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Abstract

In March 2006, a 360 km(2) no-take zone (NTZ) was established north of Gotland in the central Baltic Sea, with the purpose to scientifically evaluate the effects of a fishing ban on flatfish populations. A monitoring programme was set up to study the populations in the NTZ and in a reference area east of Gotland where the fishing pressure was high. The programme included fishing with multimesh survey nets, modelling of potential larval export and estimation of fish consumption by large marine predators. Overall, the results showed a clear positive effect of the NTZ on turbot Scophthalmus maximus, with higher densities in the closed area compared with the fished area and also higher densities after closure compared with before. The NTZ also had older individuals and a more even sex ratio. This, in combination with a high potential for larval export from the NTZ to Gotland, shows that the marine reserve may be important for maintaining a viable S. maximus stock at Gotland. Also, for flounder Platichthys flesus, the densities were higher in the NTZ compared to the reference area and there was a net larval export to the fished area. For both species, density-dependent growth was evident, with a lower length at age in the closed area. Potential predation by grey seal Halichoerus grypus and great cormorant Phalacrocorax carbo sinesis on flatfishes, that could hamper the evaluation of the marine reserve, was also addressed. Taken together, the results show that there are clear benefits of the fishing ban for both flatfish species within the NTZ, while the net effects on fisheries are difficult to quantify.

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... Additionally, OWFs may also fulfill a similar role as marine protected areas (MPAs) for certain (target) species, as these concession areas are often closed to any commercial fishing activities and can as such be considered as no-take zones (Steins et al. 2021). No-take zones can protect fish species, especially those that are targeted by fisheries, and enhance fish biomass, which might even lead to a spillover in nearby fishing areas (Langhamer 2012;Florin et al. 2013). Such spillover effects, resulting from the combined artificial reef and refuge effects, have been predicted through modelling approaches (Raoux et al. 2017;Halouani et al. 2020), but in-situ studies were not able to confirm this yet. ...
... As commercial fishing activities within OWFs are often prohibited, they can be considered as no-take zones, similar to marine protected areas (MPAs) (Ashley et al. 2014). Previous studies have reported an increase in fish size, abundance, and total biomass within MPAs compared to adjacent fished areas (Di Franco et al. 2009;Florin et al. 2013;Guidetti et al. 2014;Félix-Hackradt et al. 2018). Our study revealed that there is a higher number of plaice present within the C-Power wind farm in between the turbines and that fish within the Belwind wind farm are larger, which indicates the existence of a refuge effect. ...
... In undisturbed populations, this results in a dominance of male individuals among smaller individuals and a dominance of females among larger individuals, with an even sex ratio for the total population. A higher catchability of larger (and thus more likely female) individuals in fished areas can lead to a decrease in fish size and a higher proportion of males (van Walraven et al. 2010;Florin et al. 2013). The increased female-to-male ratio of plaice found within Belwind might therefore be a consequence of the cessation of fishing activities. ...
Book
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This report, targeting marine scientists, marine managers and policy makers, and offshore wind farm developers, presents an overview of the scientific findings of the Belgian offshore wind farm environmental monitoring programme (WinMon.BE), based on data collected up to and including 2022.
... Påverkan på fisk från fiske kan delas in i direkta effekter genom uttag av specifika arter inklusive bifångade arter, samt indirekta effekter till följd av ändrade födovävsinteraktioner inklusive trofiska kaskader och/eller fysisk påverkan från redskap på de habitat som fisken lever i (Airoldi & Beck 2007). Den direkta dödlighet som fisket utsätter fisken för minskar mängden och medelstorleken av målarterna (Edgren 2005;Florin et al. 2013;. Exempel på indirekta effekter av fiske är; förändringar i enskilda arters livshistoria som ålder vid könsmognad till följd av selektivt fiske Kokkonen et al. 2015); förändringar i trofisk reglering som leder till trofiska kaskader inom och mellan system (Österblom et al. 2007;Eriksson et al. 2011;Baden et al. 2012;Casini et al. 2012;Östman et al. 2016) och fysisk påverkan på livsmiljöer från fiskeredskap (Hiddink et al. 2006). ...
... Trots fiskets välkända inverkan på kustnära rovfiskbestånd i Östersjön finns det bara några få studier där sambandet mellan uttag av fisk och beståndsstatus belagts. Exempel inkluderar positiva effekter av fiskefria områden för gädda, piggvar, skrubbskädda och abborre (Edgren 2005;Florin et al. 2013;Bergström et al. 2016c. I Estland påvisades en kollaps av kustfiskbestånden på grund av en kraftig ökning av antalet fiskare och fiskeansträngning efter Sovjetunionens fall år 1991 (Vetemaa et al. 2006). ...
... Unga livsstadier av olika plattfiskar nyttjar kusten som uppväxtområde, och kan påverkas negativt under perioder med höga vattentemperaturer under sensommaren (Vinagre et al. 2013;Lavergne et al. 2015). Förekomsten av vuxen skrubbskädda gynnas dock något av ökande vattentemperaturer (Florin et al. 2013;Rau et al. 2019). Kortsiktiga förändringar i vattentemperatur, orsakade av väderförhållanden och strömmar, påverkar också kustfiskens aktivitet och därmed hur de nyttjar olika delar av kusten. ...
Technical Report
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The purpose of this report is to describe the current state of knowledge of the most important factors influencing fish in Swedish marine waters in preparation for the update of the program of measures in 2021 within the Swedish implementation of the Marine Strategy Framework Directive (MSFD). The objective of the MSFD is to achieve or maintain good environmental status in the marine environments. For ecosystem components such as fish where the status is poor, an analysis of the key impacting pressures can contribute with knowledge to support management in directing and prioritizing measures required to achieve the goals. This review is divided into the two Swedish assessment areas of the MSFD, the North Sea and the Baltic Sea, and makes a division into coast and open sea in terms of describing the evidence for pressures affecting the fish fauna. The report presents literature support available during the autumn 2019 for the impact of pressures on fish from fishing, climate, eutrophication, habitat loss and food-web interactions. In addition, the significance of other pressures for which knowledge is more limited such as pollutants, pharmaceutical residues, marine litter including micro plastics, underwater noise, vitamin deficiency, as well as parasites and diseases are presented in short. A qualitative synthesis of the results shows that several pressures are likely to have a major impact on fish in the coastal and offshore ecosystems both in the Baltic Sea and in the North Sea. These pressures are a combination of direct and indirect human impact, as well as of altered food-web interactions. Direct impact from fishing on target and by-catch species is important in all management areas and habitats. The number of significantly influencing factors appears somewhat lower in the North Sea (especially in the open sea), compared to the Baltic Sea. However, there also seems to be less information on other impacts in the North Sea, where fishing has been the dominant pressure for a long period. Climate, eutrophication and habitat loss are significant pressures for the status of fish in both administrative areas. However, there is a general lack of knowledge about the importance of climate on the status of stocks in the North Sea, as well as the importance of food-web interactions in all areas and habitats, including how increasing populations of seals and cormorants interact with fish. This report concludes that a quantitative estimate of the relative importance of different pressures for fish would be desirable, including studies of the cumulative effects of several pressures that act simultaneously. Cumulative effects are poorly understood and studied, but are likely significant for the development of the fish populations and fish communities in our marine waters. Given the wide plethora of potentially impacting pressures, a more precautionary and ecosystem based approach to management is advocated in the current and future management of fish stocks, populations and communities in Swedish marine waters.
... Partially or seasonally closed areas, e.g., during spawning when fish aggregate at predictable locations and times, are common in the extensive fisheries management schemes of northern Europe (van Overzee & Rijnsdorp 2015, Eero et al. 2019, while NTZs are not. There is a widespread notion that NTZs are not suitable for temperate waters since many fishes are more mobile and have greater dispersal ranges than their tropical counterparts (Laurel & Bradbury 2006;Florin et al. 2013;Breen et al. 2015). Laurel and Bradbury (2006) therefore highlighted the need to scale up NTZs in temperate waters and not use tropical NTZs as direct scalar templates in temperate regions. ...
... The implementation of NTZs could therefore be a valuable management strategy to increase populations of declining coastal and offshore species and protect the habitats they rely on. Studies on commercially important flatfish in the Baltic Sea and lobsters and cod in the North Atlantic and Skagerrak have found positive effects of NTZs on density and sizes of targeted species, suggesting that implementing NTZs in Northern Europe may be a successful management strategy (Florin et al. 2013;Moland et al. 2013;Howarth et al. 2017). ...
... Considering the short time frame of the closure, the increase was surprisingly large. A similar rapid positive effect within five years of closure has been found in other studies, the majority of them from the tropics (e.g., Roberts et al. 2001;Galal et al. 2002;Denny et al. 2004), although examples from temperate regions exist (e.g., Florin et al. 2013, Moland et al. 2013. Several meta-analyses have also found that the higher average values of density, biomass, organism size, and diversity inside reserves (relative to controls) plateaued within a few years (Halpern & Warner 2002;Halpern 2003;Babcock et al. 2010). ...
Article
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Areas closed to fishing year-round (no-take zones, NTZs) or during spawning time (spawning closures) are used as a management tool to increase declining fish populations. We evaluated the effects of a 147 km2 NTZ and a 3980 km2 spawning closure on whitefish populations in the northern Baltic Sea, and also accounted for fish consumption by seals and cormorants. Fish monitoring with multimesh gillnets in 2011–2016 showed a significant increase in catch per unit effort (CPUE) of mature whitefish (> 30 cm) both in the spawning closure and the NTZ compared with the reference area open to fishing. The rate of increase was significantly higher in the NTZ than in the spawning closure. Our results suggest that NTZs may strengthen coastal fish populations in temperate regions and that also seasonal closures under a critical period of the life cycle may benefit the populations.
... Denna metod har också använts i svenska vatten (Thoresson, 1996), i övervakning av bl.a. sik, abborre och skrubbskädda (t ex Svärdson, 1961;Neuman, 1974, Florin et al., 2013. ...
... För att utvärdera effekten av lekfredningsområdet vid Gotska sandön beräknade Florin et al. (2013) Variationen i total dödlighet mellan de provfiskade områdena kan bero på flera olika faktorer och variation i lokala förutsättningar. I flera fall kan yrkes-och fritidsfisket antas vara en bidragande faktor, men även predation från rovfisk, säl och skarv kan ha en avgörande roll (Östman et al, 2012;Veneranta et al., 2020 ...
... Skrubbskäddan runt Gotland är ett annat exempel på hur tillväxtmodeller kan nyansera skillnader mellan olika områden. Tillväxthastigheten hos skrubbskädda beräknades för fredningsområdet vid Gotska sandön, referensområdet vid Herrvik, östra Gotland och Hoburgs bank.Florin et al. (2013) har tidigare visat att skrubbskäddans längd-vid-ålder var lägre i fredningsområdet vid Gotska sandön jämfört med referensområdet vid Herrvik. Även tillväxthastigheten var något lägre för hanar men lika för honor vid Gotska sandön jämfört med tillväxthastigheten vid Herrvik (Figur 15). Vid den mer sydligt belägna lokalen vid Hoburgs bank ...
Technical Report
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Summary Fish is an important indicator in monitoring and assessment of Swedish environmental goals and international directives and agreements. Several indicators describing recruitment, growth and age structure are based on age determination of fish. Age determination is done by reading growth zones on different hard structures from fish, e.g. otoliths, operculum bones, wing bones and scales. When the fish grows changes in its environment are also reflected in fish's hard structures. Age samples of fish are taken in many ongoing monitoring programs, and at SLU there are also large archives of age samples from many older surveys. In this report, we evaluate how age determination and other analyses of hard structures in fish might complement and strengthen knowledge about the structure and function of fish populations and fish communities in environmental monitoring in Swedish freshwaters and along the Baltic coast. Different types of age-based indicators are needed in assessment according to the Water Framework Directive, the Marine Strategies Framework Directive, the Species and Habitats Directive and as a basis for ecosystem-based fisheries management. It deals with different metrics of age structure, recruitment, growth and mortality, all of them calculated from aged fish. We describe collected age samples from test-fished coastal areas and lakes, and give both published and new examples of using age data in environmental and fisheries management. We also give examples of how analyses based on the shape and chemical composition of otoliths can be used. The recruitment of fish varies more or less between years, depending on natural conditions and human impact. Recruitment indices based on fish age provide more specific information than uncertain interpretation based on fish size alone. We show variation in recruitment index and relative year-class strength for several fish species in both smaller and larger lakes and along the coast. Environmental changes also affect fish growth. We give examples of age-based analyses of growth, for individuals and stocks, with and without use of growth models. Knowledge of survival and mortality is needed to understand what affects the development of fish stocks, and is therefore an important basis for ecosystem-based management. We provide several new examples of how mortality can be estimated based on ageing for some coastal fish species that are of interest for commercial and recreational fishing, and on how fishing mortality is used in new stock models for vendace in Lake Vänern and the Gulf of Bothnia. We also show comparisons between age and length structure, illustrating that fish age cannot be correctly estimated from its length. New and previously collected age samples are stored in SLU's biological archive. The samples can be used for more analyses than was originally planned when collecting the samples within environmental monitoring and other surveys. We show examples of how collected age samples can be used to identify different stocks of fish. There are different methods based on the shape of otoliths, chemical composition of otoliths and scales, and genetic analysis of scales.
... Moreover, juvenile flatfish species utilising coastal growth areas can be impacted negatively during periods of higher water temperatures, especially as temperature maximums in late summer coincide with these groups' coastal habitat use (Vinagre et al. 2013;Lavergne et al. 2015). The abundance of adult flounder is, however, somewhat favoured by increasing water temperatures (Florin et al. 2013;HELCOM 2017a). ...
... Other species are to some extent favoured by moderate levels of eutrophication. For example, the abundance of adult flounder is higher under moderate eutrophication in areas with low fishing pressure (Olsson et al. 2012;Florin et al. 2013). However, in more shallow coastal areas, increased presence of ephemeral macroalgae, as typically seen with eutrophication, reduces the suitability of nursery habitats for flounder and a variety of other species (Wennhage & Pihl1994;Carl et al. 2008;Jokinen et al. 2015;Kraufvelin et al. 2018), as might also be the effect of lowered water transparency . ...
... Fishing has potentially strong effects on recipient populations and communities. This is mainly manifested as direct mortality reducing the abundance and mean size of targeted species (Edgren 2005;Florin et al. 2013;Bergström et al. 2016c). In addition , the indirect effects of fishing are diverse and vary from changes in individual species life-history traits caused by fisheries induced selection (Cardinale et al. 2009;Kokkonen et al. 2015), changes in trophic regulation leading to trophic cascades within and across systems (Österblom et al. 2007;Eriksson et al. 2011;Baden et al. 2012;Casini et al. 2012), and physical destruction of habitats by fishing gear (Hiddink et al. 2006). ...
