Content uploaded by Nathan Pacoureau
Author content
All content in this area was uploaded by Nathan Pacoureau on Apr 09, 2021
Content may be subject to copyright.
The IUCN Red List of Threatened Species™
ISSN 2307-8235 (online)
IUCN 2020: T161542A124503504
Scope(s): Global
Language: English
Amblyraja radiata, Thorny Skate
Assessment by: Kulka, D.W., Ellis, J., Anderson, B., Cotton, C.F., Derrick, D.,
Pacoureau, N. & Dulvy, N.K.
View on www.iucnredlist.org
Citation: Kulka, D.W., Ellis, J., Anderson, B., Cotton, C.F., Derrick, D., Pacoureau, N. & Dulvy, N.K.
2020. Amblyraja radiata. The IUCN Red List of Threatened Species 2020: e.T161542A124503504.
https://dx.doi.org/10.2305/IUCN.UK.2020-3.RLTS.T161542A124503504.en
Copyright: © 2020 International Union for Conservation of Nature and Natural Resources
Reproduction of this publication for educational or other non-commercial purposes is authorized without prior written
permission from the copyright holder provided the source is fully acknowledged.
Reproduction of this publication for resale, reposting or other commercial purposes is prohibited without prior written
permission from the copyright holder. For further details see Terms of Use.
The IUCN Red List of Threatened Species™ is produced and managed by the IUCN Global Species Programme, the IUCN
Species Survival Commission (SSC) and The IUCN Red List Partnership. The IUCN Red List Partners are: Arizona State
University; BirdLife International; Botanic Gardens Conservation International; Conservation International; NatureServe;
Royal Botanic Gardens, Kew; Sapienza University of Rome; Texas A&M University; and Zoological Society of London.
If you see any errors or have any questions or suggestions on what is shown in this document, please provide us with
feedback so that we can correct or extend the information provided.
THE IUCN RED LIST OF THREATENED SPECIES™
Taxonomy
Kingdom Phylum Class Order Family
Animalia Chordata Chondrichthyes Rajiformes Rajidae
Scientific Name:ÊÊAmblyraja radiata (Donovan, 1808)
Synonym(s):
• Raia scabrata Garman, 1913
• Raja radiata Donovan, 1808
Regional Assessments:
• Europe
Common Name(s):
• English: Thorny Skate, Starry Ray
Taxonomic Source(s):
Fricke, R., W.N. Eschmeyer and R. Van der Laan (eds.). 2020. Eschmeyer's catalog of fishes: Genera,
species, references. Available at:
http://researcharchive.calacademy.org/research/ichthyology/catalog/fishcatmain.asp. (Accessed: March
2020).
Taxonomic Notes:
McEachran and Dunne (1998) moved this species from genus Raja to Amblyraja.
Assessment Information
Red List Category & Criteria: Vulnerable A2bcd ver 3.1
Year Published: 2020
Date Assessed: July 1, 2019
Justification:
The Thorny Skate (Amblyraja radiata) is a medium-sized (to 111 cm total length) skate occurring in the
North Atlantic from South Carolina (USA) to Greenland, Iceland, Ireland, United Kingdom, Norway, and
to Russia. It is demersal on continental and insular shelves and slopes from nearshore to 1,400 m
depths, usually at 25–440 m. This skate is genetically indistinguishable throughout its range, yet it
exhibits marked life history differences on either side of the Atlantic and in different parts of the
Northwest Atlantic, growing more slowly, maturing later and reaching a larger maximum size in the
southern extent of their Northwest Atlantic distribution. The generation length is 16 years in the
Northwest Atlantic (south) and 10.6 years elsewhere. It was subject to intensive target fisheries in the
Northwest Atlantic and taken as bycatch in mainly trawl, but also longline and gillnet, fisheries in the
USA and Canadian waters south of the Laurentian Channel (Georges Bank and Scotian Shelf). In the USA,
commercial retention of Thorny Skate was banned 2003, but it is still taken as bycatch and discarded
from trawl fisheries. In Canada on the Scotian Shelf, target fisheries ended in 2002 and any bycatch is
© The IUCN Red List of Threatened Species: Amblyraja radiata – published in 2020.
