STUBBORN FUEL TAX CONCESSIONS THE CASE OF FISHERIES IN NORWAY

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STUBBORN FUEL TAX CONCESSIONS THE CASE OF FISHERIES IN NORWAY John R. Isaksen, Nofima, Tromsø Øystein Hermansen, Nofima, Tromsø Ola Flaaten, NCFS, University of Tromsø ola.flaaten@uit.no

Outline of presentation Introduction Norwegian fisheries subsidies development The fuel tax reimbursement scheme What is a subsidy? Why is it harmful in fisheries? Background Environmental taxes and excemptions Research questions: - The fleet s benefits from the subsidies (profitability) Sensitivity analysis - Subsidy removal effects Summing up some findings and recommendations

What s a (fishery) subsidy? WTO: (i) financial contributions (ii) by a government or public body (iii) that confer a benefit, all three conditions must be met Governmental financial transfers to the fishery sector are not necessarily subsidies, nor necessarily harmful OECD reports Sumaila et al. (2010): Good, bad or ambiguous (ugly) subsidies Why harmful in fisheries? Incentives for increased output, endangering fish stocks and reducing potential long term profits Trade distortion through provision of advantages for one exporting country (if underdeveloped stocks) Fuel subsidies and environmental tax exemptions

Effects of subsidies in open access fisheries: increased effort reduced stock Source: Duy et al., 2014 Revenue, Costs S TC R ws R R os TR S TR E MSY E OA E S OA Effort

Energy intensive Bottom trawling may have damaged 30-50 % of Cold Water Corals in Norway (Armstrong, 2014) 2445 km 2 protected Not allowed to damage on purpose 5

mill 2012-NOK Government financial transfers to the Norwegian fishing industy, 1964-2012. Sources MFCA and SN 5,000 4,500 4,000 3,500 3,000 Nominal values Real (2012-mNOK) 2,500 2,000 1,500 1,000 500 0 1964 1966 1968 1970 1972 1974 1976 1978 1980 1982 1984 1986 1988 1990 1992 1994 1996 1998 2000 2002 2004 2006 2008 2010 2012

The fuel tax reimbursement scheme in Norway 1970: Environmental/pollution justified Norwegian mineral oil tax Basic tax, CO 2 tax and sulphur tax Manufacturing industry consumption mainly exempted 1988: Coastal water fisheries reimbursed for most of the tax (not sulphur) while distant water fishing vessels are exempted all This, due to a difficult economic situation in the fishing fleet, international competition and fear of bunkering abroad 2007: Parliament agreement on climate policy Mineral oil tax reimbursement scheme under pressure 2012: Still in effect refunding NOK 1.6 per litre But also other industries are exempted/subsidised 2013->2014: Increasing rate to pay for fishing vessels

The mineral gas oil list price and the per litre fuel tax refund, 1988 to July 2013. Sources: Statoil Fuel and Retail ASA and the Guarantee Fund for Fishermen.

Distribution of fuel tax reimbursement by vessel size, 2011 Source: The Guarantee Fund for Fishermen 253 vessels above 28 m 73 % 201 vessels 21-28 m 13 % 857 vessels 11-21 m 9 % 2 524 vessels < 11 m 5 %

Estimated exempted mineral oil and environmental taxes in the Norwegian fishing fleet, nominal value 2007 and 2011. Million NOK Tax CO 2 SO 2 NO X Total 2007 394.7 11.4 366.6 772.7 2011 627.1 13.1 358.8 999.0

Operating margin The Average operating margin (EBIT s share of turnover) in the Norwegian fishing fleet and adjusted for the CO2 tax reimbursements, 1980 2012. For 2007 and 2011 the green squares indicate the profit margins the respective years if all fuel tax exemptions were abolished. 25% 20% Adjusted for mineral oil tax reimbursement 15% 10% 5% -1%

Fuel costs's share of revenues Fuel cost in percent of revenue for some vessel groups, 2011. CS=coastal seiners, CV=coastal vessels, ST=shrimp trawlers. 25% 20% 15% 10% 5% 0%

Safety margin Fuel price increase safety margin for vessel groups with respect to fuel price (the increase allowed for break-even result), mean for 2008-2011. (Abbrevations: ST=shrimp trawl, CS=coastal seine, CV=coastal vessels) 500% 400% 300% 200% 100% 0%

Summing up (1) Globally, the marginal damage from CO 2 emissions is independent of the location of the emission source The optimal emission tax on CO 2 should be equal across countries and sectors However, CO 2 taxes vary between countries, as well as within national sectors and across fuel types The same applies to SO 2, NO x and other environmental taxes (though local damages may vary and require differentiated taxes)

Summing up (2) In the EU quota market for CO 2 emissions, the price per ton has varied - down to 6.6 per ton in 2012 at an UK auction The taxes in Norway in 2012 correspond to a rate of about USD 100 per ton CO 2 emissions, about twelve times the EU quota price In an almost Parliament-wide compromise as a measure to promote more climate friendly conduct - a proposal: phasing out the fishing industry s fuel tax exemptions First done for 2013 when the coastal fishing vessels pay the reduced rate of about one fifth of the full CO 2 rate, whereas distant water fishing is fully exempted from the CO 2 tax The Government white paper on the 2014 budget doubled this rate

Summing up (3) A survey of the fuel tax regimes in neighbouring Nordic coastal states shows that their fleets are hardly charged any taxes on fuel (Waldo et al., 2014) Undoubtedly, this scheme is an industry support that should be abolished The worst emitters in fisheries get the highest relief from it

Conclusions Emissions take place locally but affect globally The fishing fleet emits about 3 % of Norwegian CO 2 Fuel tax concessions = 1 bn NOK (about USD 170 mill) = 6.3% of landed value (2011) Fleet profitability is no longer a reimbursement argument The worst emitters get the highest relief, in particular trawl If abolished: Larger vessels will bunker un-taxed abroad/in open sea, since some other countries have fuel subsidies/tax free Shift in supply of fish towards landings abroad Smaller energy effective vessels will loose - have considerably less opportunities to avoiding the fuel taxes Little effect on GHG emissions An international agreement on environmental taxes would be preferred

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