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data-trace="false" data-dom-id="Pill-react-component-bb3cdb7b-c769-4c0b-8d88-fb0c589859f8"></div> <div id="Pill-react-component-bb3cdb7b-c769-4c0b-8d88-fb0c589859f8"></div> </a></div></div></div></div><div class="right-panel-container"><div class="user-content-wrapper"><div class="uploads-container" id="social-redesign-work-container"><div class="upload-header"><h2 class="ds2-5-heading-sans-serif-xs">Uploads</h2></div><div class="documents-container backbone-social-profile-documents" style="width: 100%;"><div class="u-taCenter"></div><div class="profile--tab_content_container js-tab-pane tab-pane active" id="all"><div class="profile--tab_heading_container js-section-heading" data-section="Papers" id="Papers"><h3 class="profile--tab_heading_container">Papers by Darius Daunys</h3></div><div class="js-work-strip profile--work_container" data-work-id="117361992"><div class="profile--work_thumbnail hidden-xs"><a class="js-work-strip-work-link" data-click-track="profile-work-strip-thumbnail" href="https://www.academia.edu/117361992/Species_Strategy_Near_Its_Boundary_theMarenzelleria_cf_viridis_Polychaeta_Spionidae_Case_in_the_South_Eastern_Baltic_Sea"><img alt="Research paper thumbnail of Species Strategy Near Its Boundary: theMarenzelleria cf.viridis (Polychaeta, Spionidae) Case in the South-Eastern Baltic Sea" class="work-thumbnail" src="https://a.academia-assets.com/images/blank-paper.jpg" /></a></div><div class="wp-workCard wp-workCard_itemContainer"><div class="wp-workCard_item wp-workCard--title"><a class="js-work-strip-work-link text-gray-darker" data-click-track="profile-work-strip-title" href="https://www.academia.edu/117361992/Species_Strategy_Near_Its_Boundary_theMarenzelleria_cf_viridis_Polychaeta_Spionidae_Case_in_the_South_Eastern_Baltic_Sea">Species Strategy Near Its Boundary: theMarenzelleria cf.viridis (Polychaeta, Spionidae) Case in the South-Eastern Baltic Sea</a></div><div class="wp-workCard_item"><span>International Review of Hydrobiology</span><span>, Nov 1, 2000</span></div><div class="wp-workCard_item"><span class="js-work-more-abstract-truncated">The invasive polychaete worm Marenzelleria cf. viridis spread into various coastal habitats in th...</span><a class="js-work-more-abstract" data-broccoli-component="work_strip.more_abstract" data-click-track="profile-work-strip-more-abstract" href="javascript:;"><span> more </span><span><i class="fa fa-caret-down"></i></span></a><span class="js-work-more-abstract-untruncated hidden">The invasive polychaete worm Marenzelleria cf. viridis spread into various coastal habitats in the Baltic Sea. The estimated limits regarding its salinity tolerance obtained from different laboratory experiments alone only rarely explain the actual species boundaries in nature, e.g. in the Curonian lagoon. Therefore, a field study was carried out aimed at to define, how a population maintains itself in a dynamic estuarine habitat with rapid and irregular changing salinity (annual mean 3 PSU, range of variation from 0 to 7.5 PSU). Under these conditions the species females reached maturity. However, during the final reproduction phase their spawning was delayed and oosorption started. It was estimated that roughly 0.05% of the nearby sea population offspring was transported to the estuary but most of the pelagic larvae were not able to develop beyond the 10 segments stage. It seems that the estuarine benthic population is maintained by migration of the species benthic stages. This mode probably is more efficient in comparison to dispersal by pelagic larvae when a species colonises stressed and dynamic environments.</span></div><div class="wp-workCard_item wp-workCard--actions"><span class="work-strip-bookmark-button-container"></span><span class="wp-workCard--action visible-if-viewed-by-owner inline-block" style="display: none;"><span class="js-profile-work-strip-edit-button-wrapper profile-work-strip-edit-button-wrapper" data-work-id="117361992"><a class="js-profile-work-strip-edit-button" tabindex="0"><span><i class="fa fa-pencil"></i></span><span>Edit</span></a></span></span><span id="work-strip-rankings-button-container"></span></div><div class="wp-workCard_item wp-workCard--stats"><span><span><span class="js-view-count view-count u-mr2x" data-work-id="117361992"><i class="fa fa-spinner fa-spin"></i></span><script>$(function () { var workId = 117361992; window.Academia.workViewCountsFetcher.queue(workId, function (count) { var description = window.$h.commaizeInt(count) + " " + window.$h.pluralize(count, 'View'); $(".js-view-count[data-work-id=117361992]").text(description); $(".js-view-count[data-work-id=117361992]").attr('title', description).tooltip(); }); });</script></span></span><span><span class="percentile-widget hidden"><span class="u-mr2x work-percentile"></span></span><script>$(function () { var workId = 117361992; window.Academia.workPercentilesFetcher.queue(workId, function (percentileText) { var container = $(".js-work-strip[data-work-id='117361992']"); container.find('.work-percentile').text(percentileText.charAt(0).toUpperCase() + percentileText.slice(1)); container.find('.percentile-widget').show(); container.find('.percentile-widget').removeClass('hidden'); }); });</script></span><span><script>$(function() { new Works.PaperRankView({ workId: 117361992, container: "", }); });</script></span></div><div id="work-strip-premium-row-container"></div></div></div><script> require.config({ waitSeconds: 90 })(["https://a.academia-assets.com/assets/wow_profile-f77ea15d77ce96025a6048a514272ad8becbad23c641fc2b3bd6e24ca6ff1932.js","https://a.academia-assets.com/assets/work_edit-ad038b8c047c1a8d4fa01b402d530ff93c45fee2137a149a4a5398bc8ad67560.js"], function() { // from javascript_helper.rb var dispatcherData = {} if (false){ window.WowProfile.dispatcher = window.WowProfile.dispatcher || _.clone(Backbone.Events); dispatcherData = { dispatcher: window.WowProfile.dispatcher, downloadLinkId: "-1" } } $('.js-work-strip[data-work-id=117361992]').each(function() { if (!$(this).data('initialized')) { new WowProfile.WorkStripView({ el: this, workJSON: {"id":117361992,"title":"Species Strategy Near Its Boundary: theMarenzelleria cf.viridis (Polychaeta, Spionidae) Case in the South-Eastern Baltic Sea","translated_title":"","metadata":{"abstract":"The invasive polychaete worm Marenzelleria cf. viridis spread into various coastal habitats in the Baltic Sea. The estimated limits regarding its salinity tolerance obtained from different laboratory experiments alone only rarely explain the actual species boundaries in nature, e.g. in the Curonian lagoon. Therefore, a field study was carried out aimed at to define, how a population maintains itself in a dynamic estuarine habitat with rapid and irregular changing salinity (annual mean 3 PSU, range of variation from 0 to 7.5 PSU). Under these conditions the species females reached maturity. However, during the final reproduction phase their spawning was delayed and oosorption started. It was estimated that roughly 0.05% of the nearby sea population offspring was transported to the estuary but most of the pelagic larvae were not able to develop beyond the 10 segments stage. It seems that the estuarine benthic population is maintained by migration of the species benthic stages. This mode probably is more efficient in comparison to dispersal by pelagic larvae when a species colonises stressed and dynamic environments.","publisher":"Wiley","publication_date":{"day":1,"month":11,"year":2000,"errors":{}},"publication_name":"International Review of Hydrobiology"},"translated_abstract":"The invasive polychaete worm Marenzelleria cf. viridis spread into various coastal habitats in the Baltic Sea. The estimated limits regarding its salinity tolerance obtained from different laboratory experiments alone only rarely explain the actual species boundaries in nature, e.g. in the Curonian lagoon. Therefore, a field study was carried out aimed at to define, how a population maintains itself in a dynamic estuarine habitat with rapid and irregular changing salinity (annual mean 3 PSU, range of variation from 0 to 7.5 PSU). Under these conditions the species females reached maturity. However, during the final reproduction phase their spawning was delayed and oosorption started. It was estimated that roughly 0.05% of the nearby sea population offspring was transported to the estuary but most of the pelagic larvae were not able to develop beyond the 10 segments stage. It seems that the estuarine benthic population is maintained by migration of the species benthic stages. This mode probably is more efficient in comparison to dispersal by pelagic larvae when a species colonises stressed and dynamic environments.","internal_url":"https://www.academia.edu/117361992/Species_Strategy_Near_Its_Boundary_theMarenzelleria_cf_viridis_Polychaeta_Spionidae_Case_in_the_South_Eastern_Baltic_Sea","translated_internal_url":"","created_at":"2024-04-11T10:54:31.887-07:00","preview_url":null,"current_user_can_edit":null,"current_user_is_owner":null,"owner_id":64309884,"coauthors_can_edit":true,"document_type":"paper","co_author_tags":[],"downloadable_attachments":[],"slug":"Species_Strategy_Near_Its_Boundary_theMarenzelleria_cf_viridis_Polychaeta_Spionidae_Case_in_the_South_Eastern_Baltic_Sea","translated_slug":"","page_count":null,"language":"en","content_type":"Work","owner":{"id":64309884,"first_name":"Darius","middle_initials":null,"last_name":"Daunys","page_name":"DariusDaunys","domain_name":"independent","created_at":"2017-05-15T05:34:19.853-07:00","display_name":"Darius Daunys","url":"https://independent.academia.edu/DariusDaunys"},"attachments":[],"research_interests":[{"id":7710,"name":"Biology","url":"https://www.academia.edu/Documents/in/Biology"},{"id":9846,"name":"Ecology","url":"https://www.academia.edu/Documents/in/Ecology"},{"id":11872,"name":"Hydrobiology","url":"https://www.academia.edu/Documents/in/Hydrobiology"},{"id":64336,"name":"Population","url":"https://www.academia.edu/Documents/in/Population"},{"id":85707,"name":"Habitat","url":"https://www.academia.edu/Documents/in/Habitat"},{"id":379570,"name":"Estuary","url":"https://www.academia.edu/Documents/in/Estuary"},{"id":410933,"name":"Baltic Sea","url":"https://www.academia.edu/Documents/in/Baltic_Sea"},{"id":880030,"name":"Polychaete","url":"https://www.academia.edu/Documents/in/Polychaete"},{"id":3816195,"name":"pelagic zone","url":"https://www.academia.edu/Documents/in/pelagic_zone"}],"urls":[{"id":41019524,"url":"https://doi.org/10.1002/1522-2632(200011)85:5/6%3C639::aid-iroh639%3E3.0.co;2-g"}]}, dispatcherData: dispatcherData }); $(this).data('initialized', true); } }); $a.trackClickSource(".js-work-strip-work-link", "profile_work_strip") }); </script> <div class="js-work-strip profile--work_container" data-work-id="117361991"><div class="profile--work_thumbnail hidden-xs"><a class="js-work-strip-work-link" data-click-track="profile-work-strip-thumbnail" href="https://www.academia.edu/117361991/Application_of_underwater_imagery_for_the_description_of_upper_sublittoral_benthic_communities_in_glaciated_and_ice_free_Arctic_fjords"><img alt="Research paper thumbnail of Application of underwater imagery for the description of upper sublittoral benthic communities in glaciated and ice-free Arctic fjords" class="work-thumbnail" src="https://attachments.academia-assets.com/113238173/thumbnails/1.jpg" /></a></div><div class="wp-workCard wp-workCard_itemContainer"><div class="wp-workCard_item wp-workCard--title"><a class="js-work-strip-work-link text-gray-darker" data-click-track="profile-work-strip-title" href="https://www.academia.edu/117361991/Application_of_underwater_imagery_for_the_description_of_upper_sublittoral_benthic_communities_in_glaciated_and_ice_free_Arctic_fjords">Application of underwater imagery for the description of upper sublittoral benthic communities in glaciated and ice-free Arctic fjords</a></div><div class="wp-workCard_item"><span>Polar Biology</span><span>, Nov 2, 2022</span></div><div class="wp-workCard_item wp-workCard--actions"><span class="work-strip-bookmark-button-container"></span><a id="a6677fd4863099d0c41267d7cb8efa31" class="wp-workCard--action" rel="nofollow" data-click-track="profile-work-strip-download" data-download="{"attachment_id":113238173,"asset_id":117361991,"asset_type":"Work","button_location":"profile"}" href="https://www.academia.edu/attachments/113238173/download_file?st=MTczMjczMzU3MCw4LjIyMi4yMDguMTQ2&s=profile"><span><i class="fa fa-arrow-down"></i></span><span>Download</span></a><span class="wp-workCard--action visible-if-viewed-by-owner inline-block" style="display: none;"><span class="js-profile-work-strip-edit-button-wrapper profile-work-strip-edit-button-wrapper" data-work-id="117361991"><a class="js-profile-work-strip-edit-button" tabindex="0"><span><i class="fa fa-pencil"></i></span><span>Edit</span></a></span></span><span id="work-strip-rankings-button-container"></span></div><div class="wp-workCard_item wp-workCard--stats"><span><span><span class="js-view-count view-count u-mr2x" data-work-id="117361991"><i class="fa fa-spinner fa-spin"></i></span><script>$(function () { var workId = 117361991; window.Academia.workViewCountsFetcher.queue(workId, function (count) { var description = window.