https://dx.doi.org/10.2305/IUCN.UK.2020-3.RLTS.T161542A124503504.en
1
now discarded. In the Northeast Atlantic, this skate has limited value and it is generally discarded and
has a low discard mortality. Population trends and management vary widely, resulting in different status
and trends throughout its range. On both sides of the Atlantic, the southern-most populations of this
boreal species have shifted northward in response to climate-change induced habitat shifting and
alteration, which, in combination with earlier intensive fishing, resulted in very steep declines (>80%
reduction in three generations) in the most southerly parts of its distribution. At more northerly
latitudes, earlier levels of exploitation have ceased or greatly decreased resulting in recovery and
increasing abundance. Overall, Thorny skate has undergone an estimated population reduction of
30–49% over the last three generation lengths (32–48 years) due the combination of exploitation with
habitat shifting and alteration due to climate change at lower latitudes while, further north, earlier
levels of exploitation that have ceased or greatly decreased and it is assessed as Vulnerable A2bcd.
Previously Published Red List Assessments
2009 – Vulnerable (VU)
https://dx.doi.org/10.2305/IUCN.UK.2009-2.RLTS.T161542A5447511.en
Geographic Range
Range Description:
Thorny Skate is found in the North Atlantic ranging from South Carolina, USA to Greenland, Iceland,
Ireland, United Kingdom, Norway, extending through the Barents Sea to Russia (Last et al. 2016).
Country Occurrence:
Native, Extant (resident): Belgium; Canada (Labrador, New Brunswick, Newfoundland I, Nova Scotia,
Nunavut, Québec); Denmark; Faroe Islands; France (France (mainland)); Germany; Greenland; Iceland;
Ireland; Netherlands; Norway; Russian Federation (European Russia); Svalbard and Jan Mayen; Sweden;
United Kingdom (Great Britain, Northern Ireland); United States (Connecticut, Delaware, Maine,
Massachusetts, New Hampshire, New Jersey, New York, North Carolina, South Carolina, Virginia)
FAO Marine Fishing Areas:
Native: Atlantic - northwest
Native: Atlantic - northeast
© The IUCN Red List of Threatened Species: Amblyraja radiata – published in 2020.
https://dx.doi.org/10.2305/IUCN.UK.2020-3.RLTS.T161542A124503504.en
2
Distribution Map
© The IUCN Red List of Threatened Species: Amblyraja radiata – published in 2020.
https://dx.doi.org/10.2305/IUCN.UK.2020-3.RLTS.T161542A124503504.en
3
Population
There are no data available on the absolute global population size of Thorny Skate. Population trend
data were analyzed over three generation lengths using a Bayesian state-space framework (Sherley et al.
2020, Winker et al. 2020). This analysis yields an annual rate of change, a median change over three
generation lengths, and the probability of the most likely IUCN Red List category percent change over
three generations (see the Supplementary Information). These time-series exhibit striking variation and
were grouped into six regions.
• Northwest Atlantic (south) comprised of four time-series: (a) Southern Gulf of St. Lawrence (4T) trawl
survey index of abundance of mature individuals) (1971–2018), (b) Scotian Shelf and Bay of Fundy
(4VWX) trawl survey index of abundance of mature individuals (1970–2017), (c) Georges Banks,
Canada/Gulf of Maine, USA (5Z) relative abundance trawl survey index of mature individuals
(1970–2017), and (d) the standardized catch-per-unit-effort (CPUE) data from the USA Northeast
Fisheries Science Centre (NEFSC) Fall survey (1963–2018) (D.W. Kulka unpubl. data 2020, compiled from
Fisheries and Oceans Canada, and NOAA USA).
