Year | Nr. Bottom Trawl | Nr. Other | Nr. Long Line | Nr. Danish Seine | Bottom Trawl | Other | Long Line | Danish Seine | Total catch |
---|---|---|---|---|---|---|---|---|---|
2000 | 86 | 103 | 170 | 25 | 1088 | 23 | 157 | 76 | 1344 |
2001 | 76 | 129 | 139 | 25 | 929 | 66 | 114 | 64 | 1173 |
2002 | 88 | 133 | 116 | 18 | 1068 | 48 | 90 | 93 | 1299 |
2003 | 72 | 111 | 133 | 27 | 733 | 37 | 153 | 102 | 1025 |
2004 | 68 | 110 | 142 | 25 | 704 | 26 | 224 | 84 | 1038 |
2005 | 77 | 107 | 171 | 34 | 518 | 11 | 205 | 63 | 797 |
2006 | 62 | 106 | 189 | 37 | 467 | 23 | 460 | 100 | 1050 |
2007 | 66 | 86 | 216 | 43 | 767 | 26 | 394 | 71 | 1258 |
2008 | 77 | 95 | 235 | 49 | 950 | 30 | 557 | 151 | 1688 |
2009 | 77 | 221 | 244 | 60 | 1439 | 45 | 520 | 303 | 2307 |
2010 | 63 | 276 | 212 | 50 | 2192 | 42 | 425 | 191 | 2850 |
2011 | 65 | 263 | 219 | 43 | 2486 | 24 | 345 | 109 | 2964 |
2012 | 65 | 263 | 223 | 45 | 956 | 19 | 320 | 174 | 1469 |
2013 | 53 | 234 | 218 | 41 | 659 | 7 | 255 | 62 | 983 |
2014 | 52 | 174 | 208 | 32 | 643 | 7 | 207 | 73 | 930 |
2015 | 44 | 160 | 186 | 30 | 675 | 4 | 116 | 65 | 860 |
2016 | 41 | 114 | 174 | 30 | 559 | 2 | 104 | 69 | 734 |
2017 | 34 | 64 | 147 | 24 | 401 | 1 | 108 | 43 | 553 |
2018 | 38 | 37 | 115 | 21 | 688 | 1 | 61 | 67 | 817 |
2019 | 47 | 64 | 109 | 26 | 605 | 1 | 93 | 61 | 760 |
2020 | 47 | 61 | 102 | 20 | 548 | 2 | 67 | 18 | 635 |
2021 | 48 | 103 | 93 | 25 | 820 | 3 | 59 | 71 | 953 |
2022 | 48 | 101 | 78 | 26 | 631 | 3 | 67 | 72 | 773 |
2023 | 49 | 159 | 65 | 30 | 957 | 12 | 112 | 64 | 1145 |
2024 | 49 | 105 | 63 | 23 | 600 | 4 | 87 | 46 | 737 |
Key signals
Since the initiation of the spring survey in 1985, survey biomass has peaked approximately every 15 years — first in 1990, followed by a larger peak in 2005, and the highest peak in 2024.
Recruitment has followed a similar pattern, with peaks occurring one to three years before the corresponding peaks in the total biomass index.
Spawning stock biomass (SSB) has been above \(I_{trigger}\) since 2017.
Fishing pressure has been below \(F_{proxy,MSY}\) since 2017.
General information
Whiting is a demersal gadoid species like cod and haddock, but smaller with a maximum length of about 80 cm, males and females being similar in size. In Icelandic waters, sexual maturity is reached at around 30 cm.
The Fishery
Whiting has been caught mainly as bycatch all around Iceland in recent years, though mostly around south and west of Iceland (Figure 1 and Figure 2). Annual catches have been between 500 and 1000 tonnes except for 2008-2012 when catches increased with a peaked in 2011 at 2602 tonnes (Figure 2). Increased catches in this period occurred almost exclusively in the southwest (Figure 2). In 2021 and 2023, catches were slightly higher than adjacent years, or similar to 2013, but otherwise lower (Figure 2, Figure 3, Figure 4 and Figure 6). Whiting is found at depths ranging from 10 to 300 m but is mostly caught between 100 and 250 m (Figure 3).
Whiting is mainly caught in demersal trawls but to some extent in Nephrops trawls, longline and demersal seine (Table 1, Figure 4). The number of boats reporting whiting catches increased with increased catches between 2007 and 2012 but has since then decreased and were lowest in 2016 (Figure 5).
Length Distributions from commercial catches of whiting
Samples from commercial catches are mostly collected in the sout west, where whiting is most abundant (Figure 6). Length measurements from commercial catches are scarce and missing for some years, but show substantial recruitment in 1980, 1996, 2007 and 2019 (Figure 7). Most whiting caught in the commercial fishery are 38-55 cm.
Survey Data
Annual Icelandic groundfish surveys have been conducted in March (IS-SMB) since 1985 and October (IS-SMH) since 1996. Both surveys cover the distribution area of whiting on Icelandic grounds. For monitoring, harvestable biomass and recruitment indices were estimated for both surveys (Figure 8). The harvestable biomass index is calculated as the biomass of individuals 40 cm and larger. The recruitment index is defined as whiting smaller than 20 cm.
Both the total biomass index and harvestable biomass index in IS-SMB increased from 2003 to a maximum in 2005 but decreased to a low level in 2015 (Figure 8). Since then, both indices have increased, and harvestable biomass was approaching the highest value in the timeseries (1990) in 2024 but decreased substantially in the most recent year. The biomass indices from IS-SMH are much more variable but show similar trends as IS-SMB. Recruitment indices show similar trends in both surveys (Figure 8). Strong recruitment was observed in 2003, 2007 and 2019-2021 in IS-SMH and in 2004, 2008 and 2021-2022 in IS-SMB. These peaks can be observed in the length distributions (Figure 9), and in the harvestable biomass indices 2-3 years later.
Spatial distribution of whiting from the spring survey is similar to what is observed in commercial catches, that is, mostly in the south of Iceland (Figure 1, Figure 2, Figure 10 and Figure 11). The autumn survey however shows the highest indices in a larger area, southeast, southwest, and west (Figure 12 and Figure 13). The recent increase in the biomass indices has mostly taken place in the southeast and southwest areas (Figure 11 and Figure 13).