$h.commaizeInt(count) + " " + window.$h.pluralize(count, 'View'); $(".js-view-count[data-work-id=117361991]").text(description); $(".js-view-count[data-work-id=117361991]").attr('title', description).tooltip(); }); });</script></span></span><span><span class="percentile-widget hidden"><span class="u-mr2x work-percentile"></span></span><script>$(function () { var workId = 117361991; window.Academia.workPercentilesFetcher.queue(workId, function (percentileText) { var container = $(".js-work-strip[data-work-id='117361991']"); container.find('.work-percentile').text(percentileText.charAt(0).toUpperCase() + percentileText.slice(1)); container.find('.percentile-widget').show(); container.find('.percentile-widget').removeClass('hidden'); }); });</script></span><span><script>$(function() { new Works.PaperRankView({ workId: 117361991, container: "", }); });</script></span></div><div id="work-strip-premium-row-container"></div></div></div><script> require.config({ waitSeconds: 90 })(["https://a.academia-assets.com/assets/wow_profile-f77ea15d77ce96025a6048a514272ad8becbad23c641fc2b3bd6e24ca6ff1932.js","https://a.academia-assets.com/assets/work_edit-ad038b8c047c1a8d4fa01b402d530ff93c45fee2137a149a4a5398bc8ad67560.js"], function() { // from javascript_helper.rb var dispatcherData = {} if (true){ window.WowProfile.dispatcher = window.WowProfile.dispatcher || _.clone(Backbone.Events); 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One such technique is underwater imagery, which has grown in popularity in recent decades based on its effectiveness in hard-to-reach places. We demonstrate that an underwater video mosaic can be a reliable method for comparative analysis of Arctic habitats under the glacier in uence and glacier in uence-free habitats. The lming was carried out in the upper sublittoral (2-65 m) of Hornsund and Isfjorden areas, representing two ice-free and two glaciated bays. Video footage was obtained using an ROV mounted and \"drop-down\" video cameras and transformed into 148 video mosaics. Based on the lowest possible taxonomic level, 31 biological features (morphospecies) were identi ed and ascribed to benthic functional groups based on their feeding and mobility type. The morphospecies and functional groups were used for the comparative analysis of benthic communities. The study found that melting glaciers have a stronger impact on the structure of benthic communities across geographical areas. Morphological and functional composition of macrofauna re ected conditions in glacier in uence and in uence-free, and turbid water riverine bays. We discovered greater abundances of motile scavengers in glacier in uence bays whereas glacier in uence-free bay had more sessile suspension lters and glacier in uence-free riverine bay was dominated by discreetly motile and deposit feeders. Underwater imagery mosaics have proven to be a fairly reliable tool for eldwork-e cient quantitative characterization of benthic communities in the hard-to-reach Arctic's upper sublittoral. Highlights Combination of underwater imagery and morphospecies approaches provides su cient data to quantify the dominant macrobenthos forms in the arctic fjords. The morphospecies approach makes it possible to reveal the differences in the functional structure of the benthos in the periglacial and glacier in uence-free areas of the upper sublittoral. Underwater imagery may be recommended for eldwork-e cient assessment of benthos in conditions of complex bottom topography and the presence of oating ice. Consequently, this study highlights a greater in uence of melting glaciers on the structure of benthic communities than across geographical areas","publication_date":{"day":2,"month":11,"year":2022,"errors":{}},"publication_name":"Polar 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Sciences","url":"https://www.academia.edu/Documents/in/Biological_Sciences"},{"id":68049,"name":"Arctic","url":"https://www.academia.edu/Documents/in/Arctic"},{"id":79704,"name":"Underwater","url":"https://www.academia.edu/Documents/in/Underwater"},{"id":181597,"name":"Root-Mean Square Error","url":"https://www.academia.edu/Documents/in/Root-Mean_Square_Error"},{"id":322448,"name":"Fjord","url":"https://www.academia.edu/Documents/in/Fjord"},{"id":352542,"name":"Glacier","url":"https://www.academia.edu/Documents/in/Glacier"},{"id":512395,"name":"Polar Biology","url":"https://www.academia.edu/Documents/in/Polar_Biology"},{"id":1660649,"name":"Bay","url":"https://www.academia.edu/Documents/in/Bay"}],"urls":[{"id":41019523,"url":"https://www.researchsquare.com/article/rs-1808509/latest.pdf"}]}, dispatcherData: dispatcherData }); $(this).data('initialized', true); } }); $a.trackClickSource(".js-work-strip-work-link", "profile_work_strip") }); </script> <div class="js-work-strip profile--work_container" data-work-id="117361990"><div class="profile--work_thumbnail hidden-xs"><a class="js-work-strip-work-link" data-click-track="profile-work-strip-thumbnail" href="https://www.academia.edu/117361990/Effect_of_Species_Invasion_on_Transport_of_Solutes_at_Different_Levels_of_Soft_Sediment_Macrofauna_Diversity_Results_from_an_Experimental_Approach"><img alt="Research paper thumbnail of Effect of Species Invasion on Transport of Solutes at Different Levels of Soft Sediment Macrofauna Diversity: Results from an Experimental Approach" class="work-thumbnail" src="https://attachments.academia-assets.com/113238171/thumbnails/1.jpg" /></a></div><div class="wp-workCard wp-workCard_itemContainer"><div class="wp-workCard_item wp-workCard--title"><a class="js-work-strip-work-link text-gray-darker" data-click-track="profile-work-strip-title" href="https://www.academia.edu/117361990/Effect_of_Species_Invasion_on_Transport_of_Solutes_at_Different_Levels_of_Soft_Sediment_Macrofauna_Diversity_Results_from_an_Experimental_Approach">Effect of Species Invasion on Transport of Solutes at Different Levels of Soft Sediment Macrofauna Diversity: Results from an Experimental Approach</a></div><div class="wp-workCard_item"><span>Water</span><span>, Jul 25, 2019</span></div><div class="wp-workCard_item wp-workCard--actions"><span class="work-strip-bookmark-button-container"></span><a id="ab117c8fe91aff901f4ccb2f2fb201d6" class="wp-workCard--action" rel="nofollow" data-click-track="profile-work-strip-download" data-download="{"attachment_id":113238171,"asset_id":117361990,"asset_type":"Work","button_location":"profile"}" href="https://www.academia.edu/attachments/113238171/download_file?st=MTczMjczMzU3MCw4LjIyMi4yMDguMTQ2&s=profile"><span><i class="fa fa-arrow-down"></i></span><span>Download</span></a><span class="wp-workCard--action 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To comparatively analyze the effects of an exotic and a native polychaete burrower on sediment-water exchanges, two laboratory experiments were performed. In the first experiment, the invasive spionid polychaete Marenzelleria neglecta was added to defaunated sediments and fluxes of the inert tracer (bromide, Br −) were measured to quantify the effects of irrigation by the worm on the tracer transport. In the second experiment, M. neglecta or the native polychaete Hediste diversicolor were introduced to a relatively diverse Baltic soft-bottom macrofauna community. The effect of species on fluxes of reactive solutes (ammonium, NH 4 +, and phosphate, PO 4 3−) and transport rates of Br − was estimated. The results indicate different invasion effects depending on the characteristics of the recipient habitat. In defaunated sediments, a single specimen of M. neglecta significantly enhanced originally low solute exchange rates. Total tracer flux was significantly enhanced over diffusive flux by a factor of 1.6 ± 0.14 (n = 3). In natural sediments, on the other hand, the addition of either M. neglecta or H. diversicolor had no statistically significant effects on benthic fluxes. Tracer flux estimates between control and treatment incubations differed by less than 10% on average, and both reactive solutes tended to increase by 10 to 40% after additions. One specimen of M. neglecta in cores with defaunated sediment generated approximately 20% of the tracer flux produced by the relatively diverse macrofauna community. Estimated net tracer fluxes in two experiments corresponded well with the number of adult polychaetes found in sediments (r 2 = 0.73, p = 0.005, n = 12). The invasive M. neglecta produced a small effect on fluxes in biodiverse sediments, comparable to those of H. diversicolor, but it may deeply alter porewater chemistry in azoic sediment. As M. neglecta tolerates chemically reduced and sulphidic conditions, its bioirigation may favor sediment reoxidation and ultimately the recolonization by less tolerant, native species.","publication_date":{"day":25,"month":7,"year":2019,"errors":{}},"publication_name":"Water","grobid_abstract_attachment_id":113238171},"translated_abstract":null,"internal_url":"https://www.academia.edu/117361990/Effect_of_Species_Invasion_on_Transport_of_Solutes_at_Different_Levels_of_Soft_Sediment_Macrofauna_Diversity_Results_from_an_Experimental_Approach","translated_internal_url":"","created_at":"2024-04-11T10:54:31.456-07:00","preview_url":null,"current_user_can_edit":null,"current_user_is_owner":null,"owner_id":64309884,"coauthors_can_edit":true,"document_type":"paper","co_author_tags":[],"downloadable_attachments":[{"id":113238171,"title":"","file_type":"pdf","scribd_thumbnail_url":"https://attachments.academia-assets.com/113238171/thumbnails/1.jpg","file_name":"pdf.pdf","download_url":"https://www.academia.edu/attachments/113238171/download_file?st=MTczMjczMzU3MCw4LjIyMi4yMDguMTQ2&","bulk_download_file_name":"Effect_of_Species_Invasion_on_Transport.pdf","bulk_download_url":"https://d1wqtxts1xzle7.cloudfront.net/113238171/pdf-libre.pdf?1712860358=\u0026response-content-disposition=attachment%3B+filename%3DEffect_of_Species_Invasion_on_Transport.pdf\u0026Expires=1732737170\u0026Signature=cln1wpZ7qgrDnZCmipby1lvhVRY4HmblsT3w5eZV0yXQeLJPrH5fZZtV6e~BRdrPkQrtdB2-VD0BUCzgIdxNQV8aQAKb20nqY94WwJvIOnV459Gk7CSnwArALnvXh4qs-EKAUpbuDJcqzrFrt55Mn0qv6SENJXm8iX33MJUwgP~DyY2juFxeScVryCDeXmLHLIOC00G4v9451BMwkWC0Iqdh8bySXGoxg1-NmjZh9JDnKBg8VI4vZw~wkHLs7-PimUyMZNmQNGWcJya-e~qVZeaF0odMxRlnN9cwQiOl30fOuMdZd9~TzDqMDTsrqCsCj4dJJqtv7px1SHONFGIQdQ__\u0026Key-Pair-Id=APKAJLOHF5GGSLRBV4ZA"}],"slug":"Effect_of_Species_Invasion_on_Transport_of_Solutes_at_Different_Levels_of_Soft_Sediment_Macrofauna_Diversity_Results_from_an_Experimental_Approach","translated_slug":"","page_count":18,"language":"en","content_type":"Work","owner":{"id":64309884,"first_name":"Darius","middle_initials":null,"last_name":"Daunys","page_name":"DariusDaunys","domain_name":"independent","created_at":"2017-05-15T05:34:19.853-07:00","display_name":"Darius Daunys","url":"https://independent.academia.edu/DariusDaunys"},"attachments":[{"id":113238171,"title":"","file_type":"pdf","scribd_thumbnail_url":"https://attachments.academia-assets.com/113238171/thumbnails/1.jpg","file_name":"pdf.pdf","download_url":"https://www.academia.edu/attachments/113238171/download_file?st=MTczMjczMzU3MCw4LjIyMi4yMDguMTQ2&","bulk_download_file_name":"Effect_of_Species_Invasion_on_Transport.pdf","bulk_download_url":"https://d1wqtxts1xzle7.cloudfront.net/113238171/pdf-libre.pdf?1712860358=\u0026response-content-disposition=attachment%3B+filename%3DEffect_of_Species_Invasion_on_Transport.pdf\u0026Expires=1732737170\u0026Signature=cln1wpZ7qgrDnZCmipby1lvhVRY4HmblsT3w5eZV0yXQeLJPrH5fZZtV6e~BRdrPkQrtdB2-VD0BUCzgIdxNQV8aQAKb20nqY94WwJvIOnV459Gk7CSnwArALnvXh4qs-EKAUpbuDJcqzrFrt55Mn0qv6SENJXm8iX33MJUwgP~DyY2juFxeScVryCDeXmLHLIOC00G4v9451BMwkWC0Iqdh8bySXGoxg1-NmjZh9JDnKBg8VI4vZw~wkHLs7-PimUyMZNmQNGWcJya-e~qVZeaF0odMxRlnN9cwQiOl30fOuMdZd9~TzDqMDTsrqCsCj4dJJqtv7px1SHONFGIQdQ__\u0026Key-Pair-Id=APKAJLOHF5GGSLRBV4ZA"},{"id":113238172,"title":"","file_type":"pdf","scribd_thumbnail_url":"https://attachments.academia-assets.com/113238172/thumbnails/1.jpg","file_name":"pdf.pdf","download_url":"https://www.academia.edu/attachments/113238172/download_file","bulk_download_file_name":"Effect_of_Species_Invasion_on_Transport.pdf","bulk_download_url":"https://d1wqtxts1xzle7.cloudfront.net/113238172/pdf-libre.pdf?1712860365=\u0026response-content-disposition=attachment%3B+filename%3DEffect_of_Species_Invasion_on_Transport.pdf\u0026Expires=1732737170\u0026Signature=DQEQX37lwc~QaPxb6yKqFHgrj~KXJTvyREr7QYb45G5a-EZdbvxhEJt2fxniIHtioa5iHhwDEi0azRWsZda-FH9enIu3sb9Qwtu1R2r03monbE5GVcA2c9fyT6EKHvOUwEZgHQ3buJdzmprsTJZrApRihFaRFlc3uJoqFIJSaOaYoVHs~QIVTDuJRkZ-nnw9edlgpCTMIq2zgXXc8c~h~JcxWOGDSR2FIaIhjAr0OHqrnqHHgz4VqyW0BhuBZtjuAJ-krPNLMFtZibmtE6BtIVJpw8~K78Z4gLpAtWgecGaV~7EIgHIQx8~13Yh3I~hSAOTZQG1Z0RMNnjtkBFXbQw__\u0026Key-Pair-Id=APKAJLOHF5GGSLRBV4ZA"}],"research_interests":[{"id":523,"name":"Chemistry","url":"https://www.academia.edu/Documents/in/Chemistry"},{"id":2215,"name":"Water","url":"https://www.academia.edu/Documents/in/Water"},{"id":28235,"name":"Multidisciplinary","url":"https://www.academia.edu/Documents/in/Multidisciplinary"},{"id":95531,"name":"Bioturbation","url":"https://www.academia.edu/Documents/in/Bioturbation"},{"id":192294,"name":"Sediment","url":"https://www.academia.edu/Documents/in/Sediment"},{"id":880030,"name":"Polychaete","url":"https://www.academia.edu/Documents/in/Polychaete"},{"id":2022507,"name":"Tracer","url":"https://www.academia.edu/Documents/in/Tracer"}],"urls":[{"id":41019522,"url":"https://www.mdpi.com/2073-4441/11/8/1544/pdf?version=1565055315"}]}, dispatcherData: dispatcherData }); $(this).data('initialized', true); } }); $a.trackClickSource(".js-work-strip-work-link", "profile_work_strip") }); </script> <div class="js-work-strip profile--work_container" data-work-id="117361989"><div class="profile--work_thumbnail hidden-xs"><a class="js-work-strip-work-link" data-click-track="profile-work-strip-thumbnail" href="https://www.academia.edu/117361989/Long_term_macrozoobenthos_changes_in_a_shallow_boreal_lagoon_Comparison_of_a_recent_biodiversity_inventory_with_historical_data"><img alt="Research paper thumbnail of Long-term macrozoobenthos changes in a shallow boreal lagoon: Comparison of a recent biodiversity inventory with historical data" class="work-thumbnail" src="https://attachments.academia-assets.com/113238186/thumbnails/1.jpg" /></a></div><div class="wp-workCard wp-workCard_itemContainer"><div class="wp-workCard_item wp-workCard--title"><a class="js-work-strip-work-link text-gray-darker" data-click-track="profile-work-strip-title" href="https://www.academia.edu/117361989/Long_term_macrozoobenthos_changes_in_a_shallow_boreal_lagoon_Comparison_of_a_recent_biodiversity_inventory_with_historical_data">Long-term macrozoobenthos changes in a shallow boreal lagoon: Comparison of a recent biodiversity inventory with historical data</a></div><div class="wp-workCard_item"><span>Limnologica</span><span>, May 1, 2007</span></div><div class="wp-workCard_item wp-workCard--actions"><span class="work-strip-bookmark-button-container"></span><a id="ce98d84b20fd913ddce087d4be6c85e5" class="wp-workCard--action" rel="nofollow" data-click-track="profile-work-strip-download" data-download="{"attachment_id":113238186,"asset_id":117361989,"asset_type":"Work","button_location":"profile"}" href="https://www.academia.edu/attachments/113238186/download_file?st=MTczMjczMzU3MCw4LjIyMi4yMDguMTQ2&s=profile"><span><i class="fa fa-arrow-down"></i></span><span>Download</span></a><span class="wp-workCard--action visible-if-viewed-by-owner inline-block" style="display: none;"><span class="js-profile-work-strip-edit-button-wrapper profile-work-strip-edit-button-wrapper" data-work-id="117361989"><a class="js-profile-work-strip-edit-button" tabindex="0"><span><i class="fa fa-pencil"></i></span><span>Edit</span></a></span></span><span id="work-strip-rankings-button-container"></span></div><div class="wp-workCard_item wp-workCard--stats"><span><span><span class="js-view-count view-count u-mr2x" data-work-id="117361989"><i class="fa fa-spinner fa-spin"></i></span><script>$(function () { var workId = 117361989; 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In this paper, two historical biodiversity datasets (from 1920s and 1950s) and results from the recent inventory are used to trace the long-term changes of the macrozoobenthos in the eutrophic boreal lagoon of the Baltic Sea. In comparison of datasets the highest congruence was obtained for molluscs and malacostracan crustaceans, which also had a similar level of taxonomic emphasis between studies. Considering inconsistencies in methodology and taxonomic determination, only few species extinctions in these groups did likely occur during the last 100 years. Two amphipod species (Gammarus pulex and Gammarus lacustris) were not found during the recent survey, whereas five new species of this taxonomic group occurred in the lagoon since 1950s. The causes of these extinctions remain unclear; however displacement by established new amphipods cannot be excluded. Theodoxus fluviatilis was recently recorded in the very restricted area of the lagoon, while in earlier studies the species was mentioned as common and widely distributed in the water body. On the other hand, 10 gastropod species and 9 bivalves were reported for the first time in the lagoon and most likely have been overlooked in earlier surveys. Approximately 10% of the species have their origin outside the Baltic Sea basin and the number of invasions considerably exceeds the number of likely extinctions. Assessment scheme of such changes is unclear following WFD guidelines, therefore elaboration of a framework for evaluation of the alien species diversity in a context of local biodiversity should attain more effort when implementing the WFD.","publication_date":{"day":1,"month":5,"year":2007,"errors":{}},"publication_name":"Limnologica","grobid_abstract_attachment_id":113238186},"translated_abstract":null,"internal_url":"https://www.academia.edu/117361989/Long_term_macrozoobenthos_changes_in_a_shallow_boreal_lagoon_Comparison_of_a_recent_biodiversity_inventory_with_historical_data","translated_internal_url":"","created_at":"2024-04-11T10:54:31.274-07:00","preview_url":null,"current_user_can_edit":null,"current_user_is_owner":null,"owner_id":64309884,"coauthors_can_edit":true,"document_type":"paper","co_author_tags":[],"downloadable_attachments":[{"id":113238186,"title":"","file_type":"pdf","scribd_thumbnail_url":"https://attachments.academia-assets.com/113238186/thumbnails/1.jpg","file_name":"zettler_und_daunys-2007-limnologica.pdf","download_url":"https://www.academia.edu/attachments/113238186/download_file?st=MTczMjczMzU3MCw4LjIyMi4yMDguMTQ2&","bulk_download_file_name":"Long_term_macrozoobenthos_changes_in_a_s.pdf","bulk_download_url":"https://d1wqtxts1xzle7.cloudfront.net/113238186/zettler_und_daunys-2007-limnologica-libre.pdf?1712860349=\u0026response-content-disposition=attachment%3B+filename%3DLong_term_macrozoobenthos_changes_in_a_s.pdf\u0026Expires=1732737170\u0026Signature=UnD-9ijDvq-hHq~zTPYDBGy60Fsk2ZUK6riaLN5u-ntDiFYzDIbonl-qr9rCAL2UdW0YaTceV3-RKvBMNowebhHQmr47qBOU2ksRUt4rLol6tTuS~Yd~Rbivfj7tG5KY5jMuStFee0pi~fTe89GQog-tiSX8JxRa-AUbJi68Gtr~~8WnVwR8t3G7LXxB-VhaOpgdobqHBDYZ0IwLfpe-3r7y1FiRYTiQK-c9Ive0VH3ojKP8saUypNrhC3CTu-72SLah1B4kS6GC-nJmJEI57tRideNIsHudRzAEYIdJcGjeKOWFW8hwp1C~P9Rk0P5k1R7VlChUHSWHi8D0B31dKg__\u0026Key-Pair-Id=APKAJLOHF5GGSLRBV4ZA"}],"slug":"Long_term_macrozoobenthos_changes_in_a_shallow_boreal_lagoon_Comparison_of_a_recent_biodiversity_inventory_with_historical_data","translated_slug":"","page_count":16,"language":"en","content_type":"Work","owner":{"id":64309884,"first_name":"Darius","middle_initials":null,"last_name":"Daunys","page_name":"DariusDaunys","domain_name":"independent","created_at":"2017-05-15T05:34:19.853-07:00","display_name":"Darius Daunys","url":"https://independent.academia.edu/DariusDaunys"},"attachments":[{"id":113238186,"title":"","file_type":"pdf","scribd_thumbnail_url":"https://attachments.academia-assets.com/113238186/thumbnails/1.jpg","file_name":"zettler_und_daunys-2007-limnologica.pdf","download_url":"https://www.academia.edu/attachments/113238186/download_file?st=MTczMjczMzU3MCw4LjIyMi4yMDguMTQ2&","bulk_download_file_name":"Long_term_macrozoobenthos_changes_in_a_s.pdf","bulk_download_url":"https://d1wqtxts1xzle7.cloudfront.net/113238186/zettler_und_daunys-2007-limnologica-libre.pdf?1712860349=\u0026response-content-disposition=attachment%3B+filename%3DLong_term_macrozoobenthos_changes_in_a_s.pdf\u0026Expires=1732737170\u0026Signature=UnD-9ijDvq-hHq~zTPYDBGy60Fsk2ZUK6riaLN5u-ntDiFYzDIbonl-qr9rCAL2UdW0YaTceV3-RKvBMNowebhHQmr47qBOU2ksRUt4rLol6tTuS~Yd~Rbivfj7tG5KY5jMuStFee0pi~fTe89GQog-tiSX8JxRa-AUbJi68Gtr~~8WnVwR8t3G7LXxB-VhaOpgdobqHBDYZ0IwLfpe-3r7y1FiRYTiQK-c9Ive0VH3ojKP8saUypNrhC3CTu-72SLah1B4kS6GC-nJmJEI57tRideNIsHudRzAEYIdJcGjeKOWFW8hwp1C~P9Rk0P5k1R7VlChUHSWHi8D0B31dKg__\u0026Key-Pair-Id=APKAJLOHF5GGSLRBV4ZA"}],"research_interests":[{"id":402,"name":"Environmental Science","url":"https://www.academia.edu/Documents/in/Environmental_Science"},{"id":7710,"name":"Biology","url":"https://www.academia.edu/Documents/in/Biology"},{"id":9846,"name":"Ecology","url":"https://www.academia.edu/Documents/in/Ecology"},{"id":17825,"name":"Biodiversity","url":"https://www.academia.edu/Documents/in/Biodiversity"},{"id":157600,"name":"Water Framework Directive","url":"https://www.academia.edu/Documents/in/Water_Framework_Directive"},{"id":221822,"name":"Historical Data","url":"https://www.academia.edu/Documents/in/Historical_Data"},{"id":585173,"name":"Alien species","url":"https://www.academia.edu/Documents/in/Alien_species"},{"id":960649,"name":"Boreal","url":"https://www.academia.edu/Documents/in/Boreal"}],"urls":[{"id":41019521,"url":"https://doi.org/10.1016/j.limno.2006.12.004"}]}, dispatcherData: dispatcherData }); 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$(this).data('initialized', true); } }); $a.trackClickSource(".js-work-strip-work-link", "profile_work_strip") }); </script> <div class="js-work-strip profile--work_container" data-work-id="117361987"><div class="profile--work_thumbnail hidden-xs"><a class="js-work-strip-work-link" data-click-track="profile-work-strip-thumbnail" href="https://www.academia.edu/117361987/Marenzelleria_viridis_Verrill_1873_"><img alt="Research paper thumbnail of Marenzelleria viridis (Verrill, 1873)" class="work-thumbnail" src="https://a.academia-assets.com/images/blank-paper.jpg" /></a></div><div class="wp-workCard wp-workCard_itemContainer"><div class="wp-workCard_item wp-workCard--title"><a class="js-work-strip-work-link text-gray-darker" data-click-track="profile-work-strip-title" href="https://www.academia.edu/117361987/Marenzelleria_viridis_Verrill_1873_">Marenzelleria viridis (Verrill, 1873)</a></div><div class="wp-workCard_item wp-workCard--actions"><span class="work-strip-bookmark-button-container"></span><span class="wp-workCard--action visible-if-viewed-by-owner inline-block" style="display: none;"><span class="js-profile-work-strip-edit-button-wrapper profile-work-strip-edit-button-wrapper" data-work-id="117361987"><a class="js-profile-work-strip-edit-button" tabindex="0"><span><i class="fa fa-pencil"></i></span><span>Edit</span></a></span></span><span id="work-strip-rankings-button-container"></span></div><div class="wp-workCard_item wp-workCard--stats"><span><span><span class="js-view-count view-count u-mr2x" data-work-id="117361987"><i class="fa fa-spinner fa-spin"></i></span><script>$(function () { var workId = 117361987; 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$(this).data('initialized', true); } }); $a.trackClickSource(".js-work-strip-work-link", "profile_work_strip") }); </script> <div class="js-work-strip profile--work_container" data-work-id="117361986"><div class="profile--work_thumbnail hidden-xs"><a class="js-work-strip-work-link" data-click-track="profile-work-strip-thumbnail" href="https://www.academia.edu/117361986/Rating_species_sensitivity_throughout_gradient_systems_a_consistent_approach_for_the_Baltic_Sea"><img alt="Research paper thumbnail of Rating species sensitivity throughout gradient systems – a consistent approach for the Baltic Sea" class="work-thumbnail" src="https://a.academia-assets.com/images/blank-paper.jpg" /></a></div><div class="wp-workCard wp-workCard_itemContainer"><div class="wp-workCard_item wp-workCard--title"><a class="js-work-strip-work-link text-gray-darker" data-click-track="profile-work-strip-title" href="https://www.academia.edu/117361986/Rating_species_sensitivity_throughout_gradient_systems_a_consistent_approach_for_the_Baltic_Sea">Rating species sensitivity throughout gradient systems – a consistent approach for the Baltic Sea</a></div><div class="wp-workCard_item"><span>Ecological Indicators</span><span>, 2016</span></div><div class="wp-workCard_item"><span class="js-work-more-abstract-truncated">Abstract Evaluating the state of benthic communities has played an important role in water qualit...</span><a class="js-work-more-abstract" data-broccoli-component="work_strip.more_abstract" data-click-track="profile-work-strip-more-abstract" href="javascript:;"><span> more </span><span><i class="fa fa-caret-down"></i></span></a><span class="js-work-more-abstract-untruncated hidden">Abstract Evaluating the state of benthic communities has played an important role in water quality assessments. Indices incorporating species sensitivities, richness and densities are commonly applied. In Europe, the importance of benthic indices has increased in the last years with the implementation of the European Marine Strategy Framework Directive (MSFD) which at the same time demands the applicability of an index across regional scales. To date, environmental variability is rarely considered in benthic indices and most sensitivity rankings have the disadvantages of static values (i.e. the same value in all areas), expert judgement and a limited geographical range. This study presents species sensitivity values calculated along environmental gradients for the Baltic Sea. Sensitivities were calculated according to the procedure of the Benthic Quality Index (BQI). We created a matrix of subregions, classes of salinity, depth and gear to identify comparable subsets for data analysis. Altogether, 19 subsets were defined within the Baltic Sea basins. Sensitivity values were calculated for 329 species out of a total of 678 species that were recorded in this study. Sensitivity values of taxa vary between subsets as it was expected for different environmental conditions. Most sensitivity values can be assigned to species occurring in euhaline and polyhaline waters. Distribution of species with high and low sensitivity values differed along the salinity gradient. In euhaline waters more species with high sensitivity values occurred than species with low sensitivity values, while in mesohaline waters the ratio of high and low sensitivity values among species was almost equal. In oligohaline waters more species with lower sensitivity values were present. For the first time, sensitivity values were calculated for a large number of species using the same method for the entire Baltic Sea. This results in a Baltic-wide comprehensive set of sensitivity values based on a dataset across subregional borders, and divided along environmental gradients and gear type. The same principles can be applied to transient waters from rivers to coastal lagoons as well as to other environments with gradients of, e.g. hydrodynamic characteristics. Publicly available sensitivity values will increase transparency and support the improvement of state assessments under the MSFD.