• Northwest Atlantic (north) comprised of three time-series: (a) Newfoundland and Labrador Shelf
(2J3K) Fall trawl survey CPUE of mature individuals (1977–2017), (b) Grand Banks (3LNOPs) Spring trawl
survey CPUE of mature individuals (1973–2017), and (c) Northern Gulf of St. Lawrence (4RS) trawl
survey index of abundance of mature individuals (1991–2018) (D.W. Kulka unpubl. data 2020, compiled
from Fisheries and Oceans Canada, and NOAA USA).
• North central Atlantic (west Greenland) comprised of two time-series from the Greenland Shrimp and
Fish survey in West Greenland trawl survey of abundance of individuals (millions) (1992–2017) (Nygaard
and Nogueira 2019).
• North central Atlantic (Iceland) comprised of two time-series from the Iceland Spring and Autumn
trawl survey indices of biomass (1986–2020) (MFRI 2020).
• Northeast Atlantic (south) comprised of two time-series from the North Sea International Bottom
Trawl Survey in Quarter 1 and 3 in (Groundfish Areas 1 to 4 and 6 to 9) nominal CPUE of individual per
hour (1980–2020) (J.R. Ellis unpubl. data 2020, compiled from the Database of Trawl Surveys DATRAS).
• Northeast Atlantic (north) comprised of two time-series from two swept area based indices of total
biomass (metric tonnes) from (a) the Barents Sea Ecosystem Survey (2003-2016) and (b) the Coastal
Survey along the Norwegian coast (north of 62°N) (2003–2016) (Knutsen et al. 2017).
First, the trend analysis of the four time-series from the Northwest Atlantic (south) reveal very steep
annual rates of decline of 6.5%, consistent with an estimated median decline of 96% over three
generation lengths (48 years), with the highest probability of >80% reduction over three generation
lengths (see Supplementary Information figure 1).
Second, the trend analysis of the three time-series from the Northwest Atlantic (north) revealed an
initial steep decline from 1978 ending in 1995 before recovering steadily to near historical index values.
Overall, the annual rate of increase of 1.7% is consistent with a rapid increase of 1.4% in the most recent
generation and an estimated median increase of 8.5%% over the past three generation lengths (31.8
years) (see Supplementary Information figure 2).
Third, the trend analysis of the North Atlantic (West Greenland) revealed a slight increase with overall
© The IUCN Red List of Threatened Species: Amblyraja radiata – published in 2020.
https://dx.doi.org/10.2305/IUCN.UK.2020-3.RLTS.T161542A124503504.en
4
annual rates of increase of 1.5%, consistent with an estimated median increase of 52.9% over three
generation lengths (31.8 years) (see Supplementary Information figure 3). The shorter east Greenland
survey (2008–2013) was not analysed but exhibits a similar stable trend.
Fourth, the trend analysis of the North Atlantic (Iceland) revealed a steady decline from the mid-1980s
with annual rates of decrease of 1.7%, consistent with an estimated median decrease of 42.8% over
three generation lengths (31.8 years) (see Supplementary Information figure 4).
Fifth, the trend analysis of the Northeast Atlantic (south) in the North Sea revealed a steady increase in
abundance from 1980 until a peak in 1992, thereafter there has been a steady steep decline with annual
rates of decrease of 2.2% consistent with an estimated median decrease of 83.2% over three generation
lengths (31.8 years), with the highest probability of >80% reduction over three generation lengths (see
Supplementary Information figure 5). However, this decline should also be considered in relation to the
longer time-series which indicated an increase in abundance from 1980 until a peak in 1992, with the
current catch-per-unit-effort at similar levels to that observed at the start of the time-series. The recent
elevated abundance in the 1980–1990s is more similar to the early 1900s, while between these periods
Thorny Skate abundance was low (Sguotti et al. 2016). Whilst the reasons for this are uncertain,
multispecies interactions and environmental conditions are potential factors affecting this region.
Sixth, the trend analysis of the Northeast Atlantic (north) in the Barents Sea and Norwegian coast
revealed steady and rapid increase with annual rates of increase of 8.1%, consistent with an estimated
median increase of 226% over three generation lengths (31.8 years), with the highest probability of an
increase over three generation lengths (see Supplementary Information figure 6).