Technical Report
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Coastal fish, the fish assemblages in relatively near-shore and shallow (< 20 m depth) coastal areas, in the Baltic Sea harbour a mixture of species with marine and freshwater origins. Typical species are perch, pikeperch, pike, roach and breams, which are of freshwater origin and confined to coastal areas, as well as marine species like flounder, cod and herring, which often have seasonal migrations between nearshore and outer sea areas. Coastal fish populations and communities provide important ecosystem services, contributing to ecosystem functioning and high socio-economic and cultural values. They represent key elements for assessing environmental status in relation to environmental objectives within the Baltic Sea Action Plan (BSAP) and the Marine Strategy Framework Directive (MSFD). The main aim of this report is to provide a comprehensive assessment of the status of coastal fish in the Baltic Sea during 2011-2016, in support of the second holistic assessment of HELCOM (HOLAS II). The results are included in summary in the State of the Baltic Sea report. The report contains the latest status assessment of coastal fish in the Baltic Sea using two Baltic-wide CORE indicators and an agreed assessment approach (Chapter 3). The report also includes a review of major pressures acting on coastal fish communities (Chapter 2), and of potential measures to restore and support coastal fish communities in the Baltic Sea (Chapter 4). The report ends with future recommendations for continued work on coastal fish monitoring and assessment in the Baltic Sea in relation to the BSAP and MSFD (Chapter 5). The status assessments presented in this report includes data from Finland, Estonia, Latvia, Lithuania, Poland, Denmark and Sweden. Experts from Russia and Germany have also participated in the HELCOM work on coastal fish during recent years, but data from these countries are not included in the current assessment. Status is assessed based on the two HECLOM core indicators ‘Abundance of key species’ and ‘Abundance of key functional groups’, of which the latter is composed of a component assessing the abundance of piscivores and one on the abundance of Cyprinids/mesopredators. The results show that the status of the coastal fish communities varies between areas, regions and indicators, but the general status based on the two core indicators appears weak. Only approximately half of the assessed areas and assessment units are classified as being in good status. The more northern areas, where perch is used as the key species, are more often assessed to be in good status than more southern areas, where flounder is recognised as the key species. For the two functional group indicators, the status of piscivores follows a similar pattern of the key species indicator, with relatively better status in more northern areas. The other important functional group, cyprinids, shows insufficient status also in more north-eastern areas of the Baltic Sea as a result of too high abundances. The current monitoring network for coastal fish is rather extensive, but does still only support an assessment in half or less than half of the 42 listed assessment units for coastal fish in the Baltic Sea. The confidence of the assessment is moderate to low, depending on area and indicator, mainly as a result of short time-series, poor spatial representation, and data quality issues. The review of pressures acting on coastal fish communities show that a multitude of natural and human-induced pressures potentially affect coastal fish communities simultaneously. These include for example fishing, habitat exploitation, climate change, eutrophication and natural interactions within the coastal food-web. Whereas a few pressures are strong and often explain a large proportion of the variation in fish abundance and distribution, the effects of others can only be observed locally or under certain conditions and vary across areas and among communities. The potential for generalizations across areas is hence limited, and evaluations of which pressure is of key importance should be undertaken for each individual case separately considering the ambient local conditions in each area together with the range of potential human induced pressures. As a result, measures to restore and protect coastal fish communities should also be developed with a local perspective, and different measures might be relevant in different geographic areas. In general, however, scientific evidence on the effectiveness of different measures is poor, as only few thorough evaluations of implemented measures have been undertaken in the Baltic Sea. The few measures that have been scientifically evaluated with proven effects includes actions aimed at reducing the mortality of fish (e.g. no take areas). There is also partial support for temporary fishing closures and gear and catch restrictions. Among measures that aim at improving the production of fish, habitat protection and restoration have proven to be effective. For many other potential measures there is a general lack of scientific support, including biomanipulation, nutrient and substance abatement, as well as stocking of hatchery-reared fish. The assessment results and reviews presented in this report show that coastal fish assessments and monitoring in the Baltic Sea have taken noteworthy steps forward since the last thematic assessment. For example, Baltic-wide CORE indicators on coastal fish have been agreed on, as well as a regionally agreed concept for assessing the status of coastal fish communities. Knowledge has improved on the key pressures impacting on coastal fish communities, and on measures that are potentially most effective for supporting and restoring coastal fish communities. In spite of this, there are still several knowledge gaps and development needs, which should be considered in the future. There is a need to safeguard existing monitoring programs and to initiate new monitoring programs for coastal fish in geographic areas that are currently poorly covered or not possible to assess at all. There is also a need to continue harmonizing assessment approaches to enable comparisons across monitoring programs and data sources, and to further develop common indicators and assessment methods. This concerns the further evaluation and development of current indicators, as well as the development of new generic indicators, focusing on aspects of size-structure in the assessed fish communities. Finally, it is clear that initiatives to strengthen the evaluation measures must be undertaken. It is recommended that the results presented in this report should be used as the basis for following up on the objectives of the BSAP and MSFD, as well as for the development of national management plans and coastal fish assessments in the Baltic Sea.
... att de finns både stora och små individer, kan vara viktigt för ett bestånds möjligheter att klara av år med dålig rekrytering och anses också ha positiva effekter på hela ekosystemet (Froese et al. 2008;Östman et al. 2016). Ett för högt fisketryck, eller hög naturlig dödlighet, i ett bestånd leder till färre äldre individer (Froese et al. 2008;Bergström et al. 2007;Florin et al. 2013), i andra fall kan den individuella tillväxten ha stor betydelse för beståndets storleksstruktur (Svedäng & Hornborg 3.2 Mål baserade på beståndsstorlek 3.3 Mål baserade på storleks/åldersstruktur 2015). Eftersom fiske nästan alltid är storleksselektivt kan intensivt fiske leda till en skev storleksstruktur (Punt et al. 2013). ...
... Ett högt fisketryck, eller annan hög dödlighet, i en population kan leda till en hög andel små individer (Bergström et al. 2007, Florin et al. 2013. Speciellt kan det i bestånd där fångsten är storleksselektiv, leda till en skev storleksstruktur i populationen. ...
... I de fall tidsserier saknas, kan istället data från andra områden användas, om det kan anses att förutsättningarna i övrigt är tillräckligt lika. Förekomst av data från ofiskade populationer är speciellt värdefullt, eftersom dessa data kan ge information om storleksstruktur i en ofiskad population (Edgren 2005, Bergström et al. 2007, Florin et al. 2013. Det finns flera olika alternativ för att kvantifiera storleksstrukturen i en population: 1. Medellängd av alla fångade individer i en population (mL=ΣL/n) är det enklaste måttet, där ΣL är summan av alla fiskars längder och n är antalet fiskar i en slumpvis provtagning. ...
Technical Report
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Fish and shellfish stocks with distributions mainly restricted within Swedish national waters are also mainly governed nationally and to some extent by regional or local authorities and organizations. Such stocks are often, in contrast to species that are subject to international exploitation and management, utilized by several different stakeholders (e.g. commercial and recreational fisheries). The needs and long-term management objectives of these stakeholders may sometimes differ and in the worst cases be in direct conflict with each other (e.g. large yield vs. large individuals). There is often limited data available for these stocks, and consequently they often lack quan-titative management objectives, resulting in a less effective management. The aim of this report is to provide an overview of available management targets and associated methods and instruments suitable for assessing if the exploitation of nationally man-aged fish and shellfish stocks are sustainable in the long term. There are three broad categories of quantitative management targets: 1) Targets to achieving long-term sus-tainable yield, which require detailed data from many different sources. 2) Targets of biomass or abundance index, or a ratio between catch and abundance/biomass index, which requires reliable monitoring, catch or effort data. 3) Targets of the demo-graphic structure of a stock or of the life-history characters of a stock, to achieve a “natural like” or “desirable” stock structure which requires data of trait distributions (e.g. size, age, maturity) in stocks. All three categories have their merits and draw-backs. For example, sustainable yield and abundance-index goals do not consider size-structure, and vice versa, and different objectives require different types of input data. In addition we therefore review which objectives may be suitable for different types of nationally managed fish and shellfish stocks. At the current stage data are generally too limited to propose specific targets for most stocks that can be consid-ered for national management. Rather, we stress the importance of using several dif-ferent management targets or indicators of exploitation instead of relying on a single target/indicator to facilitate sustainable use of aquatic resources taking into account the demands of different stakeholders. In addition, there is no clear definition of what a local stock is and when national and/or local management should be enforced. Therefore it is important that management objectives are set such that they can reflect nationally or locally enforced measures.
... A 360 km 2 NTZ was established in 2006 around Gotska Sandön (Sweden, central Baltic Sea) as an experimental management measure to rebuild depleted flatfish stocks (Florin et al., 2013). A comprehensive monitoring program that included an estimation of larval export and consumption by large marine predators showed positive effects of the NTZ on two flatfish populations. ...
... Furthermore, the model suggested net larval export from both species. The only downside was a lower growth rate of both species inside the NTZ, possibly due to density-dependent factors (Florin et al., 2013). ...
Article
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As a response to increasing human pressures on marine ecosystems, the legislation aimed at improving the conservation and management of marine coastal areas in European and Contiguous Seas (ECS) underwent crucial advances. ECS, however, still remain largely affected by increasing threats leading to biodiversity loss. Here, by using emblematic case studies and expert knowledge, we review current conservation tools, comparing their application in different areas to assess their effectiveness, potential for synergies, and contradictions. Despite regional differences in their application, the existing legislative frameworks have the potential to regulate human activities and to protect marine biodiversity. However, four challenges remain to be addressed to fully achieve environmental policy goals: (1) Lack of shared vision representing a limitation in transboundary collaboration. Although all EU countries are committed to fulfil EU Directives and other binding international legislative acts, a remarkable heterogeneity exists among countries in the compliance with the common legislation on conservation and in their degree of implementation. (2) Lack of systematic procedures for the selection of protected marine sites. Regional and national approaches in designating Natura 2000 sites and nationally designated marine protected areas (MPAs) reflect varying conservation targets and importance of conservation issues in political agendas. (3) Lack of coherent ecological networks. Natura 2000 sites and other MPAs are still far from reaching the status of effective networks in all considered case studies. (4) Hotspot of conflicts with private economic interests prevailing over conservation aims. Recommendations are given to overcome the fragmented approach still characterizing the conservation and management of coastal marine environments. Holistic, integrated, ecosystem-based, cross-cutting approaches can avoid conflicts among institutions so as to provide effective and timely solutions to current and future challenges concerning the conservation and management of marine ecosystems and associated goods and services.
... The postban biomass increase in the GCAST had already been observed as early as 1994 [36], although supported by a much smaller dataset and a weaker statistical design than in the present work. Similar evidence of biomass increase was recorded in a few other trawl exclusion areas in the Mediterranean [52], the Atlantic Ocean [24,[81][82][83][84], and the Pacific Ocean [73], even though only a few studies [69,85] have considered the effect of protection on the whole trawlable assemblage rather than on a few target species. ...
... It is not unlikely that not only fishing pressure, but possibly also unknown site-specific variables or density-dependent effects may have affected the demographic structure of the fished populations. A complex interaction between resource availability and densitydependence [81,96] may have played a role in the growth performance of some species in our study areas, as well as the pressure exerted by artisanal fishermen targeting a small number of benthic and bentho-pelagic species-especially red mullet, pandora and cephalopods-using size-selective fishing gear [35,97]. ...
Article
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This paper reports the results of a 15-year trawl ban imposed in 1990 in the Gulf of Castellammare (GCAST: NW Sicily, central Mediterranean Sea) and its effects on the biomass and size structure of demersal finfish and shellfish and on the proportion of different commercial categories of fish. Data were collected by experimental trawl surveys conducted in the GCAST and in two trawled areas before and after 1990. The biomass of the total assemblage and of a number of selected species was significantly higher in the GCAST after the ban. Highly commercial species had the largest increase in the same gulf after the ban, particularly at the depths used by artisanal fishermen. The results from size-based indicators were not as clear-cut as those from biomass though. Although the length frequency distributions obtained in the GCAST were significantly different from the other gulfs, in several cases, the values of the size indicators were higher in the trawled gulfs. Our results suggest that, at the temporal and spatial scale adopted, trawl bans may drive full biomass recovery but only partial size structure recovery of the fish populations subject to trawl exclusion, at least in the Mediterranean. The trawl ban in the Gulf of Castellammare provides an example of an effective ecosystem-based fisheries management tool that offers the potential for fish stock rebuilding and for the economic sustainability of artisanal, small-scale fisheries.
... As no fisheries activities are allowed within any of the Belgian wind farm concessions due to safety restrictions, it is likely that the soft sedi-ments in between the turbines serve as refuge areas for plaice, at least under specific conditions. Fisheries exclusion zones are widely used in nature conservation and fisheries management plans with the aim of enhancing biodiversity and biomass of certain key species, preferably leading to spillover effects in the surrounding areas (Fenberg et al., 2012;Florin et al., 2013;Abecasis et al., 2014). The location of such fisheries exclusion zones is mostly based on the high intrinsic natural value or the presence of certain key species, which is not really the case for OWFs. ...
... As shown in our study, the inclusion of different spatial scales improves our understanding of how OWFs influence species distribution patterns, as refuge effects might be masked by an attraction towards the SPL-habitat . Finally, most OWF-studies focused on fish abundances, which are highly variable in space and time, while refuge effects may be more easily identified when looking at other fish life history or population parameters, such as age, fish length, and sex ratio (Miethe et al., 2010;Florin et al., 2013). For example, Di Franco et al. (2009) showed that the observed increase in biomass for many target species within a protected area in the Mediterranean was mainly due to an increase in fish size rather than fish abundance. ...
Article
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We investigated how the distribution of plaice Pleuronectes platessa, a typical soft-sediment fish species, has been affected by the introduction of hard substrate [turbines and scour protection layer (SPL)] at both turbine and wind farm scale in two Belgian offshore wind farms (OWFs). Diving transects (40 m) at 11 monopiles revealed four times higher plaice abundances on the sandy patches of the SPL (average radius 16.5 m) compared to the surrounding sand. We suggest that the configuration of the SPL, i.e. an open rock field, offering increased food and shelter opportunities, with sandy patches in between, facilitating the natural burrowing behaviour of plaice, forms the basis for the increased plaice abundances at the turbine scale. At the wind farm scale, beam trawl catches in between the turbines and in reference zones revealed significantly increased plaice abundances in one OWF, which suggests that wind farms can act as refuge areas for plaice, at least under specific conditions. Differences in environmental conditions, turbine foundation type, and surrounding fishing pressure may explain the equivocal findings between both OWFs, whereas low statistical power could have hampered the detection of general refuge effects. Next to the integration of different spatial scales (turbine/wind farm) within one study, longer-term monitoring and including extra life history parameters (e.g. length and sex ratio) might enhance the detectability of potential refuge effects.
