The landings obligation in view of different management regimes

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The landings obligation in view of different management regimes Hans Frost and Ayoe Hoff Department of Food and Resource Economics

21/07/2016 2 What? Using a simple two-fleet two-species bio-economic model (ToyFish) to illustrate relative economic trade-offs of introducing the landings obligation in fisheries managed with ITQs. (i) Why? The results of this simple generic model will point : towards possible trends in economic outcomes of fisheries under the landings obligation and (ii) detail the understanding of the results of more complex case specific models.

21/07/2016 3 Context: Dicardless Discardless (Horizon 2020 grant agreement No. 633680) has the aims: To develop practical, achievable, acceptable and cost-effective Discard Mitigation Strategies (DMS). To integrate knowledge, tools and technologies at local, national, EU and international level to provide and promote the solutions needed to implement DMS through the seafood supply chain. To assess the effects of discard reduction policies on the ecosystem, economic and social sustainability. To provide feedback on improved fisheries management.

21/07/2016 4 Discardless WP2: Fishery Scale Assessment Provide best estimates of likely economic and social effects of implementatioin of the landings obligation af the fishery scale (individual and fleet). 2.1 Fundation: Summarising available socioeconomic data and knowledge on discard, and identification of knowledge gaps. 2.2 Evaluation basis: Developing standard economic and social criteria for contrasting socioeconomic effects of DMSs. 2.3 Setting the scene: Model selection and setup based on DMS scenarios defined throughout the project. 2.4 Evaluating: Estimating and contrasting socioeconomic effects of DMSs. 2.5 Monitoring: Real time mapping of economic and social factors before, under and after implementation of the landings obligation for selected fleets.

21/07/2016 5 1. Fishing effort (costs) o o Fleet segments Areas 2. Fish stocks o Species interaction o Age composition 3. Restrictions Gear measures Capacity Closed periods TAC/quotas Closed areas 4. Total catch o Target species 2.1 Fundation: Summarising available socioeconomic data and knowledge on o Non-target (size, species) discard, and identification of knowledge gaps. 10. Land Price 11. Profit (gross revenue costs) Decision variable to maximize

21/07/2016 6 Long term effecs of the LO in the Danish fishery Results obtained using the bioeconomic NJORD model covering the total Danish fishery (35 fleet segments) and 20 species. ST: Short Term effects of the LO before effort and capacity have adjusted to new levels (~fixed quota shares). MLT: Medium Long Term effects of the LO after effort and capacity have adjused to new levels (~ITQ), but stocks are unchanged.

21/07/2016 7 ToyFish TTTTTTTTTT PPPPPPPPPPPP = FFllllllll sseeeeeeeeeeeeee (RR TTTT +RR TTUU + RR BBBB ) (cc DD + ff) VV R TO =Revenue of target species above minimum size R TU =Revenue of (landed) target species below minimum size R BC =Revenue of (landed) bycatch species c = Variable costs per days at sea f = Fixed costs D =Days at sea per vessel V = Number of vessels ST: - Harvest of target above min size given by CD function. - Harvest of unwanted fish proportional to harvest of target. - Quota limitations, set by estimations of stock growth and discards.

21/07/2016 8 ToyFish setup Fleet 1 ( trawl ) Fleet 2 ( gillnet ) Variable costs (1000 /day at sea) 1.38 0.80 Fixed costs (1000 /vessel) 120 70 Initial number of vessels 20 40 Maximum number of days per vessel per year 250 180 Price of species 1 ( cod ) above minimum size ( /kg) 2 3 Price of species 2 ( plaice ) above minimum size ( /kg) 1.5 2 Price of species 1 ( cod ) below minimum size ( /kg) 0.2 0.2 Price of species 2 ( plaice ) below minimum size ( /kg) 0.2 0.2 Initial biomass Initial Growth a b Species 1 8000 4800 1 0.00005 Species 2 4000 2720 1 0.00008

21/07/2016 9 Scenarios: From race to fish to long term ITQ without and with LO Before LO After LO Scenario Description Time Frame ST1 Short Term MLT1 No Landings obligation (LO) Medium long term LT1 Long term ST2 Short Term LO: No cost of landing MLT2 Medium long term unwanted catch LT2 Long term ST3 Short Term LO: Cost of landing unwanted MLT3 Medium long term catch = price of unwanted catch LT3 Long term ST4 Short Term LO: High price of landing MLT4 Medium long term unwanted catch LT4 Long term Short term (ST): Fixed quota shares. TACs=natural growth less expected discards. Medium Long Term (MLT): ITQ, seadays and number of vessels adjusted to optimal level (maximum total profit). Stocks and quotas equal to ST case. Long term (LT): ITQ, seadays, number of vessels and stocks adjusted to optimal levels Quotas adjusted accordingly.

21/07/2016 10 Results: Profitability Introduction of the LO may increase overall profitability given reduction in effort related costs. Introduction of ITQs, as expected, has larger effect on the total profit of the fishery than introduction of the LO. For the individual vessels the profitability is not changed significantly by introduction of the LO. However, this at the expense of reduction in number of vessels.

21/07/2016 11 Results: quota utilisation Species 2 chokes when quotas are shared (ST) reduced effort when LO is introduced. Under MLT (ITQ), before the stocks have adjusted, none of the species are fully utilised reduced effect of LO. Under LT (ITQ), quotas are fully utilised. But since the fishery will adjusted to the cost structure through adjustment of capacity (number of vessels), the effect of the LO on overal and individual profitability is still low.

21/07/2016 12 Danish quota utilisations 2012-2014 Denmark has had ITQ management in place since 2007. Today few Danish quotas are fully utilised. Species 2012 2013 2014 Blue whiting 31 % 64 % 89 % Sprat 53 % 47 % 97 % Monkfish 73 % 70 % 79 % Horse mackerel 31 % 48 % 33 % Whiting 22 % 14 % 20 % Norway lobster 51 % 48 % 58 % Haddock 89 % 77 % 92 % Hake 47 % 50 % 33 % Ling 55 % 64 % 48 % Mackerel 97 % 101 % 84 % Saithe 96 % 97 % 91 % Plaice 83 % 75 % 65 % Herring 95 % 91 % 98 % Norway pout 33 % 21 % 25 % Sand eel 105 % 95 % 93 % Cod 83 % 62 % 68 % Sole 62 % 61 % 85 %

21/07/2016 13 The Danish results revisited The long run effects of the introduction of the LO in the Danish fishery may be less severe than may be expected. Underutilised quotas makes room for increase in catches and thus earnings, that may counteract additional costs of application of the LO. This however at the expense of reduction in fleet size.

21/07/2016 14 Summary In a fishery managed with ITQs possible negative economic effects of the landings obligation may be counteracted by unutilised quotas and thus increase in/reallocation of catches. Individual vessels operating optimally may not experience any loss given the LO, depending on the price less costs of landing unwanted species. Extra costs incurred by landing of unwanted species will be reflected in deceased capacity (number of vessels) rather than in significant loss of overall profitability.

Thank you 21/07/2016 15