The stock’s total biomass has also increased, even though not concomitantly with the SSB ( Fig. 2b). In addition to possible climate effects, this recent increase Target Selective Inhibitor Library screening in SSB could have at least two explanations: First, illegal fishing has been reduced from the maximum of 166,000 t in 2005 to approximately zero in 2009 [4]. This decline is most likely due to the introduction of port control in 2007, requiring all vessels to document that their landings are legally caught. Second, a joint Norwegian–Russian harvest control rule (HCR) that determines the total allowable catch (TAC) has been implemented since 2004,

to ensure that the stock is not at “risk of being harvested unsustainably” or “suffering reduced reproductive capacity” [5] and [6]. NEA cod is an economically very important fish resource [7] and [8] mostly situated in the exclusive economic zones of Norway and Russia (Fig. 1). For years, NEA cod has been managed jointly by those two countries, though not without scientific and political disagreements [9]. To enable more farsighted management and Cisplatin solubility dmso to simplify

the annual negotiations on harvest levels, an HCR was agreed upon by the two countries in 2004 (Fig. 2c). In general, an HCR is an algorithm and a tactical management tool that translates biological information, such as a stock’s current SSB, into management information such as a TAC for that stock during the next fishing season. An HCR is often designed with the help of reference points for target biomass and fishing mortality. In particular, the precautionary

reference points for biomass and fishing mortality, Bpa and Fpa, respectively, act as buffers to account for natural variability and uncertainty in the stock assessment: Bpa implements a “safety margin” to reduce the risk that the true SSB falls below a limit reference point Blim below which the stock is expected to suffer from reduced reproductive capacity. Likewise, Fpa is meant to avoid a true fishing mortality that exceeds the limit reference point Flim above which SSB is expected Cell Penetrating Peptide to drop below Blim [5]. The range of these buffers depends on the level of uncertainty and on the level of risk fisheries managers are willing to accept on behalf of society. In autumn 2004, the 33rd session of the Joint Norwegian–Russian Fishery Commission adopted a HCR stipulating that the fishing mortality is allowed to be at Fpa as long as SSB exceeds Bpa, but is required linearly to decrease from Fpa to 0 as SSB decreases from Bpa to 0 ( Fig. 2c). Therefore, fishing can take place at all SSB levels [10]. The HCR contains additional elements that aim to restrict how much the TAC can change from one year to the next. However, the TAC advised by the adopted HCR is not always followed.