... In cases where maps on dispersal were available, but no distances were stated, we measured approximate maximum distances for larval dispersal using the Google Earth geographical information system, based on models and maps from Hinrichsen et al. (2017b) and Florin et al. (2013), which included maps for Atlantic cod (Gadus morhua), European flounder (Platichtys flesus) and turbot (Scophthalmus maximus). ...
... Information on passive dispersal and important areas to protect has mainly been obtained from modelling studies (Corell et al. 2012;Moksnes et al. 2015;Jonsson et al. 2016bJonsson et al. , 2020. Modelling studies have also been done separately for herring, cod, sprat, European flounder and turbot in order to identify pathways of larval dispersal and nursery grounds (Florin et al. 2013;Hinrichsen et al. 2012aHinrichsen et al. , b, 2017a. ...
Article
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Marine protected areas (MPAs) have become a key component of conservation and fisheries management to alleviate anthropogenic pressures. For MPA networks to efficiently promote persistence and recovery of populations, ecological connectivity, i.e. dispersal and movement of organisms and material across ecosystems, needs to be taken into account. To improve the ecological coherence of MPA networks, there is hence a need to evaluate the connectivity of species spreading through active migration and passive dispersal. We reviewed knowledge on ecological connectivity in the Baltic Sea, Kattegat and Skagerrak in the northeast Atlantic and present available information on species-specific dispersal and migration distances. Studies on genetic connectivity are summarised and discussed in relation to dispersal-based analyses. Threats to ecological connectivity, limiting dispersal of populations and lowering the resilience to environmental change, were examined. Additionally, a review of studies evaluating the ecological coherence of MPA networks in the Baltic Sea, Kattegat and Skagerrak was performed, and suggestions for future evaluations to meet management needs are presented.
... Overexploitation is a major threat to this species in parts of its range. Take of large females, or sex-ratio skewing (Florin et al. 2013), and exploitation of individuals on spawning sites contributes to the documented, large population declines observed in Turbot. This species has relatively low larval dispersal, strong spawning site fidelity, and limited adult migration; intrinsic characteristics that render this species to have a higher susceptibility to overfishing. ...
... The Skagerrak and Kattegat stock assessment could also be improved with the expansion of scientific surveys, collection of age and length data for fishes harvested, filling of gaps in Swedish landings data, and further studies on stock structure (ICES WGNSSK 2020). Fishing for this species is prohibited during the spawning season in the southern Baltic Sea and a Swedish marine reserve in the Baltic Sea proper also provides some refuge from fishing activity (Florin et al. 2013). Some of the aquaculture production in Europe has also been used to supplement wild populations in several localities in the Atlantic (do Prado et al. 2018). ...
Article
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The IUCN Red List of Threatened Species,Scophthalmus maximus, Turbot
... Overexploitation is a major threat to this species in parts of its range. Take of large females, or sex-ratio skewing (Florin et al. 2013), and exploitation of individuals on spawning sites contributes to the documented, large population declines observed in Turbot. This species has relatively low larval dispersal, strong spawning site fidelity, and limited adult migration; intrinsic characteristics that render this species to have a higher susceptibility to overfishing. ...
... The Skagerrak and Kattegat stock assessment could also be improved with the expansion of scientific surveys, collection of age and length data for fishes harvested, filling of gaps in Swedish landings data, and further studies on stock structure (ICES WGNSSK 2020). Fishing for this species is prohibited during the spawning season in the southern Baltic Sea and a Swedish marine reserve in the Baltic Sea proper also provides some refuge from fishing activity (Florin et al. 2013). Some of the aquaculture production in Europe has also been used to supplement wild populations in several localities in the Atlantic (do Prado et al. 2018). ...
... Furthermore, general increases in flatfish density have been observed around artificial structures in the North West Atlantic (Walton, 1982). The closure of fishing grounds, a general practice in OWFs, has had a positive impact on the egg production of turbot (Scophthalmus maximus) in the Baltic Sea (Florin et al., 2013). ...
... Due to their specific life history, flatfish have not been identified as having the potential to benefit from the establishment of marine-protected areas (Shipp, 2003). However, some studies showed that spatial restriction of fisheries or implementation of OWFs increase flatfish population size (Walton, 1982;Florin et al., 2013) whereas others reported a limited impact (e.g. Ashley et al., 2014). ...
Article
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Understanding the influence of man-made infrastructures on fish population dynamics is an important issue for fisheries management. This is particularly the case because of the steady proliferation of offshore wind farms (OWFs). Several flatfish species are likely to be affected because areas with OWFs in place or planned for show a spatial overlap with their spawning grounds. This study focuses on six commercially important flatfish species in the North Sea: common sole (Solea solea), European plaice (Pleuronectes platessa), turbot (Scophthalmus maximus), brill (Scophtalmus rhombus), European flounder (Platichthys flesus), and common dab (Limanda limanda). We used a particle-tracking model (Larvae&Co) coupled to a 3D hydrodynamic model to assess the effects of spatial overlap of OWFs with the species’ spawning grounds on the larval fluxes to known nursery grounds. An important overlap between planned areas of OWFs and flatfish spawning grounds was detected, with a resulting proportion of settlers originating from those areas varying from 2% to 16%. Our study suggests that European plaice, common dab, and brill could be the most affected flatfish species, yet with some important local disparities across the North Sea. Consequently, the study represents a first step to quantify the potential impact of OWFs on flatfish settlement, and hence on their population dynamics.
... solemdali), have been considered in only one study, focusing mainly on larval export from a no-take zone area in the northern 3.d. 28-2 (Florin et al., 2013). Thus, lack of studies focusing on larval dispersal of Baltic flounder represents a gap in knowledge of flounder ecology in the Baltic Sea, a mechanism potentially influencing recruitment to the adult stock and explaining diversity in stock structure. ...
... The results are in agreement with those of Corell et al. (2012) where 80% of the total variation in dispersal distance for invertebrate-and fish (Gobiidae) larvae in the Baltic Sea was explained by larval depth distribution, together with duration of the pelagic larval stage. Moreover, the results coincide with those in Florin et al. (2013) in which modelled Baltic flounder larval drift patterns were averaged over two depth intervals, 0-2 m and 12-14 m, showing both larval retention in the release area off the coast of Gotland (3.d. 28-2) and extensive dispersal to offshore areas, i.e. in agreement with endpoints of drifters according to the respective drifting-depth in our study. ...
Article
For flatfishes, transportation of larvae to nursery areas is regarded a key mechanism for recruitment, with adaptations in larval behaviour to reach a suitable habitat. Here we model different possibilities of larval drifting of coastal spawning Baltic flounder Platichthys solemdali (recently identified as a species from European flounder P. flesus) to reveal opportunities for local retention vs large-scale dispersal to ensure settling in coastal nursery areas. Drifting depth, duration of drifting and effects of year and time during season were modelled using 1) a high-resolution local dispersal model, and 2) a large-scale connectivity database. The outcome revealed drifting depth as a major factor affecting larval dispersal. Drift at 10-22 m depth involved retention along the coast with the majority of larvae (≥94% or 69-93% according to 1 and 2, respectively) with end points ≤20 km from the coast enabling further successful migration to nursery habitats. Contrary, larval drift close to the surface resulted in advection with end points in the open sea (72-76%), i.e. loss of larvae, but with a small fraction (5-12%) displaying cross-basin connectivity. The results suggest, in agreement with depth distribution of spawning, a larval behaviour promoting drift in the lower part of the water mass, favouring retention close to coastal nursery areas. Obtained dispersal patterns may sustain both local recruitment but also connectivity with other areas, potentially explaining the low genetic diversity between areas for P. solemdali. Low inter-annual variability in dispersal patterns when drifting at 10-22 m depth suggests that larval drift is not a major bottleneck explaining recruitment variability in P. solemdali in the area. The study highlights the differences in life-history strategies of the species pair of flounder in the Baltic Sea; P. flesus spawning in the deep basins with extensive larval dispersal, and coastal spawning P. solemdali with, according to the model outcome, mainly local larval dispersal for sustaining a viable population, i.e. request for different management strategies.
... A 360 km 2 NTZ was established in 2006 around Gotska Sandön (Sweden, central Baltic Sea) as an experimental management measure to rebuild depleted flatfish stocks (Florin et al., 2013). A comprehensive monitoring program that included an estimation of larval export and consumption by large marine predators showed positive effects of the NTZ on two flatfish populations. ...
... Furthermore, the model suggested net larval export from both species. The only downside was a lower growth rate of both species inside the NTZ, possibly due to density-dependent factors (Florin et al., 2013). ...
Article
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As a response to increasing human pressures on marine ecosystems, the legislation aimed at improving the conservation and management of marine coastal areas in European and Contiguous Seas (ECS) underwent crucial advances. ECS, however, still remain largely affected by increasing threats leading to biodiversity loss. Here, by using emblematic case studies and expert knowledge, we review current conservation tools, comparing their application in different areas to assess their effectiveness, potential for synergies, and contradictions. Despite regional differences in their application, the existing legislative frameworks have the potential to regulate human activities and to protect marine biodiversity. However, four challenges remain to be addressed to fully achieve environmental policy goals: (1) Lack of shared vision representing a limitation in transboundary collaboration. Although all EU countries are committed to fulfil EU Directives and other binding international legislative acts, a remarkable heterogeneity exists among countries in the compliance with the common legislation on conservation and in their degree of implementation. (2) Lack of systematic procedures for the selection of protected marine sites. Regional and national approaches in designating Natura 2000 sites and nationally designated marine protected areas (MPAs) reflect varying conservation targets and importance of conservation issues in political agendas. (3) Lack of coherent ecological networks. Natura 2000 sites and other MPAs are still far from reaching the status of effective networks in all considered case studies. (4) Hotspot of conflicts with private economic interests prevailing over conservation aims. Recommendations are given to overcome the fragmented approach still characterizing the conservation and management of coastal marine environments. Holistic, integrated, ecosystem-based, cross-cutting approaches can avoid conflicts among institutions so as to provide effective and timely solutions to current and future challenges concerning the conservation and management of marine ecosystems and associated goods and services.
... A 360 km 2 NTZ was established in 2006 around Gotska Sandön (Sweden, central Baltic Sea) as an experimental management measure to rebuild depleted flatfish stocks (Florin et al., 2013). A comprehensive monitoring program that included an estimation of larval export and consumption by large marine predators showed positive effects of the NTZ on two flatfish populations. ...
... Furthermore, the model suggested net larval export from both species. The only downside was a lower growth rate of both species inside the NTZ, possibly due to density-dependent factors (Florin et al., 2013). ...
Article
Full-text available
As a response to increasing human pressures on marine ecosystems, the legislation aimed at improving the conservation and management of marine coastal areas in European and Contiguous Seas (ECS) underwent crucial advances. ECS, however, still remain largely affected by increasing threats leading to biodiversity loss. Here, by using emblematic case studies and expert knowledge, we review current conservation tools, comparing their application in different areas to assess their effectiveness, potential for synergies, and contradictions. Despite regional differences in their application, the existing legislative frameworks have the potential to regulate human activities and to protect marine biodiversity. However, four challenges remain to be addressed to fully achieve environmental policy goals: (1) Lack of shared vision representing a limitation in transboundary collaboration. Although all EU countries are committed to fulfil EU Directives and other binding international legislative acts, a remarkable heterogeneity exists among countries in the compliance with the common legislation on conservation and in their degree of implementation. (2) Lack of systematic procedures for the selection of protected marine sites. Regional and national approaches in designating Natura 2000 sites and nationally designated marine protected areas (MPAs) reflect varying conservation targets and importance of conservation issues in political agendas. (3) Lack of coherent ecological networks. Natura 2000 sites and other MPAs are still far from reaching the status of effective networks in all considered case studies. (4) Hotspot of conflicts with private economic interests prevailing over conservation aims. Recommendations are given to overcome the fragmented approach still characterizing the conservation and management of coastal marine environments. Holistic, integrated, ecosystem-based, cross-cutting approaches can avoid conflicts among institutions so as to provide effective and timely solutions to current and future challenges concerning the conservation and management of marine ecosystems and associated goods and services.
... A 360 km 2 NTZ was established in 2006 around Gotska Sandön (Sweden, central Baltic Sea) as an experimental management measure to rebuild depleted flatfish stocks (Florin et al., 2013). A comprehensive monitoring program that included an estimation of larval export and consumption by large marine predators showed positive effects of the NTZ on two flatfish populations. ...
... Furthermore, the model suggested net larval export from both species. The only downside was a lower growth rate of both species inside the NTZ, possibly due to density-dependent factors (Florin et al., 2013). ...
Article
Full-text available
As a response to increasing human pressures on marine ecosystems, the legislation aimed at improving the conservation and management of marine coastal areas in European and Contiguous Seas (ECS) underwent crucial advances. ECS, however, still remain largely affected by increasing threats leading to biodiversity loss. Here, by using emblematic case studies and expert knowledge, we review current conservation tools, comparing their application in different areas to assess their effectiveness, potential for synergies, and contradictions. Despite regional differences in their application, the existing legislative frameworks have the potential to regulate human activities and to protect marine biodiversity. However, four challenges remain to be addressed to fully achieve environmental policy goals: (1) Lack of shared vision representing a limitation in transboundary collaboration. Although all EU countries are committed to fulfil EU Directives and other binding international legislative acts, a remarkable heterogeneity exists among countries in the compliance with the common legislation on conservation and in their degree of implementation. (2) Lack of systematic procedures for the selection of protected marine sites. Regional and national approaches in designating Natura 2000 sites and nationally designated marine protected areas (MPAs) reflect varying conservation targets and importance of conservation issues in political agendas. (3) Lack of coherent ecological networks. Natura 2000 sites and other MPAs are still far from reaching the status of effective networks in all considered case studies. (4) Hotspot of conflicts with private economic interests prevailing over conservation aims. Recommendations are given to overcome the fragmented approach still characterizing the conservation and management of coastal marine environments. Holistic, integrated, ecosystem-based, cross-cutting approaches can avoid conflicts among institutions so as to provide effective and timely solutions to current and future challenges concerning the conservation and management of marine ecosystems and associated goods and services.
... Studier i Östersjön har dessutom visat att piggvar påverkades positivt när ett havsområde (Gotska Sandön, 360 km 2 ) fredades. Beståndstätheten ökade, det blev fler äldre individer och jämnare könskvot (hane/hona) efter att fredningen inrättades (Florin et al. 2013). ...