Overall, there is a strong latitudinal pattern in population trends, repeated on both sides of the Atlantic,
with very steep declines (>80% reduction in three generations) in the most southerly parts of this
species' distribution (and Iceland) coupled with recovery and increasing abundance at more northerly
latitudes. The overall weighted trend was calculated by weighting each time-series by an area–based
estimate of the size of each region as a proportion of the species’ global distribution (EOO: extent of
occurrence, see Supplementary Information Table 1). When these trends are taken together, there is a
42% probability that the species is threatened and a 54% probability that it is Least Concern. Overall,
Thorny skate has undergone an estimated population reduction of 30–49% over the last three
generation lengths (31.8–48 years) due the combination of exploitation with habitat shifting and
alteration due to climate change at lower latitudes while, further north, earlier levels of exploitation
that have ceased or greatly decreased. Therefore, Thorny Skate is assessed as Vulnerable A2bcd.
For further information about this species, see Supplementary Material.
Current Population Trend:ÊÊDecreasing
Habitat and Ecology (see Appendix for additional information)
The Thorny Skate is demersal on continental and insular shelves and slopes from nearshore to 1,400 m
depths, usually at 25–440 m (Last et al. 2016). There is regional variation in maximum size, it reaches a
maximum size of 66 cm total length (TL) (North Sea) to 111 cm (NW Atlantic) (Walker 1998, Ebert and
Stehmann 2013). Reproduction is oviparous with fecundity ranging from 10 to 45 egg cases per year
(Templeman 1987), but only 38% of eggs hatching (COSEWIC 2012). Reproduction occurs year round
© The IUCN Red List of Threatened Species: Amblyraja radiata – published in 2020.
https://dx.doi.org/10.2305/IUCN.UK.2020-3.RLTS.T161542A124503504.en
5
and size-at-hatch is 10.4–11.4 cm TL (Kulka et al. 2006). Females mature at 38.4–87.3 cm TL and males
mature at 44–83 cm TL (McCully et al. 2012, Lynghammar et al. 2016). Two generation lengths were
used to reflect the striking life history differences between the Northwest Atlantic (south) and
elsewhere. Information on age-at-maturity is available for only two areas, in the North Sea (Northeast
Atlantic) age-at-maturity (Am) is 5.6 years (Walker 1998) and age-at-maturity is 11 years on the Scotian
Shelf (Northwest Atlantic, south) (McPhie and Campana 2009, Simon et al. 2012). From these studies,
generation length is calculated as 10.6 years (North Sea, Northeast Atlantic) and 16 years (Scotian
ShelfNorthwest Atlantic, south), based on GL = Am + 1/M, assuming a natural rate of mortality (M) of
0.2.
Systems:ÊÊMarine
Use and Trade
This skate is used for meat, and the wings are exported to Europe. In the Northeast Atlantic, Thorny
Skate is discarded as it is of limited value due to its smaller size (Ebert and Stehmann 2013).
Threats (see Appendix for additional information)
This skate was taken in target fisheries and as a bycatch mostly in demersal trawl fisheries, with some
catch from gillnet and longline. Most target fisheries have been closed (in Canada) or commercial
retention has been prohibited (in USA), but it is taken as bycatch in trawl fisheries and the majority are
discarded alive in the USA (Sosebee et al. 2016, Sosebee 2019). Discard mortality for Thorny Skate in the
USA bottom trawl fishery is estimated to be low (approximately 16.5–24.5%) (Mandelman et al. 2013,
Knotek et al. 2020). There is a target fishery on the Grand Banks (NAFO Division 3LNOPs) straddling the
200 mile limit and is managed through a total allowable catch (TAC) by the Northwest Atlantic Fisheries
Organisation (NAFO). The TAC has decreased over time but in 2017 continues to exceed the commercial
catch during a period where ‘minimal or no rebuilding of this stock occurred’ (Simpson et al. 2018) but a
population increase can be observed from mid-1990 to 2010, which then levelled off (see
Supplementary Information). In the Barents Sea and Norwegian Sea in the Northeast Atlantic, Thorny
Skate is the greatest fraction of biomass of skates caught in surveys or as bycatch of demersal trawling,
is generally discarded (Dolgov et al. 2005, ICES-WGEF 2018). This species is taken as bycatch in demersal
trawl fisheries in the North Sea (Northeast Atlantic), but it is not targeted and is usually discarded
(Walker and Heessen 1996). The Thorny Skate is a boreo-Arctic species, consequently, some areas of
former habitat have become less suitable as water temperature increases, resulting in northward
distribution shifts and declines in the southern parts of its distributional range, particularly in the North
Sea (Sguotti et al. 2016), and northward shifts have been documented for the Scotian Shelf (Stuart et al.
