STARRY RAY

Amblyraja radiata


Technical report
Published by

Marine and Freshwater Research Institute, Iceland

Published

7 June 2024

General information

Starry ray is by far the most abundant elasmobranch species in Icelandic waters. It has a widespread distribution over the Icelandic shelf and upper slope at depths from 20-1000 m but is most common at 30-200 m. In Icelandic surveys, starry ray is rarely caught larger than 70 cm but most commonly at 30-50 cm. Reproduction is believed to occur to some extent throughout the year, however mainly during summer.

The fishery and landings

Starry ray is abundant in Icelandic waters and is a common bycatch in variety of fishing gears. Catches of starry ray are taken all around Iceland but mostly within Faxaflói in the southwest (Figure 1). The increased landings since the 1990s are partly related to an increased retention, compensating for a lower abundance of the D. batis complex. However, fishing regulations are likely responsible for the high proportion of landings from Danish seine in the nineties. Since 2007, landings are mainly reported from the longline fishery (Figure 2). Reported landings increased from 500 tonnes in 2007 to more than 1700 tonnes in 2012. Thereafter, landings have shown a steady decline and in 2022 they didn´t exceed 300 tonnes. Last year there are drastic decline in landings from the longline fishery (Figure 2). A large proportion of the landings is for local consumption linked to the yule season. This is reflected in the strong seasonality in landings; most landings are reported from September-November each year (Figure 3).

Figure 1: Starry ray. Geographical distribution of the Icelandic fishery since 2014 as reported in logbooks.
Figure 2: Starry ray. Landings by fishing gear since 1990 according to statistics from the Directorate of Fisheries. Upper panel: Catches (kt), lower panel: Proportion of catches by gear. BMT: Bottom trawl, DSE: Danish seine and LLN: Long line.
Figure 3: Starry ray. Proportion of monthly catch to each year since 2009 according to statistics from the Directorate of Fisheries.

Survey data

Distribution and biomass indices

Starry ray is a frequent catch in MFRI spring (IS-SMB) and autumn surveys (IS-SMH). Seasonal differences in distributional patterns have been noted, with starry ray much less abundant on the shelf in IS-SMH than in IS-SMB. In IS-SMB, starry ray is found at 86% of all stations, but at about 50% of stations in the IS-SMH (Figure 4).

Figure 4: Starry ray. Frequency (occurrence at % stations) in IS-SMB and IS-SMH.

In MFRI groundfish surveys, starry ray is most abundant in the N and the NW (Figures Figure 5 and Figure 6). In IS-SMB there is a high abundance on the shelf off N-Iceland and in near-shore areas in the south and southeast (Figure 5 a,c,e). In IS-SMH, the main distribution is on the shelf break and starry ray is almost absent from the southern area (Figure 5 b,d,f). Seasonal migration could to some extend explain these seasonal differences in distributional patterns. However, the large seasonal difference in occurrence and catches, especially in the smallest length groups (>30 cm, Figure 5 c,d) could also be partly explained by differences in survey gear (size and weight). Starry ray is a frequent bycatch in several other MFRI surveys.The coastal shrimp survey occurs at various time periods in fjords and near coastal areas and starry ray is widely distributed within the survey areas (Figure 6 a). Similarly, starry ray is a frequent bycatch in the gillnet survey occurring early April each year (Figure 6 b).

Figure 5: Starry ray. Spatial distribution in IS-SMB 2024 (a,c,e) and in IS-SMH 2023 (b,d,f). The top panel shows all data, the middle panel shows individuals <30 cm, and the bottom panel shows larger individuals (>50cm).
Figure 6: Starry ray. Spatial distribution in a) shrimp and lobster surveys in 2023 and b) the gillnet survey (IS-SMN) 2023.

In general, estimates of total biomass of starry ray in IS-SMB show a declining trend over the survey period 1985-2024 with few exceptions such as the estimate from 2023 which is the highest since 2004 (Figure 7).The biomass index in IS-SMB has decreased from 19 000 (average 1985-2000) to 14 000 (average 2001-2024). Decreasing trend is in particularly notable for large fish (≥50 cm) in years 1993-2008. Since 2010 the index for large fish has remained relative stable. Estimated biomass of juveniles (≤20 cm) in IS-SMB showed large variations in years 2003-2013 but appears to be stable with increasing trend in last decade. In IS-SMH, total biomass are overall lower than in IS-SMB and in particular, small individuals (≤20 cm) are hardly caught.

Figure 7: Starry ray. Total biomass indices (upper left), biomass indices of large individuals (≥50 cm, upper right) and juvenile abundance indices (≤20 cm, lower left), from IS-SMB (black line) and IS-SMH (black dots).

In IS-SMB the highest proportion of catch is taken in areas off NW-, NE- and SE- Iceland and the reduction in biomass is most prominent in these areas. In IS-SMH, the highest proportion of catch is taken in areas off NW- and NE-Iceland; the areas where a reduction in abundance has taken place (Figure 8).

Figure 8: Starry ray. Spatial distribution of biomass indices from IS-SMB and IS-SMH.

Life history information

Length distributions from surveys indicate that most specimens are <60 cm . Mean size varies from 35-49 cm depending on surveys (Figure 9). The length distribution is negatively skewed as the proportion of large fish decreases quite abruptly (Figure 9) which is likely due to morphological attributes of the species.