... Både piggvar och slätvar förekommer regelbundet i fångsterna i provfiskena, men ingen effekt på dessa arter av fredningsområdet kan utläsas ur analyserna. Piggvar har däremot en annan studie visats reagera positivt på införande av ett fredningsområde (360 km 2 ) med bland annat ökad täthet, detta efter endast fem års fredning (Florin et al. 2013). I Kattegatt har däremot inte piggvar och slätvar varit målarter för FFO, det vill säga utformningen av FFO har inte gjorts med dessa båda arters biologiska behov i fokus, en förutsättning som kan göra att det kan ta längre tid (> 5 år) innan effekter mätbara fås efter en fredning (Babcock et al. 2010). ...
Technical Report
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This report describes the ecological effects of fishing closures (no-take areas) in Swedish marine and coastal waters. In 2005 the Swedish Board of Fisheries (now the Swedish Agency for Marine and Water Management) was commissioned by the government to establish a number of areas where all fishing was prohibited and to evaluate the effects of these closures. Five such no-take areas were established in 2009-2011. The effects on fish populations, and in some cases also on other components of the ecosystem, were monitored until 2015. This report gives a summary of biological effects of these no-take areas, focusing on fish populations and ecosystems. When these five new fishing closures had been established in 2011, the total area of no-take areas in Swedish marine and coastal waters amounted to 1 200 km2. This corresponds to less than 1 % of the Swedish sea area, but two thirds of the total areal extent of no-take areas in Europe. Hence, the monitoring and evaluation of the Swedish areas makes an important contribution also to the general knowledge base regarding no-take areas for European fisheries management. The geographical areas and target species of the evaluation were: • European whitefish in the Bothnian Sea • Pikeperch, pike and perch in the Stockholm archipelago, central Baltic Sea • Cod in the Kattegat • European lobster and predatory fish in the Gothenburg archipelago, Skagerrak • Cod, turbot and plaice in the Swedish fjords of Skagerrak More detailed results for each of the study areas are given in supplementary reports, whereas overall results are synthesized here. Abundance and body size of target species increased in most of the no-take areas, as compared to nearby reference areas where fishing was continued. The results show that the earlier fishing pressure in the no-take areas had been large enough to influence both fish abundance and size structure. The responses in abundance and body size were seen both for populations that had been targeted primarily by commercial fisheries, such as cod in Kattegat, and for coastal species where recreational fisheries dominated the catches, for example whitefish in the Bothnian Sea, pikeperch in Stockholm archipelago and European lobster in the Gothenburg archipelago. Despite the relatively short evaluation period of 5 years, substantial positive effects on the populations were evident in four of the five no-take areas, illustrating the utility of no-take areas for strengthening vulnerable fish populations. In one area, Havstensfjorden in Skagerrak, no positive effects have so far been seen in the target species cod, plaice and turbot. This is most probably explained by previous recruitment overfishing on local populations, leading to slow recovery. In addition to the studies on target fish populations, effects on fish communities and benthic fauna were studied in some of the areas, showing changes also in these ecosystem components. These observations were likely due to a combination of direct effects of excluding fisheries on target and bycatch species, and indirect effects of the increase in large predatory fish and European lobster leading to increased predation on prey species. Thus, the studies suggest that no-take areas may contribute to re-establishment of ecosystem functions by increasing the abundances of large predators. Such changes in food web function may also counterbalance other processes, such as the increased production of fast-growing algae in eutrophicated areas, through trophic cascades. Another effect of no-take areas is the cessation of bottom trawling leading to improved conditions for benthic fauna sensitive to physical disturbance. In most cases, the introduction of the no-take areas has likely decreased the total fishing effort rather than displacing it to adjacent areas. In the Kattegat no-take area, however, the purpose was explicitly to displace an unselective coastal mixed bottom-trawl fishery targeting Norway lobster and flatfish to areas where the bycatches of mature cod were smaller. The mixed fishery has continued in the buffer zones and the open areas of Kattegat, and total catches of Norway lobster and flatfish have been maintained but with substantially less bycatches of adult cod than before the introduction of the measures. The report also reviews the general scientific knowledge base on no-take areas, including also experiences from previously studied no-take areas in Swedish waters. The effects observed in these other Swedish no-take areas are consistent with the ones reported here, showing increases in population sizes and size structures, and an increase in the reproduction potential. The results also generally agree with international studies in terms of the effects no-take areas on target species for fisheries. The Swedish examples generally lack specific empirical studies on ecosystem effects of the closures. However, knowledge on the effects of large predatory fish on ecosystem functioning, including their role in trophic cascades, is available from other research projects in Sweden. As the population density and body size of fish and lobsters increase, the reproduction potential also increases, which may generate positive effects also outside the closed areas through spillover. The magnitude of such spillover effects, through export of eggs and larvae and migration of adult fish, are however not easily estimated. Apart from spillover effects, there are also other potential benefits from no-take areas. By keeping a part of the fish populations protected from fishing, the risk for stock collapse due to otherwise inadequate management decreases, whereby the no-take areas may act as an insurance policy. No-take areas may also counteract genetic impoverishment due to selective fishing on large, fast-growing individuals, and may hence mitigate a decrease in fish productivity due to genetic effects, and may support biological variation and resilience against environmental change. In the present evaluation, the net effects were quantified for the Kattegat no-take area, showing a positive effect on the cod population in the Kattegat management area as a whole, while catches of other commercial species had not decreased. In a longer-term perspective, the recovery will likely provide increased opportunities for a cod fishery, as a substantial part of the population is found outside of the no-take area after the spawning period. No-take areas can, if they are adequately designed, give rise to positive population effects and may be a useful complement to other fisheries management instruments. In many cases, the desired results can potentially also be achieved by a combination of other measures, such as gear or catch restrictions in space and time. The experiences from the current evaluation show that no-take areas can be an important tool for fisheries management especially for mixed fisheries and local coastal fish populations, as well as in cases where there is a need to counteract adverse ecosystem effects of fishing. Marine protected areas where the protection of both fish and their habitats is combined may be an important instrument for ecosystem-based management. In this context, no-take areas are also needed as reference for marine environmental management, as well as for understanding of the effects of fishing on fish populations and ecosystems in relation to other pressures.
... Higher salinity improves reproduction and somatic growth of offshore spawning flounder (Nissling et al., 2002) while high population density may have negative effects on body growth. For example, Florin et al. (2013) found that length-at-age of European flounder was lower in a high density no-take zone compared to a fished area in SD 28, likely reflecting negative density dependent body growth. Thus, temporal variation in abiotic and biotic factors may affect the length distribution and spatial structure of European Flounder over time. ...
... Estimates of mortalities from cohorts are uncertain because the sampling effort has been variable between years, but using the age distributions from each years sample do not indicate higher mortality in SD 28 (Appendix Fig. A2). There are some indications that body growth in European flounder is density dependent (Florin et al., 2013) but if that can explain spatial variation in length distributions and life-history traits is currently unknown. We can here not pinpoint the mechanisms for the observed patterns but this spatial variation may be important to consider in the management of European flounder in the Baltic Sea. ...
Article
The spatial structure of fish species is important for stock identification and management. The European flounder (Platichthys flesus L.) shows morphological differences across the Baltic Sea Proper. However, it is not known whether flounders cluster into several distinct areas based on morphological characters, indicating discrete sub-populations, or whether they show continuous morphological variation along space indicating a more continuous population structure. Here, we study the spatial structure of body length and length-at-age distributions of the European flounder (Platichthys flesus L.) across the Baltic Sea Proper (International Council for the Exploration of the Sea (ICES) subdivisions 25–28) using high spatial resolution data (ICES rectangles) from fishery independent surveys 2008–2014. Our results are in agreement with genetic data suggesting a continuous gradient of decreasing body length from south-west to north-east. Further, we observed distance decay in the spatial synchrony of temporal changes in the length distributions, such that the temporal trends were correlated among adjacent ICES rectangles but independent across the whole study area. Length-at-age and maturity patterns that were calculated for each subdivision also showed a consistent spatial difference where SD 28 was significantly different from SD 25 and 26. Our results indicate that the European flounder in the Baltic Sea consists of several loosely defined sub-populations, which may warrant a reconsideration of assessment models, management targets and regulations across subdivisions.
... For these two species, genetic drift seems to override gene flow among discrete areas where spawning occurs, suggesting that specific management units can be identified. Coastal flounder was the only coastal species with no apparent genetic structure, likely a result from drift and mixture of larvae from spawning grounds to nursery and feeding grounds in coastal areas (Florin et al. 2013). ...
... The other offshore species (herring, plaice, turbot and three-spined stickleback) had low F ST and weak IBD, that is based on neutral genetic markers they were classified as having a single population in the Baltic Sea. The flatfishes, plaice and turbot, likely have high gene flow due to high mobility of larvae (Florin et al. 2013;Moksnes et al. 2014). Reiss et al. (2009) also found (in a review over whole NE Atlantic) little genetic differentiation in most flatfish species, despite evident homing behaviour. ...
Article
Full-text available
The spatial structure of species is important for their dynamics and evolution, but also for management and conservation. There are numerous ways of inferring spatial structures, and information from multiple methods is becoming more common to examine how different processes shape the spatial structures of species to improve fish management. Here, we investigate the spatial structure of a suite of Baltic Sea fish species based on the following: (i) spatial (presumably neutral) genetic differentiation, reviewed from the literature, and (ii) spatial synchrony in abundance changes from time series of fishery-independent surveys, which we currently find to be underused given the amount of data available. For each of these two methods, species were classified as having a distinct, continuous or no/weak spatial structure. In addition, based on each source of information, we estimated the spatial scale of management units for species. The results show that only among species confined to the coastal zone the two sources of information yielded a congruence of the spatial structure (displaying a continuous spatial structure). In contrast, offshore species show weak spatial genetic structure but stronger spatial structure of synchrony in abundance. Based on this, we suggest that population genetic structure and synchrony in abundance should be used as complementary information as they reflect different spatial processes and suggest that management actions should differ with respect to scale depending on the management targets applied. We propose similar analysis should be applied to areas outside the Baltic Sea, and other stock identification methods, to improve management of fish resources.
... It is likely that higher quantities of many fish species, especially demersal fish in wind farm areas, as suggested by our synthesis, could also at least partly be attributed to restricted fishing and shipping activities, since fishing activity in OWF areas is generally disallowed (although exceptions exist) (Schupp et al., 2021). Increases in biomass and generally healthier populations have also been reported for two benthic fish species, turbot (Scophthalmus maximus) and European flounder (Platichthys flesus), within a large no-take-zone in the Baltic Sea (Florin et al., 2013). Moreover, the no-take-zone had older individuals, a lower length-at-age, and a more balanced sex ratio. ...
Article
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Offshore wind energy developments in European waters are rapidly expanding to meet the increasing global demand for renewable energy. These developments provide new substrates for species colonisation, but also introduce changes in electromagnetic fields, noise levels, and hydrological conditions. Understanding how these man-made structures affect marine biodiversity across various species groups is crucial, yet our knowledge in this field remains incomplete. In this synthesis paper, based on 14 case studies conducted in northeastern Atlantic (North, Irish and Baltic seas), we aggregated species-level data on abundance, biomass, and other quantity proxies spanning the entire food chain from invertebrates to mammals, and compared these variables between wind farms and nearby control sites. Overall, our analysis revealed that in wind farm areas, species tend to occur at higher quantities than in control areas. Additionally, we noticed a slight trend where the positive effect of wind farms was more pronounced in newly established ones, gradually diminishing as wind farms aged. None of the tested covariates (depth, distance from coastline, years in commission) nor species' characteristics (habitat and spawning types, trophic level) showed statistical significance. When examining species groups individually, there was a tendency for wind farm areas to harbour higher quantities of polychaetes, echinoderms and demersal fishes. These findings suggest that wind farms contribute to the so-called reef-effect, providing shelter and food supplies to their inhabitants and acting as no-take-zones. Our results support the idea that wind farms could serve as zones of increased local biodiversity, potentially facilitating spillover effects to nearby areas for certain species groups. Further studies are necessary to gain a more comprehensive understanding of the adverse effects of wind farms on associated biodiversity, while also exploring avenues to amplify their positive impacts.
... Vid Gotska Sandön ökade tätheten av piggvar både jämfört med ett referensområde och jämfört med före fredningen. För skrubbskädda var effekten inte lika tydlig (Florin et al. 2013). Även de fredningsområden som inrättades mellan 2009 och 2011 har visat positiva effekter i flertalet områden (Bergström et al. 2016, Berkström et al. 2021) (Havs-och vattenmyndigheten 2016d) (se också Box 11). ...
Technical Report
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Havsmiljöinstitutet genomförde under 2021 ett projekt där aktuell information om uppföljning av effekter av fysiska åtgärder och områdesbaserade åtgärder sammanställdes. Resultaten presenteras i denna rapport. Informationen har hämtats från databaser, rapporter och artiklar om uppföljning av effekter av åtgärder samt samtal med forskare och utredare på myndigheter som på olika sätt arbetar med genomförande, uppföljning eller tilldelning av medel för åtgärder. Samtalen fokuserade på personernas erfarenheter av uppföljning av åtgärder, befintligt kunskapsläge om effekter av åtgärder, och för utredare även hur arbetet med uppföljning av åtgärder organiseras på myndigheten. Från det inhämtade underlaget och samtalen framkom en samsyn kring flera brister i uppföljning av åtgärder i Sverige, bland annat: brister i kunskap om effekter för flera vanligt förekommande åtgärdstyper som genomförs för att förbättra tillståndet eller minska påverkan på kust och hav, ett behov av en tydligare systematik och långsiktighet i uppföljning av åtgärder, brister i data och information om genomförda åtgärder, beträffande såväl tillgänglighet som fullständighet och ändamålsenlig form.
... While many MPAs limit but not exclude activities in the MPA, currently three highly protected marine areas exist around the UK, out of 356 MPAs, covering 21.07km 2 (0.0024% of the UKs EEZ) (Solandt 2018; JNCC 2020) and several more are proposedly to be trailed starting 2022 (DEFRA 2022). High levels of protection for MPAs have been shown to increase organism biomass inside reserves(Shears et al., 2006), increased organism reproductive outputs and growth rates(Florin et al., 2013), and improve a site's biodiversity(Howarth et al., 2015). While what constitutes effective management is contextually dependant on each MPA, many activities are ecologically incompatible such as trawling in areas set up to conserve benthic organisms. ...