2020) as well as in the Southern Gulf of St. Lawrence and Newfoundland (Pinsky et al. 2013).
Conservation Actions (see Appendix for additional information)
Commercial retention of this species has been banned since 2003 in the USA, but it is taken as bycatch
in trawl fisheries and the majority are discarded alive (Sosebee et al. 2016, Sosebee 2019). Target
fisheries for mixed skate on the Scotian Shelf were closed in 2002 due to steep declines of Winter Skate
(Leucoraja ocellata) (COSEWIC 2012, 2015). On the Grand Banks, this species is managed under quota
by the Northwest Atlantic Fisheries Organization (NAFO). Spain and Portugal take 90% of quota, which is
currently set at 6,000 tonnes (Simpson et al. 2018). Commercial retention of this species has also been
prohibited in European Union waters of the North Sea and Skagerrak, Northeast Atlantic (EU waters of
© The IUCN Red List of Threatened Species: Amblyraja radiata – published in 2020.
https://dx.doi.org/10.2305/IUCN.UK.2020-3.RLTS.T161542A124503504.en
6
ICES Subarea 4 and Divisions 2.a and 4.a) since 2014.
Credits
Assessor(s): Kulka, D.W., Ellis, J., Anderson, B., Cotton, C.F., Derrick, D., Pacoureau, N. &
Dulvy, N.K.
Reviewer(s): Pollom, R. & Rigby, C.L.
Contributor(s): Bowlby, H., Clark, D., Endicott, M., Fowler, M., Gauthier, J., Jakobsdóttir, B,
Gedamke, T., Knutsen, M., Miri, C., Pasolini, P., Pinsky, L, Regnier-McKellar, C.,
Simpson, M., Sosebee, K., Sulikowski, J., Swain, D., Treble , M. & Winker, H.
Facilitator(s) and
Compiler(s):
Kyne, P.M., Crysler, Z. & Dulvy, N.K.
Authority/Authorities: IUCN SSC Shark Specialist Group (sharks and rays)
© The IUCN Red List of Threatened Species: Amblyraja radiata – published in 2020.
https://dx.doi.org/10.2305/IUCN.UK.2020-3.RLTS.T161542A124503504.en
7
Bibliography
COSEWIC. 2012. COSEWIC assessment and status report on the Thorny Skate Amblyraja radiata in
Canada. Committee on the Status of Endangered Wildlife in Canada, Ottawa, xviii + 75 pp.
COSEWIC. 2015. COSEWIC assessment and status report on the Winter Skate Leucoraja ocellata, Gulf of
St. Lawrence population, Eastern Scotian Shelf - Newfoundland population and Western Scotian Shelf -
Georges Bank population in Canada. Committee on the Status of Endangered Wildlife in Canada,
Ottawa, xviii + 46 pp.
Dolgov, A.V., Drevetnyak, K.V. and Gusev, E.V. 2005. Bycatch of Skates in Trawl and Longline Fisheries in
the Barents Sea. e-Journal of Northwest Atlantic Fishery Science 35(art. 33).
Ebert, D.A. and Stehmann, M.F.W. 2013. Sharks, batoids, and chimaeras of the North Atlantic. FAO
Species Catalogue for Fishery Purposes No. 7. Food and Agricultural Organization of the United Nations
(FAO). FAO, Rome.