</span></div><div class="wp-workCard_item wp-workCard--actions"><span class="work-strip-bookmark-button-container"></span><span class="wp-workCard--action visible-if-viewed-by-owner inline-block" style="display: none;"><span class="js-profile-work-strip-edit-button-wrapper profile-work-strip-edit-button-wrapper" data-work-id="117361986"><a class="js-profile-work-strip-edit-button" tabindex="0"><span><i class="fa fa-pencil"></i></span><span>Edit</span></a></span></span><span id="work-strip-rankings-button-container"></span></div><div class="wp-workCard_item wp-workCard--stats"><span><span><span class="js-view-count view-count u-mr2x" data-work-id="117361986"><i class="fa fa-spinner fa-spin"></i></span><script>$(function () { var workId = 117361986; window.Academia.workViewCountsFetcher.queue(workId, function (count) { var description = window.$h.commaizeInt(count) + " " + window.$h.pluralize(count, 'View'); $(".js-view-count[data-work-id=117361986]").text(description); $(".js-view-count[data-work-id=117361986]").attr('title', description).tooltip(); }); });</script></span></span><span><span class="percentile-widget hidden"><span class="u-mr2x work-percentile"></span></span><script>$(function () { var workId = 117361986; window.Academia.workPercentilesFetcher.queue(workId, function (percentileText) { var container = $(".js-work-strip[data-work-id='117361986']"); container.find('.work-percentile').text(percentileText.charAt(0).toUpperCase() + percentileText.slice(1)); container.find('.percentile-widget').show(); container.find('.percentile-widget').removeClass('hidden'); }); });</script></span><span><script>$(function() { new Works.PaperRankView({ workId: 117361986, container: "", }); });</script></span></div><div id="work-strip-premium-row-container"></div></div></div><script> require.config({ waitSeconds: 90 })(["https://a.academia-assets.com/assets/wow_profile-f77ea15d77ce96025a6048a514272ad8becbad23c641fc2b3bd6e24ca6ff1932.js","https://a.academia-assets.com/assets/work_edit-ad038b8c047c1a8d4fa01b402d530ff93c45fee2137a149a4a5398bc8ad67560.js"], function() { // from javascript_helper.rb var dispatcherData = {} if (false){ window.WowProfile.dispatcher = window.WowProfile.dispatcher || _.clone(Backbone.Events); dispatcherData = { dispatcher: window.WowProfile.dispatcher, downloadLinkId: "-1" } } $('.js-work-strip[data-work-id=117361986]').each(function() { if (!$(this).data('initialized')) { new WowProfile.WorkStripView({ el: this, workJSON: {"id":117361986,"title":"Rating species sensitivity throughout gradient systems – a consistent approach for the Baltic Sea","translated_title":"","metadata":{"abstract":"Abstract Evaluating the state of benthic communities has played an important role in water quality assessments. 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Sensitivity values were calculated for 329 species out of a total of 678 species that were recorded in this study. Sensitivity values of taxa vary between subsets as it was expected for different environmental conditions. Most sensitivity values can be assigned to species occurring in euhaline and polyhaline waters. Distribution of species with high and low sensitivity values differed along the salinity gradient. In euhaline waters more species with high sensitivity values occurred than species with low sensitivity values, while in mesohaline waters the ratio of high and low sensitivity values among species was almost equal. In oligohaline waters more species with lower sensitivity values were present. For the first time, sensitivity values were calculated for a large number of species using the same method for the entire Baltic Sea. This results in a Baltic-wide comprehensive set of sensitivity values based on a dataset across subregional borders, and divided along environmental gradients and gear type. The same principles can be applied to transient waters from rivers to coastal lagoons as well as to other environments with gradients of, e.g. hydrodynamic characteristics. Publicly available sensitivity values will increase transparency and support the improvement of state assessments under the MSFD.","publisher":"Elsevier BV","publication_date":{"day":null,"month":null,"year":2016,"errors":{}},"publication_name":"Ecological Indicators"},"translated_abstract":"Abstract Evaluating the state of benthic communities has played an important role in water quality assessments. Indices incorporating species sensitivities, richness and densities are commonly applied. In Europe, the importance of benthic indices has increased in the last years with the implementation of the European Marine Strategy Framework Directive (MSFD) which at the same time demands the applicability of an index across regional scales. To date, environmental variability is rarely considered in benthic indices and most sensitivity rankings have the disadvantages of static values (i.e. the same value in all areas), expert judgement and a limited geographical range. This study presents species sensitivity values calculated along environmental gradients for the Baltic Sea. Sensitivities were calculated according to the procedure of the Benthic Quality Index (BQI). We created a matrix of subregions, classes of salinity, depth and gear to identify comparable subsets for data analysis. Altogether, 19 subsets were defined within the Baltic Sea basins. Sensitivity values were calculated for 329 species out of a total of 678 species that were recorded in this study. Sensitivity values of taxa vary between subsets as it was expected for different environmental conditions. Most sensitivity values can be assigned to species occurring in euhaline and polyhaline waters. Distribution of species with high and low sensitivity values differed along the salinity gradient. In euhaline waters more species with high sensitivity values occurred than species with low sensitivity values, while in mesohaline waters the ratio of high and low sensitivity values among species was almost equal. In oligohaline waters more species with lower sensitivity values were present. For the first time, sensitivity values were calculated for a large number of species using the same method for the entire Baltic Sea. This results in a Baltic-wide comprehensive set of sensitivity values based on a dataset across subregional borders, and divided along environmental gradients and gear type. The same principles can be applied to transient waters from rivers to coastal lagoons as well as to other environments with gradients of, e.g. hydrodynamic characteristics. Publicly available sensitivity values will increase transparency and support the improvement of state assessments under the MSFD.","internal_url":"https://www.academia.edu/117361986/Rating_species_sensitivity_throughout_gradient_systems_a_consistent_approach_for_the_Baltic_Sea","translated_internal_url":"","created_at":"2024-04-11T10:54:30.700-07:00","preview_url":null,"current_user_can_edit":null,"current_user_is_owner":null,"owner_id":64309884,"coauthors_can_edit":true,"document_type":"paper","co_author_tags":[],"downloadable_attachments":[],"slug":"Rating_species_sensitivity_throughout_gradient_systems_a_consistent_approach_for_the_Baltic_Sea","translated_slug":"","page_count":null,"language":"en","content_type":"Work","owner":{"id":64309884,"first_name":"Darius","middle_initials":null,"last_name":"Daunys","page_name":"DariusDaunys","domain_name":"independent","created_at":"2017-05-15T05:34:19.853-07:00","display_name":"Darius Daunys","url":"https://independent.academia.edu/DariusDaunys"},"attachments":[],"research_interests":[{"id":402,"name":"Environmental Science","url":"https://www.academia.edu/Documents/in/Environmental_Science"},{"id":47884,"name":"Biological Sciences","url":"https://www.academia.edu/Documents/in/Biological_Sciences"},{"id":58054,"name":"Environmental Sciences","url":"https://www.academia.edu/Documents/in/Environmental_Sciences"},{"id":138744,"name":"Ecological Indicators","url":"https://www.academia.edu/Documents/in/Ecological_Indicators"},{"id":260118,"name":"CHEMICAL SCIENCES","url":"https://www.academia.edu/Documents/in/CHEMICAL_SCIENCES"},{"id":410933,"name":"Baltic Sea","url":"https://www.academia.edu/Documents/in/Baltic_Sea"}],"urls":[{"id":41019520,"url":"https://api.elsevier.com/content/article/PII:S1470160X15005324?httpAccept=text/xml"}]}, dispatcherData: dispatcherData }); 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Baltic Sea Environmental Proceedings No. 138. Information included in this publication or extracts thereof are free for citing on the condition that the complete reference of the publication is given as stated above.","grobid_abstract_attachment_id":113238184},"translated_abstract":null,"internal_url":"https://www.academia.edu/117361984/Red_List_of_Baltic_Sea_underwater_biotopes_habitats_and_biotope_complexes","translated_internal_url":"","created_at":"2024-04-11T10:54:30.478-07:00","preview_url":null,"current_user_can_edit":null,"current_user_is_owner":null,"owner_id":64309884,"coauthors_can_edit":true,"document_type":"paper","co_author_tags":[],"downloadable_attachments":[{"id":113238184,"title":"","file_type":"pdf","scribd_thumbnail_url":"https://attachments.academia-assets.com/113238184/thumbnails/1.jpg","file_name":"BSEP138.pdf","download_url":"https://www.academia.edu/attachments/113238184/download_file?st=MTczMjczMzU3MCw4LjIyMi4yMDguMTQ2&","bulk_download_file_name":"Red_List_of_Baltic_Sea_underwater_biotop.pdf","bulk_download_url":"https://d1wqtxts1xzle7.cloudfront.net/113238184/BSEP138-libre.pdf?1712860378=\u0026response-content-disposition=attachment%3B+filename%3DRed_List_of_Baltic_Sea_underwater_biotop.pdf\u0026Expires=1732737170\u0026Signature=AuQM3ymZ-Ly1KNsowYBt4hLFf1pfPjizkMfHQzCdfsNKD7a1pfixqdzQ4vYTekvZuyYjkc9z-03s7OzQgSaoUHPWopImk5QPWmtpXpFjQsttPtbwD-IE~9o8A1sM6QqV82qGOfzrdu3X6uOkCqZSpkozWRAl1iXP~-RI4J4x6xhbpeR6C3w8w~i7YuXEj2Wuxu8dzWGD9uoYFWiqjBejwA5dkqK8rtpFbCjmvEJtFZQOoGCzWUDXovwx5c6FjAgaqZgkd-rC51sjhgxiYWr-vs2qE7x8BWuQgu~JuHBUt2Q5utMFCBoaBgGxlWcRODfn~2YOPlhQZ8nfbcw89TeYXQ__\u0026Key-Pair-Id=APKAJLOHF5GGSLRBV4ZA"}],"slug":"Red_List_of_Baltic_Sea_underwater_biotopes_habitats_and_biotope_complexes","translated_slug":"","page_count":74,"language":"en","content_type":"Work","owner":{"id":64309884,"first_name":"Darius","middle_initials":null,"last_name":"Daunys","page_name":"DariusDaunys","domain_name":"independent","created_at":"2017-05-15T05:34:19.853-07:00","display_name":"Darius Daunys","url":"https://independent.academia.edu/DariusDaunys"},"attachments":[{"id":113238184,"title":"","file_type":"pdf","scribd_thumbnail_url":"https://attachments.academia-assets.com/113238184/thumbnails/1.jpg","file_name":"BSEP138.pdf","download_url":"https://www.academia.edu/attachments/113238184/download_file?st=MTczMjczMzU3MCw4LjIyMi4yMDguMTQ2&","bulk_download_file_name":"Red_List_of_Baltic_Sea_underwater_biotop.pdf","bulk_download_url":"https://d1wqtxts1xzle7.cloudfront.net/113238184/BSEP138-libre.pdf?1712860378=\u0026response-content-disposition=attachment%3B+filename%3DRed_List_of_Baltic_Sea_underwater_biotop.pdf\u0026Expires=1732737170\u0026Signature=AuQM3ymZ-Ly1KNsowYBt4hLFf1pfPjizkMfHQzCdfsNKD7a1pfixqdzQ4vYTekvZuyYjkc9z-03s7OzQgSaoUHPWopImk5QPWmtpXpFjQsttPtbwD-IE~9o8A1sM6QqV82qGOfzrdu3X6uOkCqZSpkozWRAl1iXP~-RI4J4x6xhbpeR6C3w8w~i7YuXEj2Wuxu8dzWGD9uoYFWiqjBejwA5dkqK8rtpFbCjmvEJtFZQOoGCzWUDXovwx5c6FjAgaqZgkd-rC51sjhgxiYWr-vs2qE7x8BWuQgu~JuHBUt2Q5utMFCBoaBgGxlWcRODfn~2YOPlhQZ8nfbcw89TeYXQ__\u0026Key-Pair-Id=APKAJLOHF5GGSLRBV4ZA"}],"research_interests":[],"urls":[]}, dispatcherData: dispatcherData }); $(this).data('initialized', true); } }); $a.trackClickSource(".js-work-strip-work-link", "profile_work_strip") }); </script> <div class="js-work-strip profile--work_container" data-work-id="117361983"><div class="profile--work_thumbnail hidden-xs"><a class="js-work-strip-work-link" data-click-track="profile-work-strip-thumbnail" href="https://www.academia.edu/117361983/Long_term_macrozoobenthos_changes_in_a_shallow_boreal_lagoon_Comparison_of_a_recent_biodiversity_inventory_with_historical_data"><img alt="Research paper thumbnail of Long-term macrozoobenthos changes in a shallow boreal lagoon: Comparison of a recent biodiversity inventory with historical