Patterns of extirpation. II. The role of connectivity in the decline and recovery of elasmobranch populations in the German Bight as inferred from survey data
Abstract:Abundance trends and distribution patterns from 1902 to 1932 for 7 elasmobranch species in the German Bight (eastern central North Sea) were analyzed and compared to survey trends for 1991 to 2009. Abundances of thornback ray Raja clavata, common skate Dipturus batis, smoothhound Mustelus spp., tope shark Galeorhinus galeus, and spiny dogfish Squalus acanthias declined and common skate was extirpated, while abundances of starry ray Amblyraja radiata and lesser spotted dogfish Scyliorhinus canicula increased. A… Show more
“…The interpretation of these data, however, requires a degree of caution, due to possible changes in sampling methods over time – issues that are, unfortunately, often associated with long‐term, historical data sets that predate full standardisation of surveys and documentation of their gears (Ellis et al ., ; Bartolino et al ., ; Fock et al ., ). Despite these issues, the present study can help inform on both the long‐term population dynamics of North Sea elasmobranchs and the assemblage at a time of low fishing impacts (Walker & Heessen, ; Rogers & Ellis, ).…”
Section: Discussionmentioning
confidence: 99%
“…S4.2). Over this period, beam trawl pressure has been higher in the eastern than western North Sea (Engelhard et al ., ) and has likely impacted not only adult skates but also egg‐laying and nursery grounds in coastal zones and outer estuaries (Frid et al ., ; Ellis et al ., ; Kinney & Simpfendorfer, ; Fock et al ., ). Our results show that, until the 1960s, the overall skate distribution coincided with that of thornback ray, thought to be the historically dominant species.…”
How have North Sea skate and shark assemblages changed since the early 20th century when bottom trawling became widespread, whilst their environment became increasingly impacted by fishing, climate change, habitat degradation and other anthropogenic pressures? This article examines long-term changes in the distribution and occurrence of the elasmobranch assemblage of the southern North Sea, based on extensive historical time series of fishery-independent survey data. In general, larger species (thornback ray, tope, spurdog) exhibited long-term declines, and the largest (common skate complex) became locally extirpated (as did angelshark). Smaller species increased (spotted and starry ray, lesser-spotted dogfish) as did smooth-hound, likely benefiting from greater resilience to fishing and/or climate change. This indicates a fundamental shift from historical dominance of larger, commercially valuable species to current prevalence of smaller, more productive species often of low commercial value. In recent years, however, some trends have reversed, with the (cold-water associated) starry ray now declining and thornback ray increasing. This shift may be attributed to (i) fishing, including mechanised beam trawling introduced in the 1960s-1970s, and historical target fisheries for elasmobranchs; (ii) climate change, currently favouring warm-water above cold-water species; and (iii) habitat loss, including potential degradation of coastal and outer estuarine nursery habitats. The same anthropogenic pressures, here documented to have impacted North Sea elasmobranchs over the past century, are likewise impacting shelf seas worldwide and may increase in the future; therefore, parallel changes in elasmobranch communities in other regions are to be expected.
“…The interpretation of these data, however, requires a degree of caution, due to possible changes in sampling methods over time – issues that are, unfortunately, often associated with long‐term, historical data sets that predate full standardisation of surveys and documentation of their gears (Ellis et al ., ; Bartolino et al ., ; Fock et al ., ). Despite these issues, the present study can help inform on both the long‐term population dynamics of North Sea elasmobranchs and the assemblage at a time of low fishing impacts (Walker & Heessen, ; Rogers & Ellis, ).…”
Section: Discussionmentioning
confidence: 99%
“…S4.2). Over this period, beam trawl pressure has been higher in the eastern than western North Sea (Engelhard et al ., ) and has likely impacted not only adult skates but also egg‐laying and nursery grounds in coastal zones and outer estuaries (Frid et al ., ; Ellis et al ., ; Kinney & Simpfendorfer, ; Fock et al ., ). Our results show that, until the 1960s, the overall skate distribution coincided with that of thornback ray, thought to be the historically dominant species.…”
How have North Sea skate and shark assemblages changed since the early 20th century when bottom trawling became widespread, whilst their environment became increasingly impacted by fishing, climate change, habitat degradation and other anthropogenic pressures? This article examines long-term changes in the distribution and occurrence of the elasmobranch assemblage of the southern North Sea, based on extensive historical time series of fishery-independent survey data. In general, larger species (thornback ray, tope, spurdog) exhibited long-term declines, and the largest (common skate complex) became locally extirpated (as did angelshark). Smaller species increased (spotted and starry ray, lesser-spotted dogfish) as did smooth-hound, likely benefiting from greater resilience to fishing and/or climate change. This indicates a fundamental shift from historical dominance of larger, commercially valuable species to current prevalence of smaller, more productive species often of low commercial value. In recent years, however, some trends have reversed, with the (cold-water associated) starry ray now declining and thornback ray increasing. This shift may be attributed to (i) fishing, including mechanised beam trawling introduced in the 1960s-1970s, and historical target fisheries for elasmobranchs; (ii) climate change, currently favouring warm-water above cold-water species; and (iii) habitat loss, including potential degradation of coastal and outer estuarine nursery habitats. The same anthropogenic pressures, here documented to have impacted North Sea elasmobranchs over the past century, are likewise impacting shelf seas worldwide and may increase in the future; therefore, parallel changes in elasmobranch communities in other regions are to be expected.
“…Given the huge amount of surface area designated to offshore wind farms, marine spatial planning could support the conservation of demersal fish by excluding fishing in wind farms, which may provide important habitats for sensitive and threatened fish species e.g. elasmobranchs (Fock et al, 2014) or large gadoids (Reubens et al, 2014). It should be noted, however that offshore wind parks might not cover all relevant consistent core areas as wind parks cluster in the southern North Sea.…”
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