ICES-WGEF. 2018. Report of the ICES Working Group on Elasmobranch Fishes (WGEF). ICES CM
2018/ACOM:16. International Council for the Exploration of the Seas, Copenhagen, Denmark.
IUCN. 2020. The IUCN Red List of Threatened Species. Version 2020-3. Available at: www.iucnredlist.org.
(Accessed: 10 December 2020).
Knotek, R., Kneebone, J., Sulikowski, J., Curtis, T., Jurek, J. and Mandelman, J. 2020. Utilization of pop-up
satellite archival transmitting tags to evaluate thorny skate (Amblyraja radiata) discard mortality in the
Gulf of Maine groundfish bottom trawl fishery. ICES Journal Of Marine Science 77: 256-266.
Knutsen, M., Thangstad, T.H., Søvik, G. and Albert, O.T. 2017. Survey trends of skates in Norwegian
waters. Working document for the ICES Elasmobranch Working Group (WGEF) 2017. Institute of Marine
Research, Tromso, Norway.
Kulka, D.W., Simpson, M.R. and Miri, C.M. 2006. An Assessment of Thorny Skate (Amblyraja radiata
Donovan, 1808) on the Grand Banks of Newfoundland.
Last, P., White, W., de Carvalho, M., Séret, B., Stehmann, M. and Naylor, G. 2016. Rays of the World.
CSIRO Publishing, Clayton.
Lynghammar, A., Præbel, K., Bhat, S., Fevolden, S.E. and Christiansen, J.S. 2016. Widespread physical
mixing of starry ray from differentiated populations and life histories in the North Atlantic. Marine
Ecology Progress Series 562: 123-134.
Mandelman J.W., Cicia, A.M., Ingram, G.W., Driggers, W.B., Coutre, K.M. and Sulikowski, J.A. 2013. Short-
term post-release mortality of skates (family Rajidae) discarded in a western North Atlantic commercial
otter trawl fishery. Fisheries Research 139: 76-84.
McCully, S.R., Scott, F. and Ellis, J.R. 2012. Lengths at maturity and conversion factors for skates (Rajidae)
around the British Isles, with an analysis of data in the literature. ICES Journal of Marine Science 69:
1812-1822.
McEachran, J.D. and Dunn, K.A. 1998. Phylogenetic analysis of skates, a morphologically conservative
clade of elasmobranchs (Chondrichthyes: Rajidae). Copeia 1998: 271-290.
McPhie, R.P. and Campana, S.E. 2009. Bomb dating and age determination of skates (family Rajidae) off
the eastern coast of Canada. ICES Journal of Marine Science 66(3): 546–560.
MFRI. 2020. STARRY RAY – TINDASKATA Amblyraja radiata. MFRI Assessment Reports. Marine and
© The IUCN Red List of Threatened Species: Amblyraja radiata – published in 2020.
https://dx.doi.org/10.2305/IUCN.UK.2020-3.RLTS.T161542A124503504.en
8
Freshwater Research Institute, Reykjavik, Iceland.
Nygaard, R. and Nogueira, A. 2019. Biomass and abundance of demersal fish stocks off West and East
Greenland estimated from the Greenland Institute of Natural resources Shrimp Fish Survey, 1988-2013.
33rd Scientific Council Research Meeting of North Atlantic Fisheries Organisation NAFO SCR Doc. 19/008:
1-44.
Packer, D.B., Zetlin, C.A. and Vitaliano, J.J. 2003. Essential fish habitat source document: Thorny Skate,
Amblyraja radiata, life history and habitat characteristics. NOAA Technical Memorandum. U.S.
Department of Commerce, Massachusetts, USA.
Pinsky, M.L., Worm, B., Fogarty, M.J., Sarmiento, J.L. and Levin, S.A. 2013. Marine taxa track local climate
velocities. Science 341: 1239-1242.
Sguotti, C., Lynam, C.P., Garcia-Carreras, B., Ellis, J.R. and Engelhard, G.H. 2016. Distribution of skates
and sharks in the North Sea: 112 years of change. Global Change Biology 22: 2729-2743.