Thesis
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Problems of climate change and marine conservation occur across many aspects of social-ecological systems. Addressing these challenges requires the use of interdisciplinary research techniques. Marine Protected Areas (MPAs) are a common mechanism to support marine conservation and livelihoods but are often created without regard to climate change impacts. Understanding how climate change will impact MPAs, how existing MPAs can be modified considering climate, and where current institutional practices enable climate change adaptation are all needed to support future seas. Meta-analysis of available experimental work examining European benthic organism responses to ocean acidification and warming suggests that calcifying organisms are likely to experience decreases in growth, reproductive capacity, and survival. Meta-analysis also shows European fleshy algae are resilient to end of century projected conditions. Underlying MPA ecological conditions are therefore likely to change based on current emission pathways. Examination of UK MPA case studies shows that existing conservation mechanisms can be adjusted to enhance resilience to climate change in marine social-ecological systems. Ways to achieve this include adopting adaptive management approaches, ecosystem-based management approaches, enhanced recognition of climate change in primary legislation used to support MPAs, and improved site monitoring. Doctrinal analysis of key conservation legislation supporting English MPAs and semi-structured interviews with individual’s familiar using said legislation reveals that there is large scope for adaptive governance in response to climate change in inshore waters. Current legislation has supported ecosystem-based management approaches and large-scale habitat restoration efforts. However, practical capacity issues of insufficient resourcing for key marine governance organisations prevents effective monitoring of MPAs, researching challenges within inshore regions, and enforcing conservation agreements.
... Due to the sexual dimorphism that exists for plaice, with females being generally larger than males (Bromley, 2000), high fishing pressure is expected to involuntarily select for male fish that are smaller at a certain age. A larger fish size and a sex ratio that is skewed towards more females could therefore indicate that the presence of the OWF offers a refuge effect for plaice against fishing mortality (Di Franco et al., 2009;Florin et al., 2013). These results, together with the apparent increased food availability offered by the hard substrates, suggest that plaice can benefit from the presence of OWFs. ...
Article
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Offshore wind farms (OWFs) and their associated cables, foundations and scour protection are often constructed in soft sediment environments. This introduction of hard substrate has been shown to have similar effects as artificial reefs by providing food resources and offering increased habitat complexity, thereby aggregating fish around the turbines and foundations. However, as most studies have focused their efforts on fish species that are typically associated with reef structures, knowledge on how soft sediment species are affected by OWFs is still largely lacking. In this study, we analysed the trophic ecology and condition of plaice, a flatfish species of commercial interest, in relation to a Belgian OWF. The combination of a stomach and intestine content analysis with the use of biomarkers (i.e. fatty acids and stable isotopes) identified a clear shift in diet with increased occurrences of typical hard substrate prey species for fish in the vicinity of the foundations and this both on the short and the long term . Despite some condition indices suggesting that the hard substrate provides increased food availability, no clear increases of overall plaice condition or fecundity were found. Samples from within the wind farm, however, contained larger fish and had a higher abundance of females compared to control areas, potentially indicating a refuge effect caused by the cessation of fisheries activities within the OWF. These results suggest that soft sediment species can potentially benefit from the presence of an OWF, which could lead to fish production. However, more research is still needed to further elucidate the behavioral ecology of plaice within OWFs to make inferences on how they can impact fish populations on a larger spatial scale.
... Turbot and brill (Scophthalmus rhombus) have been shown in tagging experiments to only have short seasonal migrations in the Kattegat moving to deeper waters in the autumn and winter and returning to shallow waters in the spring (Bagge, 1987). Turbot have also showed positive response with increased abundance and older individuals in an NTZ in the Baltic Sea (Florin et al., 2013). Microstomus kitt and P. platessa tagging in the English Channel indicated limited migration as opposed to P. platessa, which were recaptured in a larger part of the North Sea (Jennings et al., 1993). ...
Article
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To supplement catch and effort regulations with the purpose to rebuild the cod (Gadus morhua) stock in Kattegat, Sweden and Denmark established a large (426 km2) year-round no-take zone (NTZ) surrounded by partially protected areas (PPAs) in 2009. The purpose of these spatial regulations was to prohibit cod fishing on the spawning grounds and to displace fisheries bycatch of cod from areas where mature cod aggregate in the Kattegat. The aim of this study is to evaluate the effects of the established NTZ and PPAs on the local fish assemblage, including cod. Based on a spatially high-resolution bottom trawl survey in the Kattegat (covering 2008–2021), multivariate analyses revealed significant shifts in the fish assemblage. A closer analysis indicated that six to seven fish species, including cod increased in the NTZ relative to control areas depending on if abundance or biomass was used as dependent variable. Univariate analysis showed that two flatfish species dab (Limanda limanda) and lemon sole (Microstomus kitt), and Norway lobster (Nephrops norvegicus) significantly increased in biomass in the NTZ, and turbot (Scophthalmus maximus) in the PPA relative to the control areas. These results suggest that the NTZ protected even relatively mobile species in an open sea system, such as the Kattegat. However, neither cod abundance nor biomass showed a significant increase as an effect of the NTZ and PPA despite two relatively strong year classes in 2012 and 2013, which possibly would have helped the recovery of the cod stock. As assessed by the International Council for the Exploration of the Sea in 2022, Kattegat cod continuously suffer from being severely overfished with low recruitment, and high discard rates in the mixed N. norvegicus fishery, is considered the major driver behind the reinforced depletion of the stock.
... Higher levels of protection as showing in the UK [122,123,124] and supported by a wealth of studies globally hold the greatest potential for protecting the marine environment [1,36,64]. High levels of protection for MPAs have been shown to increase organism biomass inside reserves [125], increased organism reproductive outputs and growth rates [126], and improve a site's biodiversity [127]. Such high level of protection and associated management is rare though in UK MPAs and globally ( [63,128]; Roberts et al., 2020) with lack of management planning and implementation or inappropriate activities being permitted being reported. ...
Article
Full-text available
Climate change is impacting marine seascapes against a backdrop of multiple anthropogenic stressors. These current impacts are projected to increase in the future with increasing warming, acidification, oxygen loss, and sea level rise. Marine Protected Areas (MPAs) have been established to protect features in the ocean, traditionally with a focus to reduce fishing pressures and infrastructure placements. These MPAs are static in nature and are rarely considering climate change; therefore, their potential adaptation effectiveness as local adaptation measures for conservation in response to climate change are not clear. Here we discuss the challenges to Marine Protected Areas as conservation tools and for adaptation to climate change threats. We use two case studies from the UK to ask how climate change resilience could be included in MPA management to future-proof these conservation measures. We conclude that the resilience of MPAs to climate change would be better supported when adaptive management measures and an ecosystem-based approaches are adopted. We emphasise the need to increase the recognition in the primary legislation of MPAs and the monitoring of sites to better understand climate change as it becomes more pronounced, and impacts emerge.
... Another possibility is that the artificial reef acts as a refuge from fishing activity (e.g., trawling). Marine-protected areas or "no-take" zones have been shown to provide considerable refuge to populations of pelagic and demersal fish (Kerwath et al. 2009;Florin et al. 2013;Abecasis et al. 2014;Jacoby et al. 2020). Thus, some of the tagged fish might spend their summer period in close vicinity to the airport as a refuge. ...
Article
Offshore manmade structures, termed artificial reefs (e.g., wind farms, oil platforms, and manmade islands), affect the movement and migration of wild migratory marine animals. Certain types of migratory pelagic and benthic fish are known to utilize artificial reefs as feeding areas, for spatial reference (landmarks for their navigation), or as meeting points. However, little is known about the impact of artificial reefs on the migratory behavior of demersal flatfish. The marbled flounder (Pseudopleuronectes yokohamae), an important commercial flatfish species, exhibits seasonal migration between shallow water for spawning in winter and deeper water to avoid high water temperatures in summer. In this study, 39 tagged marbled flounders were released in the shallow water of the inner Osaka Bay area in June 2016, and then actively tracked, predominantly in deeper waters (100–140 m), from a fishing boat every week until mid-September 2016. Our active tracking detected no tagged fish in the deeper waters, whereas 36% of the fish were detected in the shallow water (10–15 m) around an artificial reef (offshore manmade island) at a high water temperature (26 °C). We suggest that a portion of the marbled flounder population did not show seasonal migration but remained in the shallow water around the artificial reef, even though the water temperature was high in summer. We suggest that this is related to the abundant food supply associated with the artificial reef.
... In Northern Europe, MPAs are increasingly being used as a fisheries management tool (Denny and Babcock, 2004;Fenberg et al., 2012;Pastoors et al., 2000), but extensive data collections for a scientific evaluation of MPAs are generally rare. As a result, the success of MPAs as means to enhance populations of target species has been questioned (Florin et al., 2013). ...
Article
Full-text available
Marine protected areas (MPAs) are usually considered to have positive effects on the recovery of over-exploited populations. However, resolving the extent to which MPAs function according to their conservation goals requires that essential demographic information such as individual survival and population size are quantified. To this end, we analyzed a 16-year replicated mark-recapture study on European lobster (Homarus gammarus, n = 8793) conducted at several protected and unprotected sites in southern Norway, quantifying the impact of MPAs on local population dynamics by means of a “before-after control-impact” study approach (BACI). Lobster survival and abundance were estimated by applying mu lti-state and robust design models to the mark-recapture data. These models revealed underlying positive responses to protection. Annual survival rates and population abundances reached higher values in the MPAs, compared to the unprotected sites (abundance range: MPAs = 96–1172, control areas = 92–747). In general, female survival was higher than male survival (range of survival: male = 0.13–0.75, female = 0.37–0.85), while larger males benefited more from protection compared to smaller males (range of increase in survival after protection: big = 100–125%, small = 55–101%). We also detected regional differences in demographic responses to protection, as not all MPAs showed the same changes in abundance over time. Our results show that MPAs can reach conservation goals by increasing the local survival and abundance of lobster, but they also highlight demographic differences between sexes and geographic areas that are worth considering for the management and design of both current and future MPAs.
... Several hypotheses, which could also be linked to each other, have been proposed to explain the bad state of the EBC: 1) increasing hypoxia, 2) decreasing availability of fish prey, 3) shortage of benthic food, 4) increasing infections of parasites and 5) change in selectivity of fisheries (ICES, 2015a). Flounder (Platichthys flesus) in the eastern Baltic Sea is another important demersal predator (Florin et al., 2013), is the most landed flatfish in the Baltic Sea (Florin and Höglund, 2008;Orio et al., 2017b) and is managed as four different stocks (24)(25)(26)(27)(28)(29)(30)(31)(32). Two of the three flounder stocks in the eastern Baltic Sea (SDs 24-25 and SDs 27+29-32 stocks) show an overall increase in abundance in the last 5 years (ICES, 2017b(ICES, , 2017a(ICES, , 2017c. ...
Thesis
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The Baltic Sea is a frontrunner in ecosystem analysis and assessment, which have been used also in multispecies fisheries management advice. In the Baltic Sea, the multispecies assessment and management advice have been focused on the pelagic interactions between cod (Gadus morhua), sprat (Sprattus sprattus) and herring (Clupea harengus), by virtue of their well-known ecology. However, the fish interactions occurring in the benthic habitat are largely unknown. This study investigates, for the first time, the feeding interactions between the most important demersal fish species, cod and flounder (Platichthys flesus), in three areas of the eastern Baltic Sea. In this study I use stomach data from 2015 and 2016, collected in the ICES subdivisions 25 – 28 by the Swedish University of Agricultural Sciences, Department of Aquatic Resources. The diet of cod differs between the areas but, overall, shows an ontogenetic shift with a decrease of benthic prey and an in-crease of fish preys with size. In the coastal area the amount of benthic prey is al-ways > 50% irrespective of predator size, while in the offshore areas the amount of fish prey increase > 50% with increasing cod size. Conversely, the diet of flounder is relatively constant between sizes and areas. Cluster analyses revealed similarity between the diet of flounder and small-medium size cod in the offshore areas. A significant diet overlap was found between cod < 30 cm and flounder > 20 cm in the offshore area in SD 25, which is mainly driven by similar benthic prey, especially Saduria entomon, in the diet of both predators. These results point to a food competition between cod and flounder, likely augmented by recent increased abundance of Baltic flounder stocks. This competition could decrease the availability of benthic prey for cod, which, in turn, can lead to low condition factor, a reduction of cod growth and ultimately accentuate the negative effects of hypoxia on cod. Because of all of these reasons, cod and flounder competition could be an-other factor explaining the current bad status of the Eastern Baltic Cod stock.
... The model presented in this thesis (Paper V) is the first and only existing approach for predicting future distribution possibilities or identifying potentially high-quality areas for population maintenance of P. solemdali, and is more rigorous than other existing approaches for predicting Baltic Sea flatfish distribution patterns. In addition to forecasting climate effects of P. solemdali, the environmental suitability model could be used for choosing and designing no-take zones and MPAs (see Florin et al. 2013). Conceptually the simulation-based approach is applicable for any species or populations. ...
Thesis
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Initiated by signs of drastic declines of once abundant flounders in the northern Baltic Sea, this thesis characterised/quantified these declines and studied their potential reasons. Multiple approaches were used to describe population trends, reveal intricacies in stock structure, and assess links to key environmental drivers. The results from the thesis verified clear negative trends in both adult and juvenile flounders in the northern Baltic Sea over the last 2–4 decades. Genetics revealed well-defined genetic structure and evidence for far gone speciation among Baltic Sea flounders, leading to the recognition of two instead of one flounder species, one of which was recently described as the only endemic fish species known to the region. Contrary to previous belief, flounders on the coast of Finland in the northern Baltic Sea were shown to be a mixed assemblage of this cryptic species pair. The thesis further showed that temporal variability in local species composition of the flounder assemblage explained some of the observed stock decline and was related to changing local and regional environmental conditions, of which reproductive volume, salinity, temperature and eutrophication were identified as potentially important factors. Finally, the thesis presented a new method for modelling environmental suitability for long-term population maintenance of the newly described Baltic flounder. The knowledge obtained has great value for how we understand and investigate stock composition and population dynamics of Baltic Sea flounders, and relates to issues of source-sink mechanisms, population connectivity, biological traits, resilience to exploitation and environmental change, among others. The results are likely important for future management and conservation of these fishes in the changing environment of the Baltic Sea.
... Thus, the number of fish in each year-class was summed and the relative abundance per age modelled using the function ln (N) = a + b (age), and obtained residuals used as an estimate of the relative year class strength. In addition, data on the relative year-class strength were derived from Fig. 6 in Florin et al. (2013); monitory fishing performed in 2006-2009 in the same area off eastern Gotland (SD 3d 28.2) as in the present study. ...