data" class="work-thumbnail" src="https://attachments.academia-assets.com/113238187/thumbnails/1.jpg" /></a></div><div class="wp-workCard wp-workCard_itemContainer"><div class="wp-workCard_item wp-workCard--title"><a class="js-work-strip-work-link text-gray-darker" data-click-track="profile-work-strip-title" href="https://www.academia.edu/117361983/Long_term_macrozoobenthos_changes_in_a_shallow_boreal_lagoon_Comparison_of_a_recent_biodiversity_inventory_with_historical_data">Long-term macrozoobenthos changes in a shallow boreal lagoon: Comparison of a recent biodiversity inventory with historical data</a></div><div class="wp-workCard_item"><span>Limnologica</span><span>, 2007</span></div><div class="wp-workCard_item wp-workCard--actions"><span class="work-strip-bookmark-button-container"></span><a id="662d166c6fe20cd791bbeeea1ace71c4" class="wp-workCard--action" rel="nofollow" data-click-track="profile-work-strip-download" data-download="{"attachment_id":113238187,"asset_id":117361983,"asset_type":"Work","button_location":"profile"}" href="https://www.academia.edu/attachments/113238187/download_file?st=MTczMjczMzU3MCw4LjIyMi4yMDguMTQ2&s=profile"><span><i class="fa fa-arrow-down"></i></span><span>Download</span></a><span class="wp-workCard--action visible-if-viewed-by-owner inline-block" style="display: none;"><span class="js-profile-work-strip-edit-button-wrapper profile-work-strip-edit-button-wrapper" data-work-id="117361983"><a class="js-profile-work-strip-edit-button" tabindex="0"><span><i class="fa fa-pencil"></i></span><span>Edit</span></a></span></span><span id="work-strip-rankings-button-container"></span></div><div class="wp-workCard_item wp-workCard--stats"><span><span><span class="js-view-count view-count u-mr2x" data-work-id="117361983"><i class="fa fa-spinner fa-spin"></i></span><script>$(function () { var workId = 117361983; 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In this paper, two historical biodiversity datasets (from 1920s and 1950s) and results from the recent inventory are used to trace the long-term changes of the macrozoobenthos in the eutrophic boreal lagoon of the Baltic Sea. In comparison of datasets the highest congruence was obtained for molluscs and malacostracan crustaceans, which also had a similar level of taxonomic emphasis between studies. Considering inconsistencies in methodology and taxonomic determination, only few species extinctions in these groups did likely occur during the last 100 years. Two amphipod species (Gammarus pulex and Gammarus lacustris) were not found during the recent survey, whereas five new species of this taxonomic group occurred in the lagoon since 1950s. The causes of these extinctions remain unclear; however displacement by established new amphipods cannot be excluded. Theodoxus fluviatilis was recently recorded in the very restricted area of the lagoon, while in earlier studies the species was mentioned as common and widely distributed in the water body. On the other hand, 10 gastropod species and 9 bivalves were reported for the first time in the lagoon and most likely have been overlooked in earlier surveys. Approximately 10% of the species have their origin outside the Baltic Sea basin and the number of invasions considerably exceeds the number of likely extinctions. 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To comparatively analyze the effects of an exotic and a native polychaete burrower on sediment-water exchanges, two laboratory experiments were performed. In the first experiment, the invasive spionid polychaete Marenzelleria neglecta was added to defaunated sediments and fluxes of the inert tracer (bromide, Br−) were measured to quantify the effects of irrigation by the worm on the tracer transport. In the second experiment, M. neglecta or the native polychaete Hediste diversicolor were introduced to a relatively diverse Baltic soft-bottom macrofauna community. The effect of species on fluxes of reactive solutes (ammonium, NH4+, and phosphate, PO43−) and transport rates of Br− was estimated. The results indicate different invasion effects depending on the characteristics of the recipient habitat. 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To comparatively analyze the effects of an exotic and a native polychaete burrower on sediment-water exchanges, two laboratory experiments were performed. In the first experiment, the invasive spionid polychaete Marenzelleria neglecta was added to defaunated sediments and fluxes of the inert tracer (bromide, Br−) were measured to quantify the effects of irrigation by the worm on the tracer transport. In the second experiment, M. neglecta or the native polychaete Hediste diversicolor were introduced to a relatively diverse Baltic soft-bottom macrofauna community. The effect of species on fluxes of reactive solutes (ammonium, NH4+, and phosphate, PO43−) and transport rates of Br− was estimated. The results indicate different invasion effects depending on the characteristics of the recipient habitat. I...","publisher":"MDPI AG","publication_date":{"day":null,"month":null,"year":2019,"errors":{}},"publication_name":"Water"},"translated_abstract":"Different irrigation or ventilation strategies by macrofauna may provide a competitive advantage to tolerant species invading impacted benthic systems and alter benthic-pelagic coupling. To comparatively analyze the effects of an exotic and a native polychaete burrower on sediment-water exchanges, two laboratory experiments were performed. In the first experiment, the invasive spionid polychaete Marenzelleria neglecta was added to defaunated sediments and fluxes of the inert tracer (bromide, Br−) were measured to quantify the effects of irrigation by the worm on the tracer transport. In the second experiment, M. neglecta or the native polychaete Hediste diversicolor were introduced to a relatively diverse Baltic soft-bottom macrofauna community. The effect of species on fluxes of reactive solutes (ammonium, NH4+, and phosphate, PO43−) and transport rates of Br− was estimated. The results indicate different invasion effects depending on the characteristics of the recipient habitat. 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$(this).data('initialized', true); } }); $a.trackClickSource(".js-work-strip-work-link", "profile_work_strip") }); </script> </div><div class="profile--tab_content_container js-tab-pane tab-pane" data-section-id="17300314" id="papers"><div class="js-work-strip profile--work_container" data-work-id="117361992"><div class="profile--work_thumbnail hidden-xs"><a class="js-work-strip-work-link" data-click-track="profile-work-strip-thumbnail" href="https://www.academia.edu/117361992/Species_Strategy_Near_Its_Boundary_theMarenzelleria_cf_viridis_Polychaeta_Spionidae_Case_in_the_South_Eastern_Baltic_Sea"><img alt="Research paper thumbnail of Species Strategy Near Its Boundary: theMarenzelleria cf.viridis (Polychaeta, Spionidae) Case in the South-Eastern Baltic Sea" class="work-thumbnail" src="https://a.academia-assets.com/images/blank-paper.jpg" /></a></div><div class="wp-workCard wp-workCard_itemContainer"><div class="wp-workCard_item wp-workCard--title"><a class="js-work-strip-work-link text-gray-darker" data-click-track="profile-work-strip-title" href="https://www.academia.edu/117361992/Species_Strategy_Near_Its_Boundary_theMarenzelleria_cf_viridis_Polychaeta_Spionidae_Case_in_the_South_Eastern_Baltic_Sea">Species Strategy Near Its Boundary: theMarenzelleria cf.viridis (Polychaeta, Spionidae) Case in the South-Eastern Baltic Sea</a></div><div class="wp-workCard_item"><span>International Review of Hydrobiology</span><span>, Nov 1, 2000</span></div><div class="wp-workCard_item"><span class="js-work-more-abstract-truncated">The invasive polychaete worm Marenzelleria cf. viridis spread into various coastal habitats in th...</span><a class="js-work-more-abstract" data-broccoli-component="work_strip.more_abstract" data-click-track="profile-work-strip-more-abstract" href="javascript:;"><span> more </span><span><i class="fa fa-caret-down"></i></span></a><span class="js-work-more-abstract-untruncated hidden">The invasive polychaete worm Marenzelleria cf. viridis spread into various coastal habitats in the Baltic Sea. The estimated limits regarding its salinity tolerance obtained from different laboratory experiments alone only rarely explain the actual species boundaries in nature, e.g. in the Curonian lagoon. Therefore, a field study was carried out aimed at to define, how a population maintains itself in a dynamic estuarine habitat with rapid and irregular changing salinity (annual mean 3 PSU, range of variation from 0 to 7.5 PSU). Under these conditions the species females reached maturity. However, during the final reproduction phase their spawning was delayed and oosorption started. It was estimated that roughly 0.05% of the nearby sea population offspring was transported to the estuary but most of the pelagic larvae were not able to develop beyond the 10 segments stage. It seems that the estuarine benthic population is maintained by migration of the species benthic stages. This mode probably is more efficient in comparison to dispersal by pelagic larvae when a species colonises stressed and dynamic environments.</span></div><div class="wp-workCard_item wp-workCard--actions"><span class="work-strip-bookmark-button-container"></span><span class="wp-workCard--action visible-if-viewed-by-owner inline-block" style="display: none;"><span class="js-profile-work-strip-edit-button-wrapper profile-work-strip-edit-button-wrapper" data-work-id="117361992"><a class="js-profile-work-strip-edit-button" tabindex="0"><span><i class="fa fa-pencil"></i></span><span>Edit</span></a></span></span><span id="work-strip-rankings-button-container"></span></div><div class="wp-workCard_item wp-workCard--stats"><span><span><span class="js-view-count view-count u-mr2x" data-work-id="117361992"><i class="fa fa-spinner fa-spin"></i></span><script>$(function () { var workId = 117361992; window.Academia.workViewCountsFetcher.queue(workId, function (count) { var description = window.$h.commaizeInt(count) + " " + window.$h.pluralize(count, 'View'); $(".js-view-count[data-work-id=117361992]").text(description); $(".js-view-count[data-work-id=117361992]").attr('title', description).tooltip(); }); });</script></span></span><span><span class="percentile-widget hidden"><span class="u-mr2x work-percentile"></span></span><script>$(function () { var workId = 117361992; window.Academia.workPercentilesFetcher.queue(workId, function (percentileText) { var container = $(".js-work-strip[data-work-id='117361992']"); container.find('.work-percentile').text(percentileText.charAt(0).toUpperCase() + percentileText.slice(1)); container.find('.percentile-widget').show(); container.find('.percentile-widget').removeClass('hidden'); }); });</script></span><span><script>$(function() { new Works.PaperRankView({ workId: 117361992, container: "", }); });</script></span></div><div id="work-strip-premium-row-container"></div></div></div><script> require.config({ waitSeconds: 90 })(["https://a.academia-assets.com/assets/wow_profile-f77ea15d77ce96025a6048a514272ad8becbad23c641fc2b3bd6e24ca6ff1932.js","https://a.academia-assets.com/assets/work_edit-ad038b8c047c1a8d4fa01b402d530ff93c45fee2137a149a4a5398bc8ad67560.js"], function() { // from javascript_helper.rb var dispatcherData = {} if (false){ window.WowProfile.dispatcher = window.WowProfile.dispatcher || _.clone(Backbone.Events); dispatcherData = { dispatcher: window.WowProfile.dispatcher, downloadLinkId: "-1" } } $('.js-work-strip[data-work-id=117361992]').each(function() { if (!