Sherley, R.B., Winker, H., Rigby, C.L., Kyne, P.M., Pollom, R., Pacoureau, N., Herman, K., Carlson, J.K., Yin,
J.S., Kindsvater, H.K. and Dulvy, N.K. 2020. Estimating IUCN Red List population reduction: JARA—A
decision-support tool applied to pelagic sharks. Conservation Letters 13(2): e12688.
Simon, J.E., Rowe, S. and Cook, A. 2012. Status of smooth skate (Malacoraja senta) and thorny skate
(Amblyraja radiata) in the Maritimes Region. Fisheries and Oceans Canada, Can. Sci. Advis. Sec. Res.
Doc. 2011/080: viii + 102 p.
Simpson, M.R., Miri, C.M. and Collins, R.K. 2018. Assessment of Thorny Skate (Amblyraja radiata
Donovan, 1808) in NAFO Divisions 3LNO and Subdivision 3Ps. NAFO Scientific Council Research
Document 18/027: 1-34.
Sosebee, K. 2019. 2018 NE Skate Stock Status Update. NOAA Northeast Fisheries Science Center.
Sosebee, K., Miller, A., O’Brien, L., McElroy, D. and Sherman, S. 2016. Update of Thorny Skate (Amblyraja
radiata) Commercial and Survey Data. US Dept Commer, Northeast Fish. Sci. Cent. Ref. Doc.16-08 145 p.
Stuart, M.R., Forrest, D.L., Batt, R.D. and Pinsky, M.L. 2020. OceanAdapt: Update 2020. Available at:
http://doi.org/10.5281/zenodo.3885625. (Accessed: 1st July 2020).
Templeman, W. 1987. Differences in sexual maturity and related characteristics between populations of
thorny skate Raja radiata in the northwest atlantic. Journal of Northwest Atlantic Fisheries Science 44(1):
155-168.
Walker. P.A. 1998. Fleeting Images, Dynamics of North Sea Ray Populations. Ph.D. Thesis, University of
Amsterdam.
Walker P.A. and Heessen H.J.L. 1996. Long-term changes in ray populations in the North Sea. ICES
Journal of Marine Science 53: 1085-1093.
Winker, H, Pacoureau, N. and Sherley, R.B. 2020. JARA: 'Just Another Red List Assessment'. BioRᵴiv
Preprint: http://dx.doi.org/10.1101/672899.
Citation
Kulka, D.W., Ellis, J., Anderson, B., Cotton, C.F., Derrick, D., Pacoureau, N. & Dulvy, N.K. 2020. Amblyraja
radiata. The IUCN Red List of Threatened Species 2020: e.T161542A124503504.
https://dx.doi.org/10.2305/IUCN.UK.2020-3.RLTS.T161542A124503504.en
© The IUCN Red List of Threatened Species: Amblyraja radiata – published in 2020.
https://dx.doi.org/10.2305/IUCN.UK.2020-3.RLTS.T161542A124503504.en
9
Disclaimer
To make use of this information, please check the Terms of Use.
External Resources
For Supplementary Material, and for Images and External Links to Additional Information, please see the
Red List website.
© The IUCN Red List of Threatened Species: Amblyraja radiata – published in 2020.
https://dx.doi.org/10.2305/IUCN.UK.2020-3.RLTS.T161542A124503504.en
10
Appendix
Habitats
(http://www.iucnredlist.org/technical-documents/classification-schemes)
Habitat Season Suitability Major
Importance?