Article
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The brackish water Baltic Sea is strongly influenced by irregular saline water inflows. Fewer inflow events since the 1980s have resulted in a decrease in salinity, and will according to predicted climate change continue to decrease. The newly described Baltic flounder Platichthys solemdali has adapted to reproduction at low salinity conditions since it colonized the Baltic Sea 7000 years BP; in the area studied (ICES SD 3d 28.2) spawning occurs at 3–20 m depth at ca 7 psu. Here we monitored variability in year-class strength as newly settled 0-gr fish in three coastal nursery areas, and compared obtained recruitment indices with prevailing temperature and salinity conditions. 0-gr abundance indices varied considerably between years, from 1 to 90, 10–296 and 17–86 at the respective sampling site, and showed strong accordance with the age structure of the adult stock. Variability in temperature showed no effect, but stronger and weaker year-classes respectively were related to variability in salinity in the range 6.6–7.1 psu with stronger year-classes at >6.8 psu. This coincides with variability in spermatozoa motility, fertilization rates and early egg development at different salinities and suggests that the year-class strength may be set already at the egg stage. Thus, only small changes in salinity at spawning may affect reproductive success and ultimately stock development. The potential effects on stock abundance and distribution facing climate change call for changes in future fishing patterns as well as adaptations in management to prevent stock collapse.
... In particular, no-take MPAs have proven effective at replenishing fish stocks especially of predator species targeted by fishermen, restoring ecosystems and rebuilding food webs (Claudet et al., 2011;Edgar et al., 2014;Garcia Charton et al., 2000;Lester et al., 2009;Sala and Giakoumi, 2018). While such evidence comes mainly from coastal rocky habitats (Di Franco et al., 2018), data from soft-bottom offshore areas show that also partial protection, namely from industrial fishing may effectively lead to a recovery of fishery resources (Bailey, 1997;Fisher and Frank, 2004;Florin et al., 2013;Jaworski et al., 2006;Murawski et al., 2000). ...
Article
Fishing leads to drastic changes in ecosystems with a net loss of predatory biomass. This issue has been evidenced from historical ecological studies and from the evaluation of the effects of effective and large marine protected areas. In two fishery reserves off the northern Sicily coast the red mullet Mullus barbatus underwent an impressive biomass increment and a few piscivores fish species recovered after a trawl ban. The red mullet, more than 20% of all demersal fish in the untrawled areas, represented a huge food resource to its potential predators. By contrasting two trawled and two untrawled gulfs we figured out predator-prey relationships through the use of a combined approach based on trophic niche, stable isotopes data and biomass. We show that the white grouper Epinephelus aeneus and the black-bellied anglerfish Lophius budegassa are the most important predators of the red mullet with higher biomass in the untrawled areas. We also found a potential re-establishment of the trophic role for white grouper inside the untrawled areas. Our study highlights some of the benefits obtained from the use of large offshore marine protected areas as a tool for ecosystem restoration.
... In the central Baltic Sea (SD27-28), populations of flounder (Platichthys flesus) and turbot (Scophthalmus maximus) are impacted by the fishery, as shown by changes in abundance and size composition in a no-take area (Florin et al., 2013). In some areas seals and cormorants take at least as much flatfish as the fishery (Table 1) and it is likely that there is competition for flatfish. ...
... Data not available Belgium NORTH SEA (de Clerck et al. 1984, Misra et al. 1989, 1990, Roose et al. 1998, Baeyens et al. 2003 SCHELDT ESTUARY (Álvarez-Muñoz et al. 2015, Hampel et al. 2005, Maes et al. 1997 GREAT BELT (Jørgensen & Pedersen 1994, Vorkamp et al. 2011 Bay of Aarhus (Tarpgaard et al. 2005, Madsen et al. 2013 Gabet, Kerteminde, Odense Fjord, Seden, Vejle (Madsen et al. 2013) KATTEGAT (Skall et al. 2000, 2005, Strand & Jacobsen 2005 Ålborg, Sebbersund (Madsen et al. 2013 NORTH SEA (Borsa et al. 1997, Mortensen et al. 1999, Skall et al. 2000, 2005 Limfjord (Kiørboe et al. 1983, A. K. Andersen et al. 2005, Riisgård et al. 2012, Tomczak et al. 2013 Ringkøbing (Madsen et al. 2013 , Karlsson et al. 2003, Malmström et al. 2004 Knyllgorna, Segelska (Sipiä et al. 2006) Kyrksundet (Voigt 2001) Sundholm Bay (Sipiä et al. , 2002 Tvärminne (Boström et al. 2002, Kankaanpää et al 2005, Sipiä et al. 2006, Borg et al. 2014 RIVER BIDASOA (Lekuona & Campos 1996 (Goksøyr et al. 1991, Marthinsen et al. 1991, Staveland et al. 1993 Glomma estuary (Marthinsen et al. 1991, Staveland et al. 1993 Hubukta, Øra (Hylland et al. 1998) Oslofjord (Reiersen & Fugelli 1984, Husøy et al. 1996 BALSFJORDEN (TROMSØ) (Lønning et al. 1988) BORGENFJORD (He & Mork 2015) HARDANGERFJORD Eikhamran, Granvin, Grimo, Herand, Nordheimsund, Strandebarm, Utne, Varaldsøy (Julshamn & Grahl-Nielsen 1996) SØRFJORDEN TRONDJORD (Lile 1998) Poland BALTIC SEA (Baršienė et al. 2012) off Kolobrzeg (Køie 1999) off Leba (Køie 1999) BAY OF GDAŃSK (Køie 1999, Skwarzec et al. 2001, Kijewska et al. 2009, Baršienė et al. 2012 Mechelinki, Sobieszewo Gdańsk (Mazur-Marzec et al. 2007) Sopot , Mazur-Marzec et al. 2007) Portugal DOURO ESTUARY (Vinagre et al. 2008) LIMA ESTUARY (Ramos et al. 2006, Mendes et al. 2014, Amorim et al. 2016 MINHO ESTUARY (Morais et al. 2011, Souza et al. 2013, Dias et al. 2017 MONDEGO ESTUARY (Calvès et al. 2013, Primo et al. 2013 NORTHERN COAST (Sobral 2007, Vasconcelos et al. 2008 RIA DE AVEIRO LAGOON (Sobral 2007) SADO ESTUARY (Borsa et al. 1997 -currently absent (Nissling et al. 2002) Himmerfjärden (Elmgren et al. 1983) Island Gotska Sandön (Florin et al. 2013) Karlskrona, Nynăshamn, Öland, Văstervik (Fornbacke et al. 2002) Kvädöfjärden SEA OF MARMARA Ekinli Lagoon (Oguz & Öktener 2007) Gönen River (Fautz 1986) Ukraine ...
Technical Report
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The European flounder is a demersal species present along the NE-Atlantic Ocean, from Norway to Portugal, both in coastal and estuarine ecosystems (Nielsen, 1986). It is also present in the adjacent seas - Baltic, North, White, Mediterranean, and Black seas (Nielsen, 1986; Figure 5.2.2-1, Table 5.2.2-2). The species was introduced in North America through ballast water; however, the last record dates back to 2000 (Erling Holm, personal communication). The European flounder has been considered a strict catadromous species. However, there is some controversy about classifying flounder as catadromic, semi-catadromic, estuarine migrant, marine-estuarine opportunistic, or even as an estuarine resident species (Elliott & Dewailly, 1995; Elliott et al., 2007). Recent works revealed that flounder is not an estuarine resident species (Daverat, Martin, Fablet, 2011, & Pécheyran, 2011a; Morais, Dias, Babaluk, & Antunes, 2011), despite using estuarine habitats for extended periods of time (Jagger, 1998; Marchand, Tanguy, Laroche, Quiniou, & Moraga, 2003).
... The key role of EFH for the maintenance of fish stocks has been acknowledged in management, for example in the USA and Canada, by the introduction of legal acts for the protection of EFH. The integration of conservation and fisheries objectives is still a matter of controversy in European environmental legislation (Michanek and Christiernsson, 2013;Salomon et al., 2014), despite the clear mutual benefits demonstrated by the implementation of marine protected areas, indicating that a broader perspective on habitat protection will be essential for moving towards an ecosystembased management of marine resources (Baskett and Barnett, 2015;Fenberg et al., 2012;Florin et al., 2013;Seitz et al., 2014;Sundblad et al., 2014). A central part of an ecosystem-based marine management and spatial planning process is full-coverage mapping of EFH Le Pape et al., 2014;Valavanis et al., 2008). ...
Article
Identification of essential fish habitats (EFH), such as spawning habitats, is important for nature conservation, sustainable fisheries management and marine spatial planning. Two sympatric flounder (Platichthys flesus) ecotypes are present in the Baltic Sea, pelagic and demersal spawning flounder, both displaying ecological and physiological adaptations to the low-salinity environment of this young inland sea. In this study we have addressed three main research questions: 1) What environmental conditions characterize the spatial distribution and abundance of adult flounder during the spawning season? 2) What are the main factors defining the habitats of the two flounder ecotypes during the spawning season? 3) Where are the potential spawning areas of flounder? We modelled catch per unit of effort (CPUE) of flounder from gillnet surveys conducted over the southern and central Baltic Sea in the spring of 2014 and 2015 using generalized additive models. A general model included all the stations fished during the survey while two other models, one for the demersal and one for the pelagic spawning flounder, included only the stations where each flounder ecotype should dominate. The general model captured distinct ecotype-specific signals as it identified dual salinity and water depth responses. The model for the demersal spawning flounder revealed a negative relation with the abundance of round goby (Neogobius melanostomus) and a positive relation with Secchi depth and cod abundance. Vegetation and substrate did not play an important role in the choice of habitat for the demersal ecotype. The model for the pelagic spawning flounder showed a negative relation with temperature and bottom current and a positive relation with salinity. Spatial predictions of potential spawning areas of flounder showed a decrease in habitat availability for the pelagic spawning flounder over the last 20 years in the central part of the Baltic Sea, which may explain part of the observed changes in populations' biomass. We conclude that spatiotemporal modelling of habitat availability can improve our understanding of fish stock dynamics and may provide necessary biological knowledge for the development of marine spatial plans.
... For the cod stocks, these stock assessments already exists, although the assessment for Eastern Baltic cod stock has been rejected in the last years and the fisheriesindependent time series used before have been shorter. For flounder, which is equally important for fisheries and has a central role in the ecosystem (Florin et al., 2013;€ Ostman et al., 2013;ICES, 2016) analytical stock assessments are not available. The CPUE time series and size-based indicators we developed hopefully help the conservation and management of these stocks in the Baltic Sea. ...
Article
Standardized indices of abundance and size-based indicators are of extreme importance for monitoring fish population status. The main objectives of the current study were to (i) combine and standardize recently performed trawl survey with historical ones, (ii) explore and discuss the trends in abundance, and (iii) the trends in maximum length (Lmax) for cod (Gadus morhua) and flounder (Platichthys flesus) stocks in the Baltic Sea. Standardization of catch per unit of effort (CPUE) from trawl surveys from 1978 to 2014 to swept area per unit of time was conducted using information on trawling speed and horizontal opening of the trawls. CPUE data for cod and flounder stocks were modelled using generalized additive models (GAMs) in a delta modelling approach framework, while the Lmax data were modelled using ordinary GAMs. The CPUE time series of the Eastern Baltic cod stock closely resembles the spawning stock biomass trend from analytical stock assessment. The results obtained furnish evidence of the cod spill-over from Subdivisions (SD) 25–28 to SD 24. The decline of Lmax in recent years was evident for both species in all the stocks analysed indicating that the demersal fish community is becoming progressively dominated by small individuals. It is concluded that the standardization of long time series of fisheries-independent data constitutes a powerful tool that could help improve our knowledge on the dynamics of fished populations, thus promoting a long-term sustainable use of these marine resources.
... According to observations in the present study, large differences in realized fecundity between areas may occur, and potentially also between years. Hence, in addition to varying abiotic conditions affecting offspring survival prior to settlement (Nissling et al., 2006) and food availability affecting growth and potentially survival after settlement in nursery areas (Martinsson, 2011), variability in egg production according to fish condition may contribute to the high recruitment variability of S. maximus in the Baltic Sea (Molander, 1954;Florin et al., 2013). A topic for future studies is to evaluate the interannual variability of the realized fecundity in different areas, and to reveal whether differences are driven mainly by discrepancies in the potential fecundity, i.e. the number of vitellogenic oocytes recruited or by the extent of down-regulation during spawning (present investigation). ...
Article
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Down-regulation of fecundity through oocyte resorption was assessed in Baltic Sea turbot Scophthalmus maximus at three locations in the period from late vitellogenesis in April to spawning during June to July. The mean ± s.d. total length of the sampled fish was 32·7 ± 3·1 cm and mean ± s.d. age was 6·2 ± 1·5 years. Measurements of atresia were performed using the 'profile method' with the intensity of atresia adjusted according to the 'dissector method' (10·6% adjustment; coefficient of determination was 0·675 between methods). Both prevalence (portion of fish with atresia) and intensity (calculated as the average proportion of atretic cells in fish displaying atresia) of atresia were low in prespawning fish, but high from onset of spawning throughout the spawning period. Atretic oocytes categorized as in early alpha and in late alpha state occurred irrespective of maturity stage from late prespawning individuals up to late spawning fish, showing that oocytes may become atretic throughout the spawning period. Observed prevalence of atresia throughout the spawning period was almost 40% with an intensity of c. 20%. This indicates extensive down-regulation, i.e. considerably lower realized (number of eggs spawned) v. potential fecundity (number of developing oocytes), suggesting significant variability in reproductive potential. The extent of fecundity regulation in relation to fish condition (Fulton's condition factor) is discussed, suggesting an association between levels of atresia and fish condition.
... Piscivores were defined as species with a fish-dominated diet during most of their life cycle, as identified by a trophic level !4.0 (Froese and Pauly, 2014). Since both commercial and household fisheries generally target piscivores (Jakubavi ci ut _ e et al., 2011; Karlsson et al., 2014;Pauly et al., 1998;Troynikov et al., 2013), the indicator is expected to decrease with increasing fishing pressure (Florin et al., 2013) and can be used as an estimate of the potential value of the fish community for human use. The indicator may also indicate ecosystem functionality in general, due to the role of piscivores in regulating food web processes (Eriksson et al., , 2009. ...
... In northern Europe, PPAs are increasingly being used as a fisheries management tool (Pastoors, Rijnsdorp & Van Beek 2000;Denny & Babcock 2004), but few studies have so far empirically evaluated the effects of PPAs on harvested species, in part due to the lack of sufficiently detailed data collections (Allison, Lubchenco & Carr 1998;Lubchenco et al. 2003;Sale et al. 2005; but see Goñi et al. 2008;Moland et al. 2013a). Indeed, the success of PPAs at enhancing populations of target species remains unclear because most scientific evaluations have focused on no-take zones and also because of the poor monitoring programmes conducted outside marine protected areas in general, especially in the case of northern Europe (Florin et al. 2013). ...