$(this).data('initialized')) { new WowProfile.WorkStripView({ el: this, workJSON: {"id":117361992,"title":"Species Strategy Near Its Boundary: theMarenzelleria cf.viridis (Polychaeta, Spionidae) Case in the South-Eastern Baltic Sea","translated_title":"","metadata":{"abstract":"The invasive polychaete worm Marenzelleria cf. viridis spread into various coastal habitats in the Baltic Sea. The estimated limits regarding its salinity tolerance obtained from different laboratory experiments alone only rarely explain the actual species boundaries in nature, e.g. in the Curonian lagoon. Therefore, a field study was carried out aimed at to define, how a population maintains itself in a dynamic estuarine habitat with rapid and irregular changing salinity (annual mean 3 PSU, range of variation from 0 to 7.5 PSU). Under these conditions the species females reached maturity. However, during the final reproduction phase their spawning was delayed and oosorption started. It was estimated that roughly 0.05% of the nearby sea population offspring was transported to the estuary but most of the pelagic larvae were not able to develop beyond the 10 segments stage. It seems that the estuarine benthic population is maintained by migration of the species benthic stages. This mode probably is more efficient in comparison to dispersal by pelagic larvae when a species colonises stressed and dynamic environments.","publisher":"Wiley","publication_date":{"day":1,"month":11,"year":2000,"errors":{}},"publication_name":"International Review of Hydrobiology"},"translated_abstract":"The invasive polychaete worm Marenzelleria cf. viridis spread into various coastal habitats in the Baltic Sea. The estimated limits regarding its salinity tolerance obtained from different laboratory experiments alone only rarely explain the actual species boundaries in nature, e.g. in the Curonian lagoon. Therefore, a field study was carried out aimed at to define, how a population maintains itself in a dynamic estuarine habitat with rapid and irregular changing salinity (annual mean 3 PSU, range of variation from 0 to 7.5 PSU). Under these conditions the species females reached maturity. However, during the final reproduction phase their spawning was delayed and oosorption started. It was estimated that roughly 0.05% of the nearby sea population offspring was transported to the estuary but most of the pelagic larvae were not able to develop beyond the 10 segments stage. It seems that the estuarine benthic population is maintained by migration of the species benthic stages. This mode probably is more efficient in comparison to dispersal by pelagic larvae when a species colonises stressed and dynamic environments.","internal_url":"https://www.academia.edu/117361992/Species_Strategy_Near_Its_Boundary_theMarenzelleria_cf_viridis_Polychaeta_Spionidae_Case_in_the_South_Eastern_Baltic_Sea","translated_internal_url":"","created_at":"2024-04-11T10:54:31.887-07:00","preview_url":null,"current_user_can_edit":null,"current_user_is_owner":null,"owner_id":64309884,"coauthors_can_edit":true,"document_type":"paper","co_author_tags":[],"downloadable_attachments":[],"slug":"Species_Strategy_Near_Its_Boundary_theMarenzelleria_cf_viridis_Polychaeta_Spionidae_Case_in_the_South_Eastern_Baltic_Sea","translated_slug":"","page_count":null,"language":"en","content_type":"Work","owner":{"id":64309884,"first_name":"Darius","middle_initials":null,"last_name":"Daunys","page_name":"DariusDaunys","domain_name":"independent","created_at":"2017-05-15T05:34:19.853-07:00","display_name":"Darius Daunys","url":"https://independent.academia.edu/DariusDaunys"},"attachments":[],"research_interests":[{"id":7710,"name":"Biology","url":"https://www.academia.edu/Documents/in/Biology"},{"id":9846,"name":"Ecology","url":"https://www.academia.edu/Documents/in/Ecology"},{"id":11872,"name":"Hydrobiology","url":"https://www.academia.edu/Documents/in/Hydrobiology"},{"id":64336,"name":"Population","url":"https://www.academia.edu/Documents/in/Population"},{"id":85707,"name":"Habitat","url":"https://www.academia.edu/Documents/in/Habitat"},{"id":379570,"name":"Estuary","url":"https://www.academia.edu/Documents/in/Estuary"},{"id":410933,"name":"Baltic Sea","url":"https://www.academia.edu/Documents/in/Baltic_Sea"},{"id":880030,"name":"Polychaete","url":"https://www.academia.edu/Documents/in/Polychaete"},{"id":3816195,"name":"pelagic zone","url":"https://www.academia.edu/Documents/in/pelagic_zone"}],"urls":[{"id":41019524,"url":"https://doi.org/10.1002/1522-2632(200011)85:5/6%3C639::aid-iroh639%3E3.0.co;2-g"}]}, dispatcherData: dispatcherData }); $(this).data('initialized', true); } }); $a.trackClickSource(".js-work-strip-work-link", "profile_work_strip") }); </script> <div class="js-work-strip profile--work_container" data-work-id="117361991"><div class="profile--work_thumbnail hidden-xs"><a class="js-work-strip-work-link" data-click-track="profile-work-strip-thumbnail" href="https://www.academia.edu/117361991/Application_of_underwater_imagery_for_the_description_of_upper_sublittoral_benthic_communities_in_glaciated_and_ice_free_Arctic_fjords"><img alt="Research paper thumbnail of Application of underwater imagery for the description of upper sublittoral benthic communities in glaciated and ice-free Arctic fjords" class="work-thumbnail" src="https://attachments.academia-assets.com/113238173/thumbnails/1.jpg" /></a></div><div class="wp-workCard wp-workCard_itemContainer"><div class="wp-workCard_item wp-workCard--title"><a class="js-work-strip-work-link text-gray-darker" data-click-track="profile-work-strip-title" href="https://www.academia.edu/117361991/Application_of_underwater_imagery_for_the_description_of_upper_sublittoral_benthic_communities_in_glaciated_and_ice_free_Arctic_fjords">Application of underwater imagery for the description of upper sublittoral benthic communities in glaciated and ice-free Arctic fjords</a></div><div class="wp-workCard_item"><span>Polar Biology</span><span>, Nov 2, 2022</span></div><div class="wp-workCard_item wp-workCard--actions"><span class="work-strip-bookmark-button-container"></span><a id="a6677fd4863099d0c41267d7cb8efa31" class="wp-workCard--action" rel="nofollow" data-click-track="profile-work-strip-download" data-download="{"attachment_id":113238173,"asset_id":117361991,"asset_type":"Work","button_location":"profile"}" href="https://www.academia.edu/attachments/113238173/download_file?st=MTczMjczMzU3MCw4LjIyMi4yMDguMTQ2&st=MTczMjczMzU3MCw4LjIyMi4yMDguMTQ2&s=profile"><span><i class="fa fa-arrow-down"></i></span><span>Download</span></a><span class="wp-workCard--action visible-if-viewed-by-owner inline-block" style="display: none;"><span class="js-profile-work-strip-edit-button-wrapper profile-work-strip-edit-button-wrapper" data-work-id="117361991"><a class="js-profile-work-strip-edit-button" tabindex="0"><span><i class="fa fa-pencil"></i></span><span>Edit</span></a></span></span><span id="work-strip-rankings-button-container"></span></div><div class="wp-workCard_item wp-workCard--stats"><span><span><span class="js-view-count view-count u-mr2x" data-work-id="117361991"><i class="fa fa-spinner fa-spin"></i></span><script>$(function () { var workId = 117361991; window.Academia.workViewCountsFetcher.queue(workId, function (count) { var description = window.$h.commaizeInt(count) + " " + window.$h.pluralize(count, 'View'); $(".js-view-count[data-work-id=117361991]").text(description); $(".js-view-count[data-work-id=117361991]").attr('title', description).tooltip(); }); });</script></span></span><span><span class="percentile-widget hidden"><span class="u-mr2x work-percentile"></span></span><script>$(function () { var workId = 117361991; window.Academia.workPercentilesFetcher.queue(workId, function (percentileText) { var container = $(".js-work-strip[data-work-id='117361991']"); container.find('.work-percentile').text(percentileText.charAt(0).toUpperCase() + percentileText.slice(1)); container.find('.percentile-widget').show(); container.find('.percentile-widget').removeClass('hidden'); }); });</script></span><span><script>$(function() { new Works.PaperRankView({ workId: 117361991, container: "", }); });</script></span></div><div id="work-strip-premium-row-container"></div></div></div><script> require.config({ waitSeconds: 90 })(["https://a.academia-assets.com/assets/wow_profile-f77ea15d77ce96025a6048a514272ad8becbad23c641fc2b3bd6e24ca6ff1932.js","https://a.academia-assets.com/assets/work_edit-ad038b8c047c1a8d4fa01b402d530ff93c45fee2137a149a4a5398bc8ad67560.js"], function() { // from javascript_helper.rb var dispatcherData = {} if (true){ window.WowProfile.dispatcher = window.WowProfile.dispatcher || _.clone(Backbone.Events); dispatcherData = { dispatcher: window.WowProfile.dispatcher, downloadLinkId: "a6677fd4863099d0c41267d7cb8efa31" } } $('.js-work-strip[data-work-id=117361991]').each(function() { if (!$(this).data('initialized')) { new WowProfile.WorkStripView({ el: this, workJSON: {"id":117361991,"title":"Application of underwater imagery for the description of upper sublittoral benthic communities in glaciated and ice-free Arctic fjords","translated_title":"","metadata":{"publisher":"Springer Science+Business Media","grobid_abstract":"Complex bottom topography and the presence of oating ice signi cantly complicates the use of traditional sampling methods in Arctic coastal waters, forcing to look for alternative approaches. One such technique is underwater imagery, which has grown in popularity in recent decades based on its effectiveness in hard-to-reach places. We demonstrate that an underwater video mosaic can be a reliable method for comparative analysis of Arctic habitats under the glacier in uence and glacier in uence-free habitats. The lming was carried out in the upper sublittoral (2-65 m) of Hornsund and Isfjorden areas, representing two ice-free and two glaciated bays. Video footage was obtained using an ROV mounted and \"drop-down\" video cameras and transformed into 148 video mosaics. Based on the lowest possible taxonomic level, 31 biological features (morphospecies) were identi ed and ascribed to benthic functional groups based on their feeding and mobility type. The morphospecies and functional groups were used for the comparative analysis of benthic communities. The study found that melting glaciers have a stronger impact on the structure of benthic communities across geographical areas. Morphological and functional composition of macrofauna re ected conditions in glacier in uence and in uence-free, and turbid water riverine bays. We discovered greater abundances of motile scavengers in glacier in uence bays whereas glacier in uence-free bay had more sessile suspension lters and glacier in uence-free riverine bay was dominated by discreetly motile and deposit feeders. Underwater imagery mosaics have proven to be a fairly reliable tool for eldwork-e cient quantitative characterization of benthic communities in the hard-to-reach Arctic's upper sublittoral. Highlights Combination of underwater imagery and morphospecies approaches provides su cient data to quantify the dominant macrobenthos forms in the arctic fjords. The morphospecies approach makes it possible to reveal the differences in the functional structure of the benthos in the periglacial and glacier in uence-free areas of the upper sublittoral. Underwater imagery may be recommended for eldwork-e cient assessment of benthos in conditions of complex bottom topography and the presence of oating ice. Consequently, this study highlights a greater in uence of melting glaciers on the structure of benthic communities than across geographical areas","publication_date":{"day":2,"month":11,"year":2022,"errors":{}},"publication_name":"Polar 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Sciences","url":"https://www.academia.edu/Documents/in/Biological_Sciences"},{"id":68049,"name":"Arctic","url":"https://www.academia.edu/Documents/in/Arctic"},{"id":79704,"name":"Underwater","url":"https://www.academia.edu/Documents/in/Underwater"},{"id":181597,"name":"Root-Mean Square Error","url":"https://www.academia.edu/Documents/in/Root-Mean_Square_Error"},{"id":322448,"name":"Fjord","url":"https://www.academia.edu/Documents/in/Fjord"},{"id":352542,"name":"Glacier","url":"https://www.academia.edu/Documents/in/Glacier"},{"id":512395,"name":"Polar Biology","url":"https://www.academia.edu/Documents/in/Polar_Biology"},{"id":1660649,"name":"Bay","url":"https://www.academia.edu/Documents/in/Bay"}],"urls":[{"id":41019523,"url":"https://www.researchsquare.com/article/rs-1808509/latest.pdf"}]}, dispatcherData: dispatcherData }); $(this).data('initialized', true); } }); $a.trackClickSource(".js-work-strip-work-link", "profile_work_strip") }); </script> <div class="js-work-strip profile--work_container" data-work-id="117361990"><div class="profile--work_thumbnail hidden-xs"><a class="js-work-strip-work-link" data-click-track="profile-work-strip-thumbnail" href="https://www.academia.edu/117361990/Effect_of_Species_Invasion_on_Transport_of_Solutes_at_Different_Levels_of_Soft_Sediment_Macrofauna_Diversity_Results_from_an_Experimental_Approach"><img alt="Research paper thumbnail of Effect of Species Invasion on Transport of Solutes at Different Levels of Soft Sediment Macrofauna Diversity: Results from an Experimental Approach" class="work-thumbnail" src="https://attachments.academia-assets.com/113238171/thumbnails/1.jpg" /></a></div><div class="wp-workCard wp-workCard_itemContainer"><div class="wp-workCard_item wp-workCard--title"><a class="js-work-strip-work-link text-gray-darker" data-click-track="profile-work-strip-title" href="https://www.academia.edu/117361990/Effect_of_Species_Invasion_on_Transport_of_Solutes_at_Different_Levels_of_Soft_Sediment_Macrofauna_Diversity_Results_from_an_Experimental_Approach">Effect of Species Invasion on Transport of Solutes at Different Levels of Soft Sediment Macrofauna Diversity: Results from an Experimental Approach</a></div><div class="wp-workCard_item"><span>Water</span><span>, Jul 25, 2019</span></div><div class="wp-workCard_item wp-workCard--actions"><span class="work-strip-bookmark-button-container"></span><a id="ab117c8fe91aff901f4ccb2f2fb201d6" class="wp-workCard--action" rel="nofollow" data-click-track="profile-work-strip-download" data-download="{"attachment_id":113238171,"asset_id":117361990,"asset_type":"Work","button_location":"profile"}" href="https://www.academia.edu/attachments/113238171/download_file?st=MTczMjczMzU3MCw4LjIyMi4yMDguMTQ2&st=MTczMjczMzU3MCw4LjIyMi4yMDguMTQ2&s=profile"><span><i class="fa 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})(["https://a.academia-assets.com/assets/wow_profile-f77ea15d77ce96025a6048a514272ad8becbad23c641fc2b3bd6e24ca6ff1932.js","https://a.academia-assets.com/assets/work_edit-ad038b8c047c1a8d4fa01b402d530ff93c45fee2137a149a4a5398bc8ad67560.js"], function() { // from javascript_helper.rb var dispatcherData = {} if (true){ window.WowProfile.dispatcher = window.WowProfile.dispatcher || _.clone(Backbone.Events); dispatcherData = { dispatcher: window.WowProfile.dispatcher, downloadLinkId: "ab117c8fe91aff901f4ccb2f2fb201d6" } } $('.js-work-strip[data-work-id=117361990]').each(function() { if (!