9. Marine Neritic -> 9.4. Marine Neritic - Subtidal Sandy Resident Suitable Yes
9. Marine Neritic -> 9.5. Marine Neritic - Subtidal Sandy-Mud Resident Suitable Yes
9. Marine Neritic -> 9.6. Marine Neritic - Subtidal Muddy Resident Suitable Yes
11. Marine Deep Benthic -> 11.1. Marine Deep Benthic - Continental
Slope/Bathyl Zone (200-4,000m)
- - -
Use and Trade
(http://www.iucnredlist.org/technical-documents/classification-schemes)
End Use Local National International
Food - human No Yes Yes
Threats
(http://www.iucnredlist.org/technical-documents/classification-schemes)
Threat Timing Scope Severity Impact Score
5. Biological resource use -> 5.4. Fishing & harvesting
aquatic resources -> 5.4.2. Intentional use: (large
scale) [harvest]
Ongoing Minority (50%) Slow, significant
declines
Low impact: 5
Stresses: 2. Species Stresses -> 2.1. Species mortality
5. Biological resource use -> 5.4. Fishing & harvesting
aquatic resources -> 5.4.4. Unintentional effects:
(large scale) [harvest]
Ongoing Minority (50%) Slow, significant
declines
Low impact: 5
Stresses: 2. Species Stresses -> 2.1. Species mortality
11. Climate change & severe weather -> 11.1. Habitat
shifting & alteration
Ongoing Minority (50%) Slow, significant
declines
Low impact: 5
Stresses: 2. Species Stresses -> 2.2. Species disturbance
Conservation Actions in Place
(http://www.iucnredlist.org/technical-documents/classification-schemes)
Conservation Action in Place
In-place research and monitoring
Action Recovery Plan: No
© The IUCN Red List of Threatened Species: Amblyraja radiata – published in 2020.
https://dx.doi.org/10.2305/IUCN.UK.2020-3.RLTS.T161542A124503504.en
11
Conservation Action in Place
Systematic monitoring scheme: Yes
In-place land/water protection
Conservation sites identified: Yes, over part of range
Area based regional management plan: No
Occurs in at least one protected area: No
Invasive species control or prevention: Not Applicable
In-place species management
Harvest management plan: Yes
Successfully reintroduced or introduced benignly: No
Subject to ex-situ conservation: No
In-place education
Subject to recent education and awareness programmes: No
Included in international legislation: No
Subject to any international management / trade controls: No
Conservation Actions Needed
(http://www.iucnredlist.org/technical-documents/classification-schemes)
Conservation Action Needed
3. Species management -> 3.1. Species management -> 3.1.1. Harvest management
3. Species management -> 3.1. Species management -> 3.1.2. Trade management
5. Law & policy -> 5.1. Legislation -> 5.1.2. National level
Research Needed
(http://www.iucnredlist.org/technical-documents/classification-schemes)
Research Needed
1. Research -> 1.2. Population size, distribution & trends
1. Research -> 1.3. Life history & ecology
2. Conservation Planning -> 2.1. Species Action/Recovery Plan
3. Monitoring -> 3.1. Population trends
3. Monitoring -> 3.2. Harvest level trends
© The IUCN Red List of Threatened Species: Amblyraja radiata – published in 2020.
https://dx.doi.org/10.2305/IUCN.UK.2020-3.RLTS.T161542A124503504.en
12
Additional Data Fields
Distribution
Lower depth limit (m): 1,400
Upper depth limit (m): 0
Habitats and Ecology
Generation Length (years): 16
© The IUCN Red List of Threatened Species: Amblyraja radiata – published in 2020.
https://dx.doi.org/10.2305/IUCN.UK.2020-3.RLTS.T161542A124503504.en
13
The IUCN Red List of Threatened Species™
ISSN 2307-8235 (online)
IUCN 2020: T161542A124503504
Scope(s): Global
Language: English
The IUCN Red List Partnership
The IUCN Red List of Threatened Species™ is produced and managed by the IUCN Global Species
Programme, the IUCN Species Survival Commission (SSC) and The IUCN Red List Partnership.
The IUCN Red List Partners are: Arizona State University; BirdLife International; Botanic Gardens
Conservation International; Conservation International; NatureServe; Royal Botanic Gardens, Kew;
Sapienza University of Rome; Texas A&M University; and Zoological Society of London.
THE IUCN RED LIST OF THREATENED SPECIES™
© The IUCN Red List of Threatened Species: Amblyraja radiata – published in 2020.
https://dx.doi.org/10.2305/IUCN.UK.2020-3.RLTS.T161542A124503504.en
14