Article
In recent years, marine protected areas ( MPA s) excluding all or some fishing activities have become widely applied as a tool to rebuild marine ecosystems and fisheries, but still, our knowledge of the effects of MPA s on the demography of harvested populations remains scarce, especially in cases where partly protected areas are still supporting some fishing activities. Here, we investigated the influence of partial protection – excluding fixed gears such as gillnets and traps but still allowing a hook and line fishery – on the demography of A tlantic cod G adus morhua along the N orwegian S kagerrak coast. To do so, we applied novel multi‐event models to a 9‐year data set containing both live recaptures and dead recoveries of marked fish of different sizes collected before and after the implementation of an MPA , also including several unprotected sites. At the MPA site, the annual proportion of deaths due to fishing decreased from 0·59 before MPA implementation to 0·32 after MPA implementation. As a result, annual survival increased by 167% (from 0·09 to 0·24) for small (16–44 cm) and 83% (from 0·23 to 0·42) for big (45–97 cm) cod, respectively. Average survival was lower in unprotected areas, and annual fishing mortality was higher, representing almost 100% of the total mortality of large‐sized cod in some years. Annual emigration rates (i.e. spillover from the MPA ) increased in the last years of the study, but no differences in body growth were detected between sites. Closure of the fishery within the MPA would further increase the annual survival of smaller individuals by 100% (from 0·24 ± 0·07 to 0·48 ± 0·11) and that of larger individuals by 44% (from 0·42 ± 0·05 to 0·60 ± 0·09). Synthesis and applications . Our study reveals how current marine protected areas (MPA s) function and provides important insights for guiding a future adaptive management process. Given that harvested populations will not be able to sustain annual survival rates consistently below 30%, as found here; our results underscore the urgency of effective management measures such as no‐take zones in areas where local populations are particularly reduced or in dire need of demographic rescue.
... Benefits of spatial closures are not restricted to reef fishes on rocky habitats. The establishment of a no-take zone for flatfishes in the Baltic Sea resulted in increased densities of two exploited species and a net larval export to fished areas [4]. ...
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Skates (Rajiformes: Rajoidei) are common mesopredators in marine benthic communities. The spatial associations of individual species and the structure of assemblages are of considerable importance for effective monitoring and management of exploited skate populations. This study investigated the spatial associations of eastern North Pacific (ENP) skates in continental shelf and upper continental slope waters of two regions: central California and the western Gulf of Alaska. Long-term survey data were analyzed using GIS/spatial analysis techniques and regression models to determine distribution (by depth, temperature, and latitude/longitude) and relative abundance of the dominant species in each region. Submersible video data were incorporated for California to facilitate habitat association analysis. We addressed three main questions: 1) Are there regions of differential importance to skates?, 2) Are ENP skate assemblages spatially segregated?, and 3) When skates co-occur, do they differ in size? Skate populations were highly clustered in both regions, on scales of 10s of kilometers; however, high-density regions (i.e., hot spots) were segregated among species. Skate densities and frequencies of occurrence were substantially lower in Alaska as compared to California. Although skates are generally found on soft sediment habitats, Raja rhina exhibited the strongest association with mixed substrates, and R. stellulata catches were greatest on rocky reefs. Size segregation was evident in regions where species overlapped substantially in geographic and depth distribution (e.g., R. rhina and Bathyraja kincaidii off California; B. aleutica and B. interrupta in the Gulf of Alaska). Spatial niche differentiation in skates appears to be more pronounced than previously reported.
... At least one situation where it is possible to see the effects of exploitation and density is inside and outside no-take zones (NTZ). In the central Baltic, Florin et al. (2013) show reduced growth rates for both European flounder and turbot inside the NTZ where the densities are higher, however, there are compound- ing effects such as the variability in salinity affecting growth inside and outside the NTZ and the size selective fishing pressure outside the NTZ. Rijnsdorp (1994) also points out that other factors could be involved in the changes in growth rate. ...
Chapter
Age and growth studies of flatfish form some of the oldest contributions to the scientific literature. Age-estimation methods are based mostly on reading otolith annuli, however, scales are used for some species. A variety of age validation studies have been pursued, using direct methods and radiometric techniques. The growth of flatfish larvae is better understood for aquaculture species than for wild species and there seems to be a propensity for high individual variability. Growth slows during metamorphosis in many species studied. On the nursery grounds growth is influenced by food availability and temperature but also shows patterns of density dependence and compensatory growth, and counter- and co-gradient variation in species with wide latitudinal ranges. Flatfishes can reach considerable ages and in general there is a sexual dimorphism where females are larger than males.
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Connectivity in coastal waters is described as the ability of animals, plants, sediments and organic material to spread freely between the open sea and coast, along the coastline and between coastal areas and inland waters. Since connectivity has an important and pivotal role regarding the biological, physicochemical, and hydromorphological conditions in aquatic systems, it is included as a quality element when estimating ecological status of surface waters in the coastal zone. The description of connectivity and how it should be evaluated is deficient in the regulations provided by the Swedish Agency for Marine and Water Management, SwAM (HVMFS 2019:25). As such, the Department of Aquatic Resources at the Swedish University of Agricultural Sciences (SLU Aqua) was assigned to give suggestions on what information on the biological connectivity concerning plants and animals that could be included in a revised version of these regulations. The assignment also included to provide a knowledge base on connectivity and physical disturbance in the coastal zone. In addition, the assignment included analysing physical disturbance on the connectivity of fish in the coastal areas of the Skagerrak, Kattegat and the Baltic Sea. When revising the regulations, it was noted that information on the biological aspects of connectivity, and at what scales it operates, are missing. The current regulations do not account for connectivity being either active, through migrations of young and adult organisms, or passive, through transport of eggs, larvae, spores, seeds or fragments by currents (Chapter 2.1.2). This is important to keep in mind, since physical disturbance caused by jetties, piers, noise, boat traffic, etc. has different effects depending on what type of connectivity is in focus. The different dispersal types also occur over different time scales, where active migrations often occur on a seasonal basis and between different life stages, while passive dispersal generally occurs over days or weeks as larvae and spores develop in the free water column before settling on suitable habitat. There are also species that live their entire lives in open waters, such as phytoplankton, which is also included as a biological quality element to be assessed. Within the assessment process, it is essential to distinguish between typical home ranges and maximum migration and dispersal distances, as home ranges are relevant for population dynamics, while maximum migration and dispersal distances have a greater impact on genetic variation between populations. It is also important to consider how connectivity may be affected by a changing climate. Fish play a central role in marine ecosystems, and therefore connectivity of fishes – both between the coast and sea, within coastal areas and between the coast and freshwater – become crucial determinants of ecological status, both in freshwater and in coastal waters. As it is mainly fish that undertake migration between coastal and freshwater areas and the coast and sea, it is difficult to classify parameter 8.3 Connectivity between coastal waters and transitional waters and coastal land areas in the regulations (HVMFS 2019:25) without including fish. Fish should therefore also be included as a biological quality element in the regulations for coastal waters (Chapter 2.1.3). Fish are included in the assessment of ecological status in the Marine Strategy Framework Directive (MSFD), which geographically overlaps with the Water Framework Directive (WFD) in the coastal zone. On the other hand, the MSFD does not include connectivity as a criterion in ecological status assessments. This means that connectivity in the coastal zone, especially for fish, is currently overlooked and coordination between the directives is therefore required to address this. As connectivity is primarily a biological function linked to fish and other organisms, it is also worth considering whether connectivity should be included among the biological quality elements instead of the hydromorphological ones. Summary To our knowledge, Sweden seems to be one of the countries in the EU that has come furthest in terms of assessment of connectivity within the Water Framework Directive. The other EU countries seem to focus on the other two hydromorphological quality elements hydrographic condition and morphological condition in their assessments. This may be due to the fact that connectivity is not included in the Water Framework Directive, but that Sweden has chosen to include it as a separate quality factor in the regulations on status assessment in Swedish coastal waters. Connectivity is mentioned in some contexts in other EU countries, but is then most often linked to freshwater systems with a focus on migratory fish and barriers in the form of hydropower and other physical structures that interfere with the flow of water. Interest in developing the hydromorphological quality element, including connectivity, has grown in the EU and a number of reports and scientific articles are available on the subject (Chapter 2.1.4). Connectivity can be measured in different ways and at different spatial scales. In Chapter 3, we summarise this information in a knowledge base for assessing connectivity in the coastal zone. Measuring and analysing the distribution of species in coastal and marine areas is a challenging task, and therefore knowledge in this area is still limited. Spatial analyses based on habitat maps and information on the dispersal distance of species have been used to analyse and assess active migration, especially in the Baltic Sea and the Skagerrak, as well as tagging studies and combinations of methods. To investigate passive dispersal, a combination of empirical data and hydrodynamic models have mainly been used to investigate dispersal routes and nursery habitats of different marine organisms and to identify key areas of connectivity such as sources and sinks. Chapter 3 also summarises the connectivity patterns of some biologically important groups of organisms and information on natural barriers such as salinity, depth and temperature that affect the dispersal of organisms and organic matter. Few studies have examined the effects of physical disturbance on connectivity, both within Europe and other parts of the world. Chapter 4.2 describes the studies that have been carried out in Swedish waters, regarding the effects of physical disturbance on passive dispersal and active migration, and Chapter 4.3 summarises information on physical disturbance and connectivity on some key habitats. Chapter 5 describes the results of new analyses of physical disturbance on fish along the Swedish west coast that are part of the current assignment. The results of these studies show that physical disturbance can have a significant impact on connectivity, especially for those species that depend on shallow and wave-sheltered areas for their reproduction. This type of habitat is particularly sensitive to physical impacts, with a noticeable reduction in connectivity. These areas are also the most affected by loss of connectivity due to their high degree of coastal development, including jetties, buoys and marinas. In addition, the results from the modelling studies showed that macroalgae and macrophytes are strongly affected by physical changes. These findings underscore the importance of carefully considering and managing physical disturbance on species and habitats in the coastal zone in order to conserve and protect vulnerable marine ecosystems and the services they provide. The results are important for decision-makers and planners working on conservation measures and management of these environments. There are significant knowledge gaps on connectivity and physical disturbance in coastal waters. Chapter 6 lists these knowledge gaps, including the need for high-resolution spatial data on the distribution of both organisms and pressures, as well as the relationships between these, both for the biological quality elements benthic fauna, macroalgae, marine plants and phytoplankton and for fish, which are not included as biological quality elements in the coastal zone. There is also a need for increasing the knowledge base on the effects of a changing climate and of various types of restoration measures on connectivity.
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Marine protected areas (MPAs) are increasingly established worldwide to protect and restore degraded ecosystems. However, the level of protection varies among MPAs and has been found to affect the outcome of the closure. In no-take zones (NTZs), no fishing or extraction of marine organisms is allowed. The EU Commission recently committed to protect 30% of European waters by 2030 through the updated Biodiversity Strategy. Importantly, one third of these 30% should be of strict protection. Exactly what is meant by strict protection is not entirely clear, but fishing would likely have to be fully or largely prohibited in these areas. This new target for strictly protected areas highlights the need to evaluate the ecological effects of NTZs, particularly in regions like northern Europe where such evaluations are scarce. The Swedish NTZs made up approximately two thirds of the total areal extent of NTZs in Europe a decade ago. Given that these areas have been closed for at least 10 years and can provide insights into long-term effects of NTZs on fish and ecosystems, they are of broad interest in light of the new 10% strict protection by 2030 commitment by EU member states. In total, eight NTZs in Swedish coastal and offshore waters were evaluated in the current report, with respect to primarily the responses of focal species for the conservation measure, but in some of the areas also ecosystem responses. Five of the NTZs were established in 2009-2011, as part of a government commission, while the other three had been established earlier. The results of the evaluations are presented in a synthesis and also in separate, more detailed chapters for each of the eight NTZs. Overall, the results suggest that NTZs can increase abundances and biomasses of fish and decapod crustaceans, given that the closed areas are strategically placed and of an appropriate size in relation to the life cycle of the focal species. A meta-regression of the effects on focal species of the NTZs showed that CPUE was on average 2.6 times higher after three years of protection, and 3.8 times higher than in the fished reference areas after six years of protection. The proportion of old and large individuals increased in most NTZs, and thereby also the reproductive potential of populations. The increase in abundance of large predatory fish also likely contributed to restoring ecosystem functions, such as top-down control. These effects appeared after a 5-year period and in many cases remained and continued to increase in the longer term (>10 years). In the two areas where cod was the focal species of the NTZs, positive responses were weak, likely as an effect of long-term past, and in the Kattegat still present, recruitment overfishing. In the Baltic Sea, predation by grey seal and cormorant was in some cases so high that it likely counteracted the positive effects of removing fisheries and led to stock declines in the NTZs. In most cases, the introduction of the NTZs has likely decreased the total fishing effort rather than displacing it to adjacent areas. In the Kattegat NTZ, however, the purpose was explicitly to displace an unselective coastal mixed bottom-trawl fishery targeting Norway lobster and flatfish to areas where the bycatches of mature cod were smaller. In two areas that were reopened to fishing after 5 years, the positive effects of the NTZs on fish stocks eroded quickly to pre-closure levels despite that the areas remained closed during the spawning period, highlighting that permanent closures may be necessary to maintain positive effects. We conclude from the Swedish case studies that NTZs may well function as a complement to other fisheries management measures, such as catch, effort and gear regulations. The experiences from the current evaluation show that NTZs can be an important tool for fisheries management especially for local coastal fish populations and areas with mixed fisheries, as well as in cases where there is a need to counteract adverse ecosystem effects of fishing. NTZs are also needed as reference for marine environmental management, and for understanding the effects of fishing on fish populations and other ecosystem components in relation to other pressures. MPAs where the protection of both fish and their habitats is combined may be an important instrument for ecosystem-based management, where the recovery of large predatory fish may lead to a restoration of important ecosystem functions and contribute to improving decayed habitats. With the new Biodiversity Strategy, EUs level of ambition for marine conservation increases significantly, with the goal of 30% of coastal and marine waters protected by 2030, and, importantly, one third of these areas being strictly protected. From a conservation perspective, rare, sensitive and/or charismatic species or habitats are often in focus when designating MPAs, and displacement of fisheries is then considered an unwanted side effect. However, if the establishment of strictly protected areas also aims to rebuild fish stocks, these MPAs should be placed in heavily fished areas and designed to protect depleted populations by accounting for their home ranges to generate positive outcomes. Thus, extensive displacement of fisheries is required to reach benefits for depleted populations, and need to be accounted for e.g. by specific regulations outside the strictly protected areas. These new extensive EU goals for MPA establishment pose a challenge for management, but at the same time offer an opportunity to bridge the current gap between conservation and fisheries management.
