Regulation (EU) No 1380/2013 of the European Parliament and of the Council1 requires that conservation measures be adopted taking into account available scientific, technical and economic advice, including, where relevant, reports drawn up by the Scientific, Technical and Economic Committee for Fisheries and other advisory bodies, as well as in the light of any advice received from Advisory Councils established for the relevant geographical areas or fields of competence and joint recommendations made by Member States.

It is incumbent upon the Council to adopt measures on the fixing and allocation of fishing opportunities, including certain conditions functionally linked thereto, as appropriate. Fishing opportunities should be allocated to Member States in such a way as to ensure the relative stability of fishing activities of each Member State for each stock or fishery and having due regard to the objectives of the Common Fisheries Policy (CFP) set out in Regulation (EU) No 1380/2013.

Regulation (EU) No 1380/2013 provides that the objective of the CFP is to achieve the maximum sustainable yield (MSY) exploitation rate by 2015 where possible and, on a progressive, incremental basis, at the latest by 2020 for all stocks.

The total allowable catches (TACs) should therefore be established, in accordance with Regulation (EU) No 1380/2013, on the basis of the available scientific advice, taking into account biological and socioeconomic aspects whilst ensuring fair treatment between fishing sectors, as well as having regard to the opinions expressed during the consultation with stakeholders.

Regulation (EU) 2016/1139 of the European Parliament and of the Council2 establishes a multiannual plan for the stocks of cod, herring and sprat in the Baltic Sea and for the fisheries exploiting those stocks (‘the plan’). The plan aims to ensure that exploitation of living marine biological resources restores and maintains populations of harvested species above levels which can produce the MSY. To that end, the target fishing mortality for the stocks concerned, expressed in ranges, is to be achieved as soon as possible and, on a progressive, incremental basis, by 2020. It is appropriate that the catch limits applicable in 2019 for the cod, herring and sprat stocks in the Baltic Sea are established in line with the objectives of the plan.

The International Council for the Exploration of the Sea (ICES) has indicated the biomass of Western Baltic herring in ICES subdivisions 20-24 to be below the conservation reference points of the spawning stock biomass as set out in Annex II, column A, to Regulation (EU) 2016/1139. In accordance with Article 5(2) of that Regulation, all appropriate remedial measures should be adopted to ensure a rapid return of the stock concerned to a level capable of producing MSY. To that end, it is necessary to take into account the timeline for the achievement of the objectives of the CFP in general and of the plan in particular in view of the expected effect of the remedial measures adopted, whilst at the same time adhering to the objectives of achieving economic, social and employment benefits as set out in Article 2 of Regulation (EU) No 1380/2013. Accordingly, and in line with Article 4(3) of Regulation (EU) 2016/1139, it is appropriate that fishing opportunities for Western Baltic herring are set below the fishing mortality range in Annex I, column A, of that Regulation, as such a level takes into account the decrease in the biomass.

As regards the Western Baltic Sea cod stock, scientific advice indicates that recreational fisheries contribute significantly to the overall fishing mortality of that stock and should be limited. It is therefore appropriate to set a daily bag limit per fisherman. This is without prejudice to the principle of relative stability applicable to commercial fishing activities.

As regards the Eastern Baltic cod stock, ICES has not yet been able to establish biological reference points, following changes in the biology of the stock. It is therefore appropriate, in order to contribute to the achievement of the objectives of the plan, to fix the TAC for Eastern Baltic cod in accordance with the precautionary approach as established in Regulation (EU) No 1380/2013 and to set a closure period.

In order to guarantee full use of coastal fishing opportunities, it is appropriate to introduce a limited inter-area flexibility for salmon from ICES subdivisions 22-31 to ICES subdivision 32 for the Member State that has requested that flexibility.

According to ICES advice, 29 % of catches in the salmon fishery is misreported, in particular as sea trout catches. As most of the sea trout in the Baltic Sea is exploited in coastal areas, it is appropriate to prohibit fishing for sea trout beyond four nautical miles and to limit by-catches of sea trout to 3 % of the combined catch of sea trout and salmon in order to contribute to preventing misreporting of salmon catches as sea trout catches.

The use of the fishing opportunities set out in this Regulation is subject to Council Regulation (EC) No 1224/20093, and in particular to Articles 33 and 34 thereof concerning the recording of catches and fishing effort, and to the transmission of data on the exhaustion of fishing opportunities to the Commission. This Regulation should therefore specify the codes relating to landings of stocks subject to this Regulation that are to be used by Member States when sending data to the Commission.

Council Regulation (EC) No 847/964 introduced additional conditions for year-to-year management of TACs including, under Articles 3 and 4, flexibility provisions for precautionary and analytical TACs. Under Article 2 of that Regulation, when fixing the TACs, the Council is to decide to which stocks Articles 3 or 4 shall not apply, in particular on the basis of the biological status of the stocks. More recently, the year-to-year flexibility mechanism was introduced by Article 15(9) of Regulation (EU) No 1380/2013 for all stocks that are subject to the landing obligation. Therefore, in order to avoid excessive flexibility that would undermine the principle of rational and responsible exploitation of living marine biological resources, hinder the achievement of the objectives of the CFP and cause the biological status of the stocks to deteriorate, it should be established that Articles 3 and 4 of Regulation (EC) No 847/96 apply to analytical TACs only where the year-to-year flexibility provided for in Article 15(9) of Regulation (EU) No 1380/2013 is not used.

Based on new scientific advice, a preliminary TAC for Norway pout in ICES division 3a and Union waters of ICES division 2a and ICES subarea 4 should be established for the period from 1 November 2018 to 31 October 2019.

In previous years the TACs for anchovy in ICES subareas 9 and 10 and Union waters of CECAF division 34.1.1 have been fixed for a calendar year. In July 2018 ICES issued its advice for the period from 1 July 2018 to 30 June 2019 for that stock. Those periods should be aligned in order to match the TAC period with the period covered by the ICES advice. Exceptionally and only due to the transition, the TAC for anchovy should be amended to cover the period of 18 months, ending on 30 June 2019.

In order to avoid the interruption of fishing activities and to ensure the livelihoods of Union fishermen, this Regulation should apply from 1 January 2019. However, this Regulation should apply to anchovy in ICES subareas 9 and 10 and Union waters of CECAF division 34.1.1 from 1 January 2018. Such retroactive application is without prejudice to the principles of legal certainty and protection of legitimate expectations as the fishing opportunities for that longer period exceed those initially fixed under Council Regulation (EU) 2018/1205. Furthermore, this Regulation should apply to Norway pout in ICES division 3a and Union waters of ICES division 2a and ICES subarea 4 from 1 November 2018 until 31 October 2019. For reasons of urgency, this Regulation should enter into force immediately after its publication,