$(this).data('initialized')) { new WowProfile.WorkStripView({ el: this, workJSON: {"id":117361990,"title":"Effect of Species Invasion on Transport of Solutes at Different Levels of Soft Sediment Macrofauna Diversity: Results from an Experimental Approach","translated_title":"","metadata":{"publisher":"Multidisciplinary Digital Publishing Institute","grobid_abstract":"Different irrigation or ventilation strategies by macrofauna may provide a competitive advantage to tolerant species invading impacted benthic systems and alter benthic-pelagic coupling. To comparatively analyze the effects of an exotic and a native polychaete burrower on sediment-water exchanges, two laboratory experiments were performed. In the first experiment, the invasive spionid polychaete Marenzelleria neglecta was added to defaunated sediments and fluxes of the inert tracer (bromide, Br −) were measured to quantify the effects of irrigation by the worm on the tracer transport. In the second experiment, M. neglecta or the native polychaete Hediste diversicolor were introduced to a relatively diverse Baltic soft-bottom macrofauna community. The effect of species on fluxes of reactive solutes (ammonium, NH 4 +, and phosphate, PO 4 3−) and transport rates of Br − was estimated. The results indicate different invasion effects depending on the characteristics of the recipient habitat. In defaunated sediments, a single specimen of M. neglecta significantly enhanced originally low solute exchange rates. Total tracer flux was significantly enhanced over diffusive flux by a factor of 1.6 ± 0.14 (n = 3). In natural sediments, on the other hand, the addition of either M. neglecta or H. diversicolor had no statistically significant effects on benthic fluxes. Tracer flux estimates between control and treatment incubations differed by less than 10% on average, and both reactive solutes tended to increase by 10 to 40% after additions. One specimen of M. neglecta in cores with defaunated sediment generated approximately 20% of the tracer flux produced by the relatively diverse macrofauna community. Estimated net tracer fluxes in two experiments corresponded well with the number of adult polychaetes found in sediments (r 2 = 0.73, p = 0.005, n = 12). The invasive M. neglecta produced a small effect on fluxes in biodiverse sediments, comparable to those of H. diversicolor, but it may deeply alter porewater chemistry in azoic sediment. As M. neglecta tolerates chemically reduced and sulphidic conditions, its bioirigation may favor sediment reoxidation and ultimately the recolonization by less tolerant, native species.","publication_date":{"day":25,"month":7,"year":2019,"errors":{}},"publication_name":"Water","grobid_abstract_attachment_id":113238171},"translated_abstract":null,"internal_url":"https://www.academia.edu/117361990/Effect_of_Species_Invasion_on_Transport_of_Solutes_at_Different_Levels_of_Soft_Sediment_Macrofauna_Diversity_Results_from_an_Experimental_Approach","translated_internal_url":"","created_at":"2024-04-11T10:54:31.456-07:00","preview_url":null,"current_user_can_edit":null,"current_user_is_owner":null,"owner_id":64309884,"coauthors_can_edit":true,"document_type":"paper","co_author_tags":[],"downloadable_attachments":[{"id":113238171,"title":"","file_type":"pdf","scribd_thumbnail_url":"https://attachments.academia-assets.com/113238171/thumbnails/1.jpg","file_name":"pdf.pdf","download_url":"https://www.academia.edu/attachments/113238171/download_file?st=MTczMjczMzU3MCw4LjIyMi4yMDguMTQ2&st=MTczMjczMzU3MCw4LjIyMi4yMDguMTQ2&","bulk_download_file_name":"Effect_of_Species_Invasion_on_Transport.pdf","bulk_download_url":"https://d1wqtxts1xzle7.cloudfront.net/113238171/pdf-libre.pdf?1712860358=\u0026response-content-disposition=attachment%3B+filename%3DEffect_of_Species_Invasion_on_Transport.pdf\u0026Expires=1732737170\u0026Signature=cln1wpZ7qgrDnZCmipby1lvhVRY4HmblsT3w5eZV0yXQeLJPrH5fZZtV6e~BRdrPkQrtdB2-VD0BUCzgIdxNQV8aQAKb20nqY94WwJvIOnV459Gk7CSnwArALnvXh4qs-EKAUpbuDJcqzrFrt55Mn0qv6SENJXm8iX33MJUwgP~DyY2juFxeScVryCDeXmLHLIOC00G4v9451BMwkWC0Iqdh8bySXGoxg1-NmjZh9JDnKBg8VI4vZw~wkHLs7-PimUyMZNmQNGWcJya-e~qVZeaF0odMxRlnN9cwQiOl30fOuMdZd9~TzDqMDTsrqCsCj4dJJqtv7px1SHONFGIQdQ__\u0026Key-Pair-Id=APKAJLOHF5GGSLRBV4ZA"}],"slug":"Effect_of_Species_Invasion_on_Transport_of_Solutes_at_Different_Levels_of_Soft_Sediment_Macrofauna_Diversity_Results_from_an_Experimental_Approach","translated_slug":"","page_count":18,"language":"en","content_type":"Work","owner":{"id":64309884,"first_name":"Darius","middle_initials":null,"last_name":"Daunys","page_name":"DariusDaunys","domain_name":"independent","created_at":"2017-05-15T05:34:19.853-07:00","display_name":"Darius 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dispatcherData: dispatcherData }); $(this).data('initialized', true); } }); $a.trackClickSource(".js-work-strip-work-link", "profile_work_strip") }); </script> <div class="js-work-strip profile--work_container" data-work-id="117361989"><div class="profile--work_thumbnail hidden-xs"><a class="js-work-strip-work-link" data-click-track="profile-work-strip-thumbnail" href="https://www.academia.edu/117361989/Long_term_macrozoobenthos_changes_in_a_shallow_boreal_lagoon_Comparison_of_a_recent_biodiversity_inventory_with_historical_data"><img alt="Research paper thumbnail of Long-term macrozoobenthos changes in a shallow boreal lagoon: Comparison of a recent biodiversity inventory with historical data" class="work-thumbnail" src="https://attachments.academia-assets.com/113238186/thumbnails/1.jpg" /></a></div><div class="wp-workCard wp-workCard_itemContainer"><div class="wp-workCard_item wp-workCard--title"><a class="js-work-strip-work-link text-gray-darker" 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water bodies, which implies assessment of their current ecological quality status in respect to defined reference (pristine) conditions. In this paper, two historical biodiversity datasets (from 1920s and 1950s) and results from the recent inventory are used to trace the long-term changes of the macrozoobenthos in the eutrophic boreal lagoon of the Baltic Sea. In comparison of datasets the highest congruence was obtained for molluscs and malacostracan crustaceans, which also had a similar level of taxonomic emphasis between studies. Considering inconsistencies in methodology and taxonomic determination, only few species extinctions in these groups did likely occur during the last 100 years. Two amphipod species (Gammarus pulex and Gammarus lacustris) were not found during the recent survey, whereas five new species of this taxonomic group occurred in the lagoon since 1950s. The causes of these extinctions remain unclear; however displacement by established new amphipods cannot be excluded. Theodoxus fluviatilis was recently recorded in the very restricted area of the lagoon, while in earlier studies the species was mentioned as common and widely distributed in the water body. On the other hand, 10 gastropod species and 9 bivalves were reported for the first time in the lagoon and most likely have been overlooked in earlier surveys. Approximately 10% of the species have their origin outside the Baltic Sea basin and the number of invasions considerably exceeds the number of likely extinctions. Assessment scheme of such changes is unclear following WFD guidelines, therefore elaboration of a framework for evaluation of the alien species diversity in a context of local biodiversity should attain more effort when implementing the WFD.","publication_date":{"day":1,"month":5,"year":2007,"errors":{}},"publication_name":"Limnologica","grobid_abstract_attachment_id":113238186},"translated_abstract":null,"internal_url":"https://www.academia.edu/117361989/Long_term_macrozoobenthos_changes_in_a_shallow_boreal_lagoon_Comparison_of_a_recent_biodiversity_inventory_with_historical_data","translated_internal_url":"","created_at":"2024-04-11T10:54:31.274-07:00","preview_url":null,"current_user_can_edit":null,"current_user_is_owner":null,"owner_id":64309884,"coauthors_can_edit":true,"document_type":"paper","co_author_tags":[],"downloadable_attachments":[{"id":113238186,"title":"","file_type":"pdf","scribd_thumbnail_url":"https://attachments.academia-assets.com/113238186/thumbnails/1.jpg","file_name":"zettler_und_daunys-2007-limnologica.pdf","download_url":"https://www.academia.edu/attachments/113238186/download_file?st=MTczMjczMzU3MCw4LjIyMi4yMDguMTQ2&st=MTczMjczMzU3MCw4LjIyMi4yMDguMTQ2&","bulk_download_file_name":"Long_term_macrozoobenthos_changes_in_a_s.pdf","bulk_download_url":"https://d1wqtxts1xzle7.cloudfront.net/113238186/zettler_und_daunys-2007-limnologica-libre.pdf?1712860349=\u0026response-content-disposition=attachment%3B+filename%3DLong_term_macrozoobenthos_changes_in_a_s.pdf\u0026Expires=1732737170\u0026Signature=UnD-9ijDvq-hHq~zTPYDBGy60Fsk2ZUK6riaLN5u-ntDiFYzDIbonl-qr9rCAL2UdW0YaTceV3-RKvBMNowebhHQmr47qBOU2ksRUt4rLol6tTuS~Yd~Rbivfj7tG5KY5jMuStFee0pi~fTe89GQog-tiSX8JxRa-AUbJi68Gtr~~8WnVwR8t3G7LXxB-VhaOpgdobqHBDYZ0IwLfpe-3r7y1FiRYTiQK-c9Ive0VH3ojKP8saUypNrhC3CTu-72SLah1B4kS6GC-nJmJEI57tRideNIsHudRzAEYIdJcGjeKOWFW8hwp1C~P9Rk0P5k1R7VlChUHSWHi8D0B31dKg__\u0026Key-Pair-Id=APKAJLOHF5GGSLRBV4ZA"}],"slug":"Long_term_macrozoobenthos_changes_in_a_shallow_boreal_lagoon_Comparison_of_a_recent_biodiversity_inventory_with_historical_data","translated_slug":"","page_count":16,"language":"en","content_type":"Work","owner":{"id":64309884,"first_name":"Darius","middle_initials":null,"last_name":"Daunys","page_name":"DariusDaunys","domain_name":"independent","created_at":"2017-05-15T05:34:19.853-07:00","display_name":"Darius Daunys","url":"https://independent.academia.edu/DariusDaunys"},"attachments":[{"id":113238186,"title":"","file_type":"pdf","scribd_thumbnail_url":"https://attachments.academia-assets.com/113238186/thumbnails/1.jpg","file_name":"zettler_und_daunys-2007-limnologica.pdf","download_url":"https://www.academia.edu/attachments/113238186/download_file?st=MTczMjczMzU3MCw4LjIyMi4yMDguMTQ2&st=MTczMjczMzU3MCw4LjIyMi4yMDguMTQ2&","bulk_download_file_name":"Long_term_macrozoobenthos_changes_in_a_s.pdf","bulk_download_url":"https://d1wqtxts1xzle7.cloudfront.net/113238186/zettler_und_daunys-2007-limnologica-libre.pdf?1712860349=\u0026response-content-disposition=attachment%3B+filename%3DLong_term_macrozoobenthos_changes_in_a_s.pdf\u0026Expires=1732737170\u0026Signature=UnD-9ijDvq-hHq~zTPYDBGy60Fsk2ZUK6riaLN5u-ntDiFYzDIbonl-qr9rCAL2UdW0YaTceV3-RKvBMNowebhHQmr47qBOU2ksRUt4rLol6tTuS~Yd~Rbivfj7tG5KY5jMuStFee0pi~fTe89GQog-tiSX8JxRa-AUbJi68Gtr~~8WnVwR8t3G7LXxB-VhaOpgdobqHBDYZ0IwLfpe-3r7y1FiRYTiQK-c9Ive0VH3ojKP8saUypNrhC3CTu-72SLah1B4kS6GC-nJmJEI57tRideNIsHudRzAEYIdJcGjeKOWFW8hwp1C~P9Rk0P5k1R7VlChUHSWHi8D0B31dKg__\u0026Key-Pair-Id=APKAJLOHF5GGSLRBV4ZA"}],"research_interests":[{"id":402,"name":"Environmental Science","url":"https://www.academia.edu/Documents/in/Environmental_Science"},{"id":7710,"name":"Biology","url":"https://www.academia.edu/Documents/in/Biology"},{"id":9846,"name":"Ecology","url":"https://www.academia.edu/Documents/in/Ecology"},{"id":17825,"name":"Biodiversity","url":"https://www.academia.edu/Documents/in/Biodiversity"},{"id":157600,"name":"Water Framework Directive","url":"https://www.academia.edu/Documents/in/Water_Framework_Directive"},{"id":221822,"name":"Historical Data","url":"https://www.academia.edu/Documents/in/Historical_Data"},{"id":585173,"name":"Alien species","url":"https://www.academia.edu/Documents/in/Alien_species"},{"id":960649,"name":"Boreal","url":"https://www.academia.edu/Documents/in/Boreal"}],"urls":[{"id":41019521,"url":"https://doi.org/10.1016/j.limno.2006.12.004"}]}, dispatcherData: dispatcherData }); $(this).data('initialized', true); } }); $a.trackClickSource(".js-work-strip-work-link", "profile_work_strip") }); </script> <div class="js-work-strip profile--work_container" data-work-id="117361988"><div class="profile--work_thumbnail hidden-xs"><a class="js-work-strip-work-link" data-click-track="profile-work-strip-thumbnail" href="https://www.academia.edu/117361988/Modelling_the_material_uptake_and_deposition_of_the_Mytilus_edulis_in_the_Baltic_coastal_ecosystem"><img alt="Research paper thumbnail of Modelling the material uptake and deposition of the Mytilus edulis in the Baltic coastal ecosystem" class="work-thumbnail" src="https://a.academia-assets.com/images/blank-paper.jpg" /></a></div><div class="wp-workCard wp-workCard_itemContainer"><div class="wp-workCard_item wp-workCard--title"><a class="js-work-strip-work-link text-gray-darker" data-click-track="profile-work-strip-title" href="https://www.academia.edu/117361988/Modelling_the_material_uptake_and_deposition_of_the_Mytilus_edulis_in_the_Baltic_coastal_ecosystem">Modelling the material uptake and deposition of the Mytilus edulis in the Baltic coastal ecosystem</a></div><div class="wp-workCard_item"><span>Oceanological and Hydrobiological Studies</span><span>, 2003</span></div><div class="wp-workCard_item wp-workCard--actions"><span class="work-strip-bookmark-button-container"></span><span class="wp-workCard--action visible-if-viewed-by-owner inline-block" style="display: none;"><span