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Report on stock status & management advice for fish & shellfish species in Swedish waters (Report In Swedish). The resource overview for fish and shellfish stocks describes conditions and trends for commercial and recreational fishing's most relevant stocks of fish and shellfish in the sea and the four great lakes: Lake Vänern, Lake Vättern, Mälaren and Hjälmaren. The report is published annually and for the 2022 report, 48 species divided into more than a hundred different populations are described. For each stock, catch advice is given with the aim of keeping the stock within biological safe borders. The advice does not consider social or economic aspects of fishing. For nationally managed stocks the Swedish University of Agricultural Sciences, Department of Aquatic Resources (SLU Aqua) develops and gives the biological catch advice, and for stocks managed by the EU, advice is based on the International Council for the Exploration of the Sea (Ices) relevant catch advice. About 50 researchers from SLU Aqua participate in Ice's advisory work. SLU Aqua's advice is worked out in a process with an internal review, partly by species-specifically selected experts, partly in the form of joint seminars. Citation: Sundelöf, A., Florin, A., Rogell, B. and Bolund, E. V., F; Sundblad, G; Strömberg, H; Bergendahl, IA, Sundin, J; Lundström, K; Wikström, K; Magnusson, K; Fetterplace, L; Wennström, L; Ogonowski, M; Bergenius, M; Holmgren, N; Kaljuste, O; Bohman, P; Fredriksson, R; Eiler, S; Larsson, S; Axenrot, T; Östman, Ö. (2022). Havs-och vattenmyndigheten.
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Report on stock status & management advice for fish & shellfish species in Swedish waters (In Swedish). Open Access in DiVA - http://havochvatten.diva-portal.org/smash/record.jsf?pid=diva2%3A1531416&dswid=9443
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Populations of fish eating mammals (primarily seals) and birds have increased in the Baltic Sea and there is concern that their consumption reduces fish stocks and has negative impact on the fishery. Based primarily on published data on fisheries' landings and abundances, consumption and diets of birds and seals around year 2010, we compare consumption of commercial fish species by seals (1*10 5 metric tons per year) and birds (1*10 5 tons) to the catch in the commercial and recreational fishery (7*10 5 tons), and when applicable at the geographical resolution of ICES subdivisions. The large populations of herring (Clupea harengus), sprat (Sprattus sprattus) and cod (Gadus morhua), primarily inhabit offshore areas and are mainly caught by the fishery. Predation by birds and mammals likely has little impact on these stocks. For these species, seals and birds may be negatively impacted by competition from the fishery. In the central and southern Baltic, seals and birds consume about as much flatfish as is caught by the fishery and competition is possible. Birds and seals consume 2-3 times as much coastal fish as is caught in the fishery. Many of the coastal species are not much targeted by the fishery (e.g. eelpout Zoarces viviparus, roach Rutilus rutilus and ruffe Gymnocephalus cernua), while other species used by wildlife are important to the fishery (e.g. perch Perca fluviatilis and whitefish Coregonus spp.) and competition between wildlife and the fishery is likely, at least locally. Estimated wildlife consumption of pike (Esox lucius), sea trout (Salmo trutta) and pikeperch (Sander lucioperca) varies among ICES subdivisions and the degree of competition for these species will likely differ among areas. Our results indicate that competition between wildlife and fisheries need to be addressed in basic ecosystem research, management and conservation. This requires improved quantitative data on wildlife diets, abundances and fish production.
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Ecological indicators are increasingly used in marine and freshwater management but only few are developed towards full operationalization with known patterns of variability and documented responses to natural and anthropogenic environmental drivers. Here, we evaluate potential sources of indicator variability at two different spatial scales in three coastal fish-based indicators of environmental status in the Baltic Sea; abundance of cyprinids, abundance of perch and the proportion of larger perch. The study was performed on a data set covering 41 monitoring areas subject to different levels of anthropogenic impact, at a latitudinal range of 56–66°N and a salinity range of 2–8. Interannual variation was clearly minor relative to spatial variation. Small-scale spatial variation was related to water depth, wave exposure and water temperature. The remaining variation was assessed in relation to differences in natural and anthropogenic drivers between monitoring areas. Cyprinids showed a clear inverse relationship to water transparency, which was used as a proxy for eutrophication, indicating increased abundances in nutrient enriched areas. None of the indicators showed an expected negative relationship to the level of coastal commercial fisheries catches. Rather, a positive relationship for Perch suggested that the coastal fisheries were concentrated to areas with strong perch populations in the studied areas. The effect of salinity and climate (temperature during the growth season) among monitoring areas were small. The results emphasize the importance of assigning area-specific boundary levels to define good environmental status in the coastal fish indicators, in order to account for natural sources of variability. Further, although long-term monitoring in reference areas is crucial for obtaining a historical baseline, our results suggest that the status assessment of coastal fish would generally gain precision by increasingly including spatially based assessments. We propose that similar analytical approaches could be applied to other ecosystem components, especially in naturally heterogenic environments, in order to separate indicator variability attributed to potential anthropogenic impact.
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To reveal the temporal and spatial utilization of a preferred nursery ground habitat by 0-group turbot and flounder in the Baltic Sea, sampling was conducted in six sandy bays in early-mid-July to early-mid-September 2003-2005 off the coast of Gotland (ICES SD 27 & 28-2). Settlement and peak abundance of turbot occurred from late July-early August to early September and from mid-August to early September, respectively. Settlement of flounder occurred from early-mid-July with decreasing numbers over time, except in 2005. Peak abundance of 0-group flounder occurred in late July-early August to mid-September, suggesting a considerable temporal overlap with 0-group turbot. 0-group turbot and flounder also overlapped in respect to depth with preference for 0.2 and 0.6 m over 1 m. The spatial and temporal overlap of the species was verified by a logistic regression analysis; the probability of sampling 0-group flounder when 0-group turbot was caught in a haul was 0.84 (0.80-0.87, 95% CI).
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Gårdmark, A., Östman, Ö., Nielsen, A., Lundström K., Karlsson O., Pönni, J., and Aho, T. 2012. Does predation by grey seals (Halichoerus grypus) affect Bothnian Sea herring stock estimates? – ICES Journal of Marine Science, 69: . Mortality of small pelagic fish due to marine mammals is generally considered to be low compared with other sources of mortality. With recent recoveries of marine mammal predators worldwide, this may no longer hold. The grey seal (Halichoerus grypus) population in the Bothnian Sea has increased fivefold since 1985. Its main prey, herring (Clupea harrengus), is a key species for fisheries in the region. Yet, current stock assessments assume constant natural mortality, leading to a risk of biased stock estimates with increasing predation and misleading analyses of herring population dynamics. We estimated grey seal predation from diet data and reanalysed herring spawning stock biomass (SSB) during 1973–2009. Accounting for predation increased the herring SSB 16% (maximum 19%), but this was within the confidence intervals when ignoring predation. Although mortality in older individuals was inflated when accounting for seal predation, this did not change the conclusions about drivers of herring dynamics. Accounting for grey seal predation is important for abundance estimates of old herring, but currently not for SSB estimates, given the great uncertainties in the standard assessment. The grey seal impact on Bothnian Sea herring will need to be reassessed if stock age composition, grey seal feeding preferences, or total stock development change.
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Mäntyniemi, S., Romakkaniemi, A., Dannewitz, J., Palm, S., Pakarinen, T., Pulkkinen, H., Gårdmark, A., and Karlsson, O. 2012. Both predation and feeding opportunities may explain changes in survival of Baltic salmon post-smolts. – ICES Journal of Marine Science, 69: 1574–1579. The survival of wild and hatchery-reared post-smolts of salmon (Salmo salar) in the Baltic Sea has declined since the 1990s. Direct observations of the processes affecting survival are, however, lacking. Here, the importance of food availability and predation in regulating post-smolt survival is analysed. Based on previous studies, the following explanatory variables were selected: (i) availability of herring (Clupea harengus membras) recruits in the Gulf of Bothnia (Bothnian Sea, Bothnian Bay) in the northern Baltic Sea; (ii) sprat (Sprattus sprattus balticus) and herring abundance in the southern Baltic Sea; and (iii) abundance of grey seal (Halichoerus grypus) along the post-smolt migration route. Bayesian analysis was used to estimate the relative probability of each of the 32 combinations of these variables and revealed that the model including grey seal abundance and herring recruits per post-smolt had the highest posterior probability and a high coefficient of determination. The results suggest that the declining trend in post-smolt survival is explained by the increased number of grey seals, whereas the annual variation in survival coincides with variation in the recruitment of Bothnian Sea herring. However, it remains uncertain whether the observed correlations arise from direct causalities or other mechanisms.
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In the brackish water Baltic Sea turbot spawn at ~ 6-9 psu along the coast and on offshore banks in ICES SD 24-29, with salinity influencing the reproductive success. The potential fecundity (the stock of vitellogenic oocytes in the pre-spawning ovary), egg size (diameter and dry weight of artificially fertilized 1-day-old eggs) and gonad dry weight were assessed for fish sampled in SD 25 and SD 28. Multiple regression analysis identified somatic weight, or total length in combination with Fulton's condition factor, as main predictors of fecundity and gonad dry weight with stage of maturity (oocyte packing density or leading cohort) as an additional predictor. For egg size, somatic weight was identified as main predictor while otolith weight (proxy for age) was an additional predictor. Univariate analysis using GLM revealed significantly higher fecundity and gonad dry weight for turbot from SD 28 (3378-3474 oocytes/g somatic weight) compared to those from SD 25 (2343 oocytes/g somatic weight), with no difference in egg size (1.05 ± 0.03 mm diameter and 46.8 ± 6.5 μg dry weight; mean ± sd). The difference in egg production matched egg survival probabilities in relation to salinity conditions suggesting selection for higher fecundity as a consequence of poorer reproductive success at lower salinities. This supports the hypothesis of higher size-specific fecundity towards the limit of the distribution of a species as an adaptation to harsher environmental conditions and lower offspring survival probabilities. Within SD 28 comparisons were made between two major fishing areas targeting spawning aggregations and a marine protected area without fishing. The outcome was inconclusive and is discussed with respect to potential fishery induced effects, effects of the salinity gradient, effects of specific year-classes, and effects of maturation status of sampled fish.
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The size of the year 2000 summer population of grey seals in the Baltic Sea was estimated using identification of individual seals from photographs taken over a period of 6 years. Photos were taken at haul-out sites within all major grey seal areas in the semi-closed Baltic Sea. The point estimate is 15,631, based on a value for annual survival of identification markings of 0.904, which was also estimated using the photo-id data, with 95% confidence limits from 9,592 to 19,005. The estimate is subject to an unknown, but probably small, upward bias resulting from the risk of failure to identify all individuals in the photographs used for the analysis. An estimated min- imum of 15,950 seals were counted at moulting haul-outs in 2003, which thus provides a low- er bound on the population size in that year and represents 80% of the photo-id point estimate. Hiby, L., Lundberg, T., Karlsson, O., Watkins, J., Jüssi, M., Jüssi, I. and Helander, B. 2007. Estimates of the size of the Baltic grey seal population based on photo-identification data. NAMMCO Sci. Publ. 6:163-175.
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We examined the digestive tract contents from 145 grey seals (Halichoerus grypus) collected be- tween 2001 and 2004 in the Baltic Sea. We compensated for biases introduced by erosion of otoliths, both by using additional hard-part structures other than otoliths, and species-specific size and nu- merical correction factors. In the absence of numerical correction factors based on feeding experi- ments for some species, we used correction factors based on a relationship between otolith recovery rate and otolith width. A total of 24 prey taxa were identified but only a few species contributed substantially to the diet. The estimated diet composition was, independently of the prey number estimation method and diet composition estimation model used, dominated by herring (Clupea harengus), both by numbers and biomass. In addition to herring, common whitefish (Coregonus lavaretus) and sprat (Sprattus sprattus) were important prey, but cyprinids (Cyprinidae), eelpout (Zoarces viviparus), flounder (Platichtys flesus) and salmon (Salmo salar) also contributed sig- nificantly. Our results indicated dietary differences between grey seals of different age as well as between seals from the northern (Gulf of Bothnia) and the southern (Baltic Proper) Baltic Sea. Lundström, K., Hjerne, O., Alexandersson, A. and Karlsson O. 2007. Estimation of grey seal (Halichoerus grypus) diet composition in the Baltic Sea. NAMMCO Sci. Publ. 6:177-196.
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The brackish water of the Baltic Sea, with decreasing salinity from the west to the east and from the south to the north, is a borderline area for cod Gadus morhua. The major stock, the eastern Baltic cod, has decreased substantially during the last decade. A discussion concerning the possibility of immigration of cod and the potential of stock interactions has evolved. The present study was conducted in order to elucidate if differences in salinity requirements for successful spawning exist between the eastern Baltic cod and the western Belt Sea cod, and if adaptation to ambient salinity is possible. Activation of the spermatozoa occurred at greater than or equal to 11 to 12 psu (practical salinity units) for Baltic cod and at greater than or equal to 15 to 16 psu for Belt Sea cod. Neutral egg buoyancy was obtained at 14.5 +/- 1.2 psu and at 20 to 22 psu respectively. Transfer of fish from marine to brackish water conditions showed that these characteristics remained essentially the same; activation of spermatozoa occurred at greater than or equal to 14 to 15 psu and neutral egg buoyancy at 19 to 21 psu. The results suggest that these characteristics are specific to populations. Regarding hydrographic conditions in the spawning areas of cod in the Baltic, the results suggest that stock interactions may be possible in the western Baltic spawning areas where salinity requirements for both stocks are fulfilled, but not in the eastern spawning areas as low salinity prevents successful spawning of Belt Sea cod. Salinity and oxygen conditions in the Baltic vary with highly irregular saline water inflows. Periods of stagnation without inflows may, due to decreasing salinity, e.g. <15 psu during the last stagnation period, act as an ecological barrier separating the stocks.
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Cormorants and humans are purported to compete for fish resources. Recent increases in cormorant populations in western Europe have led to new conflicts between fishermen and nature conservationists, a situation which has stimulated research into the food requirements of these seabirds. However, most dietary studies are based on stomach content or pellet analysis. Both these methods are biased. We used a time-budget model to calculate the energy requirements of great cormorants Phalacrocorax carbo sinensis breeding in Schleswig-Holstein, Germany. The time budgets of the birds were recorded for different breeding phases and the energetic costs of the different activities determined through respirometric measurements or by using values derived from the literature. The food requirements of great cormorants during incubation were calculated to be 238 g adult(-1) d(-1). These requirements rise to 316 g d(-1) during the rearing of young chicks and to 588 g d(-1) during rearing of downy chicks. Human disturbance causing great cormorants to fly off their nests entails an additional consumption of 23 g fish per bird or ca 23 kg per disturbance event for a typical colony.
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