase prices. Both effects increase production but have vastly different consequences for low-income consumers.

Bivalves may contribute substantially to food security by providing relatively low-cost and thus accessible food, because they have a high production potential at low costs compared to finfish production (Fig. 3). If all seafood is perfectly substitutable, bivalves could contribute 43% and 34% of future aquatic food under future and extreme demand scenarios, respectively (Supplementary Fig. 3)—which suggests potential large increases in production, provided demand is high enough.

Trade also has an important role in distributing seafood from high-production to low-production regions, and in overcoming regional mismatches in price. The rate of international trade of seafood products has increased over past decades, and 27% of seafood products were traded in 2016, although major economic disruptions—such as the COVID-19 pandemic—can jointly reduce both supply and demand of traded seafood. On the other hand, trade may become increasingly relied upon as climate change alters regional productivity.

Substantially expanding the production of food from the sea will bring co-benefits and trade-offs, and will require national and interregional governance, as well as local capacity to ensure equity and sustainability.

The improved management of wild fisheries can not only increase fish biomass, but also brings the co-benefit of improved livelihoods of fishers. However, there will be some short-term costs as overfished stocks rebuild to levels that support greater food provision.

As mariculture expands, interactions with wild fisheries and other ecosystem services (via spatial overlaps, pollution and so on) must be constantly addressed. Ambitious technical innovation (that is, the substitution of marine ingredients with terrestrial-sourced proteins) can help to decouple fed mariculture from wild fisheries, but will probably refocus some pressure on terrestrial ecosystems.

Climate change will further challenge food security. Estimates suggest that active adaptation to climate-induced changes will be crucial in both wild fisheries and mariculture. Climate-adaptive management of wild fisheries and decisions regarding mariculture production (for example, the type of feed used, species produced and farm sitting) could improve food provision from the sea under conditions of climate change.

We have shown that the sea can be a much larger contributor to sustainable food production than is currently the case, and that this comes about by implementing a range of plausible and actionable mechanisms.

  • The price mechanism—when it motivates improved fishery management and the sustainable expansion of mariculture into new areas—arises from change in demand, and acts on its own without any explicit intervention.

  • The feed technology mechanism is driven by incentives to innovate, and thus acquire intellectual property rights to new technologies. When intellectual property is not ensured, or to achieve other social goals, there may be a role for public subsidies or other investments in these technologies.

  • The policy mechanism pervades all three production sectors, and could make—or break—the ability of food from the sea to sustainably, equitably and efficiently expand in the future.

 

 

 

Responding to: Why I don't I don't subscribe to paid content by Francisco Blaha

I get a lot of questions via mail and social media, that in most cases I’m always happy to respond. One that I get from people working in paywalled media (who wants to use my content of photos) is why I’m against subscriptions to paid content… my standard response is below:

Always looking for fish or information :-)

Always looking for fish or information :-)

I totally understand you run a business and your livelihood depends on this... but you see, 30 years ago I was working on fishing boat earning 300USD a month. I manage to gain qualifications and progress in life thanks to studying and to many people that I knew but even more people I didn't, that provided me information, books (that's you FAO!), and training materials for free.

I started my blog as a sideline in my website (the blog option was part of the minimal package) so I started writing it for free and i always love making pictures of what is ee on board (and also said many times: no thanks to offers of paid sponsorship), mostly as a way to partly pay back all that free info and advice I was given... 

I work at the present with many fishers and fisheries officers in the pacific that earn less per month than the value of most paywalled fisheries news sites...

So I adhere to the principle that fisheries information should be free, otherwise the gap in between those that can access and those that by no fault of their own cannot pay for it will keep growing... and with that, we will see sustainability fall even further, since only the rich can afford to be informed and care, while the less fortunate, keep having their choices and options further and further eroded.

I'm totally aware that it is a total ideological stand, as the gap is too wide already for a one-man band like myself to make a difference, yet I’m a man of principles... so I don't subscribe to paid content.

Said so, I really appreciate your interest in my personal rumblings in the blog, and as long as I'm acknowledged as the source of pictures and contents I'm honoured for you to be using them... just let me know when you do as a matter of courtesy, that is all.

Yours in legal and safe fishing,
--
Francisco Blaha

While we worry about IUU, the real big issue keep coming in. by Francisco Blaha

is not them the real problem… is us

is not them the real problem… is us

And when you read: the combined catch of both tuna species is projected to decrease by ~10–40% by 2050 in the exclusive economic zones of Federated States of Micronesia, Marshall Islands, Nauru, Palau, Papua New Guinea, Solomon Islands, Tokelau and Tuvalu… is hard to swallow... I work with friends in all those countries

That is enough to disbalance the weekend, and made me question my self on what I’m doing?

Is already hard to deal with the IUU issues that are my work, yet they are quite minimal in terms of political clout in comparison… so the reversion of the drivers of climate change ain’t going to change anytime soon.

The demise of commercial tuna fisheries in the WCPO is not on the greedy and terrible fisherman as the usual narrative goes on or the lack of effort of the Pacific Island countries. Is on the worldwide medium and above social class almost insatiable hunger for more energy, cars, goods etc… while the cost of their greed is paid by those that don’t have those goods and facilities. 

So yeah… have a read on the paper and let’s look deep into ourselves… because this one is on us.

I just quote there the box for the pacific…

Across the 22 Pacific Island countries and territories (PICTs), models predict an eastern redistribution in the biomass of skipjack and yellowfin tuna — the two main exported fish species — by 2050). Under Representative Concentration Pathway (RCP) 8.5, for example, the combined catch of both tuna species is projected to decrease by ~10–40% by 2050 in the exclusive economic zones of Federated States of Micronesia, Marshall Islands, Nauru, Palau, Papua New Guinea, Solomon Islands, Tokelau and Tuvalu However, given the eastern redistribution, tuna catch is anticipated to increase in the exclusive economic zones of Kiribati and Cook Islands by 15–20% 

As several PICTs are tuna-dependent economies, the impact of climate change on tuna fisheries increases the vulnerability of these small island developing states. For instance, shifts in tuna distribution, and resulting increases in catches from international waters, are expected to cause proportional changes in government revenue received by small island developing states from fishing licence fees. These changes need to be considered by the Western and Central Pacific Fisheries Commission when governing the sustainable use of the region’s tuna resources, developing harvest strategies and allocating fishing rights to minimize the implications of tuna redistribution for island economies.

The projected 20–50% decrease in productivity of coral reef fish in the Pacific Islands region by 2050 under RCP8.5 is expected to influence the contributions of small-scale fisheries to food security in most PICTs However, rapid population growth in several PICTs is expected to have a greater influence than declining reef fish production on future availability of fish per capita. The rich tuna resources of the Pacific Islands region can be used to fill the widening gap between the total amount of fish that can be harvested sustainably from coral reefs and other coastal habitats, and that required for good nutrition.