class="js-profile-work-strip-edit-button-wrapper profile-work-strip-edit-button-wrapper" data-work-id="117361988"><a class="js-profile-work-strip-edit-button" tabindex="0"><span><i class="fa fa-pencil"></i></span><span>Edit</span></a></span></span><span id="work-strip-rankings-button-container"></span></div><div class="wp-workCard_item wp-workCard--stats"><span><span><span class="js-view-count view-count u-mr2x" data-work-id="117361988"><i class="fa fa-spinner fa-spin"></i></span><script>$(function () { var workId = 117361988; 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$(this).data('initialized', true); } }); $a.trackClickSource(".js-work-strip-work-link", "profile_work_strip") }); </script> <div class="js-work-strip profile--work_container" data-work-id="117361987"><div class="profile--work_thumbnail hidden-xs"><a class="js-work-strip-work-link" data-click-track="profile-work-strip-thumbnail" href="https://www.academia.edu/117361987/Marenzelleria_viridis_Verrill_1873_"><img alt="Research paper thumbnail of Marenzelleria viridis (Verrill, 1873)" class="work-thumbnail" src="https://a.academia-assets.com/images/blank-paper.jpg" /></a></div><div class="wp-workCard wp-workCard_itemContainer"><div class="wp-workCard_item wp-workCard--title"><a class="js-work-strip-work-link text-gray-darker" data-click-track="profile-work-strip-title" href="https://www.academia.edu/117361987/Marenzelleria_viridis_Verrill_1873_">Marenzelleria viridis (Verrill, 1873)</a></div><div class="wp-workCard_item wp-workCard--actions"><span class="work-strip-bookmark-button-container"></span><span class="wp-workCard--action visible-if-viewed-by-owner inline-block" style="display: none;"><span class="js-profile-work-strip-edit-button-wrapper profile-work-strip-edit-button-wrapper" data-work-id="117361987"><a class="js-profile-work-strip-edit-button" tabindex="0"><span><i class="fa fa-pencil"></i></span><span>Edit</span></a></span></span><span id="work-strip-rankings-button-container"></span></div><div class="wp-workCard_item wp-workCard--stats"><span><span><span class="js-view-count view-count u-mr2x" data-work-id="117361987"><i class="fa fa-spinner fa-spin"></i></span><script>$(function () { var workId = 117361987; 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$(this).data('initialized', true); } }); $a.trackClickSource(".js-work-strip-work-link", "profile_work_strip") }); </script> <div class="js-work-strip profile--work_container" data-work-id="117361986"><div class="profile--work_thumbnail hidden-xs"><a class="js-work-strip-work-link" data-click-track="profile-work-strip-thumbnail" href="https://www.academia.edu/117361986/Rating_species_sensitivity_throughout_gradient_systems_a_consistent_approach_for_the_Baltic_Sea"><img alt="Research paper thumbnail of Rating species sensitivity throughout gradient systems – a consistent approach for the Baltic Sea" class="work-thumbnail" src="https://a.academia-assets.com/images/blank-paper.jpg" /></a></div><div class="wp-workCard wp-workCard_itemContainer"><div class="wp-workCard_item wp-workCard--title"><a class="js-work-strip-work-link text-gray-darker" data-click-track="profile-work-strip-title" href="https://www.academia.edu/117361986/Rating_species_sensitivity_throughout_gradient_systems_a_consistent_approach_for_the_Baltic_Sea">Rating species sensitivity throughout gradient systems – a consistent approach for the Baltic Sea</a></div><div class="wp-workCard_item"><span>Ecological Indicators</span><span>, 2016</span></div><div class="wp-workCard_item"><span class="js-work-more-abstract-truncated">Abstract Evaluating the state of benthic communities has played an important role in water qualit...</span><a class="js-work-more-abstract" data-broccoli-component="work_strip.more_abstract" data-click-track="profile-work-strip-more-abstract" href="javascript:;"><span> more </span><span><i class="fa fa-caret-down"></i></span></a><span class="js-work-more-abstract-untruncated hidden">Abstract Evaluating the state of benthic communities has played an important role in water quality assessments. Indices incorporating species sensitivities, richness and densities are commonly applied. In Europe, the importance of benthic indices has increased in the last years with the implementation of the European Marine Strategy Framework Directive (MSFD) which at the same time demands the applicability of an index across regional scales. To date, environmental variability is rarely considered in benthic indices and most sensitivity rankings have the disadvantages of static values (i.e. the same value in all areas), expert judgement and a limited geographical range. This study presents species sensitivity values calculated along environmental gradients for the Baltic Sea. Sensitivities were calculated according to the procedure of the Benthic Quality Index (BQI). We created a matrix of subregions, classes of salinity, depth and gear to identify comparable subsets for data analysis. Altogether, 19 subsets were defined within the Baltic Sea basins. Sensitivity values were calculated for 329 species out of a total of 678 species that were recorded in this study. Sensitivity values of taxa vary between subsets as it was expected for different environmental conditions. Most sensitivity values can be assigned to species occurring in euhaline and polyhaline waters. Distribution of species with high and low sensitivity values differed along the salinity gradient. In euhaline waters more species with high sensitivity values occurred than species with low sensitivity values, while in mesohaline waters the ratio of high and low sensitivity values among species was almost equal. In oligohaline waters more species with lower sensitivity values were present. For the first time, sensitivity values were calculated for a large number of species using the same method for the entire Baltic Sea. This results in a Baltic-wide comprehensive set of sensitivity values based on a dataset across subregional borders, and divided along environmental gradients and gear type. The same principles can be applied to transient waters from rivers to coastal lagoons as well as to other environments with gradients of, e.g. hydrodynamic characteristics. Publicly available sensitivity values will increase transparency and support the improvement of state assessments under the MSFD.</span></div><div class="wp-workCard_item wp-workCard--actions"><span class="work-strip-bookmark-button-container"></span><span class="wp-workCard--action visible-if-viewed-by-owner inline-block" style="display: none;"><span class="js-profile-work-strip-edit-button-wrapper profile-work-strip-edit-button-wrapper" data-work-id="117361986"><a class="js-profile-work-strip-edit-button" tabindex="0"><span><i class="fa fa-pencil"></i></span><span>Edit</span></a></span></span><span id="work-strip-rankings-button-container"></span></div><div class="wp-workCard_item wp-workCard--stats"><span><span><span class="js-view-count view-count u-mr2x" data-work-id="117361986"><i class="fa fa-spinner fa-spin"></i></span><script>$(function () { var workId = 117361986; window.Academia.workViewCountsFetcher.queue(workId, function (count) { var description = window.$h.commaizeInt(count) + " " + window.$h.pluralize(count, 'View'); $(".js-view-count[data-work-id=117361986]").text(description); $(".js-view-count[data-work-id=117361986]").attr('title', description).tooltip(); }); });</script></span></span><span><span class="percentile-widget hidden"><span class="u-mr2x work-percentile"></span></span><script>$(function () { var workId = 117361986; window.Academia.workPercentilesFetcher.queue(workId, function (percentileText) { var container = $(".js-work-strip[data-work-id='117361986']"); container.find('.work-percentile').text(percentileText.charAt(0).toUpperCase() + percentileText.slice(1)); container.find('.percentile-widget').show(); container.find('.percentile-widget').removeClass('hidden'); }); });</script></span><span><script>$(function() { new Works.PaperRankView({ workId: 117361986, container: "", }); });</script></span></div><div id="work-strip-premium-row-container"></div></div></div><script> require.config({ waitSeconds: 90 })(["https://a.academia-assets.com/assets/wow_profile-f77ea15d77ce96025a6048a514272ad8becbad23c641fc2b3bd6e24ca6ff1932.js","https://a.academia-assets.com/assets/work_edit-ad038b8c047c1a8d4fa01b402d530ff93c45fee2137a149a4a5398bc8ad67560.js"], function() { // from javascript_helper.rb var dispatcherData = {} if (false){ window.WowProfile.dispatcher = window.WowProfile.dispatcher || _.clone(Backbone.Events); dispatcherData = { dispatcher: window.WowProfile.dispatcher, downloadLinkId: "-1" } } $('.js-work-strip[data-work-id=117361986]').each(function() { if (!$(this).data('initialized')) { new WowProfile.WorkStripView({ el: this, workJSON: {"id":117361986,"title":"Rating species sensitivity throughout gradient systems – a consistent approach for the Baltic Sea","translated_title":"","metadata":{"abstract":"Abstract Evaluating the state of benthic communities has played an important role in water quality assessments. 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Sensitivity values were calculated for 329 species out of a total of 678 species that were recorded in this study. Sensitivity values of taxa vary between subsets as it was expected for different environmental conditions. Most sensitivity values can be assigned to species occurring in euhaline and polyhaline waters. Distribution of species with high and low sensitivity values differed along the salinity gradient. In euhaline waters more species with high sensitivity values occurred than species with low sensitivity values, while in mesohaline waters the ratio of high and low sensitivity values among species was almost equal. In oligohaline waters more species with lower sensitivity values were present. For the first time, sensitivity values were calculated for a large number of species using the same method for the entire Baltic Sea. This results in a Baltic-wide comprehensive set of sensitivity values based on a dataset across subregional borders, and divided along environmental gradients and gear type. The same principles can be applied to transient waters from rivers to coastal lagoons as well as to other environments with gradients of, e.g. hydrodynamic characteristics. Publicly available sensitivity values will increase transparency and support the improvement of state assessments under the MSFD.","publisher":"Elsevier BV","publication_date":{"day":null,"month":null,"year":2016,"errors":{}},"publication_name":"Ecological Indicators"},"translated_abstract":"Abstract Evaluating the state of benthic communities has played an important role in water quality assessments. Indices incorporating species sensitivities, richness and densities are commonly applied. In Europe, the importance of benthic indices has increased in the last years with the implementation of the European Marine Strategy Framework Directive (MSFD) which at the same time demands the applicability of an index across regional scales. To date, environmental variability is rarely considered in benthic indices and most sensitivity rankings have the disadvantages of static values (i.e. the same value in all areas), expert judgement and a limited geographical range. This study presents species sensitivity values calculated along environmental gradients for the Baltic Sea. Sensitivities were calculated according to the procedure of the Benthic Quality Index (BQI). We created a matrix of subregions, classes of salinity, depth and gear to identify comparable subsets for data analysis. Altogether, 19 subsets were defined within the Baltic Sea basins. Sensitivity values were calculated for 329 species out of a total of 678 species that were recorded in this study. Sensitivity values of taxa vary between subsets as it was expected for different environmental conditions. Most sensitivity values can be assigned to species occurring in euhaline and polyhaline waters. Distribution of species with high and low sensitivity values differed along the salinity gradient. In euhaline waters more species with high sensitivity values occurred than species with low sensitivity values, while in mesohaline waters the ratio of high and low sensitivity values among species was almost equal. In oligohaline waters more species with lower sensitivity values were present. For the first time, sensitivity values were calculated for a large number of species using the same method for the entire Baltic Sea. This results in a Baltic-wide comprehensive set of sensitivity values based on a dataset across subregional borders, and divided along environmental gradients and gear type. The same principles can be applied to transient waters from rivers to coastal lagoons as well as to other environments with gradients of, e.g. hydrodynamic characteristics. Publicly available sensitivity values will increase transparency and support the improvement of state assessments under the MSFD.","internal_url":"https://www.academia.edu/117361986/Rating_species_sensitivity_throughout_gradient_systems_a_consistent_approach_for_the_Baltic_Sea","translated_internal_url":"","created_at":"2024-04-11T10:54:30.700-07:00","preview_url":null,"current_user_can_edit":null,"current_user_is_owner":null,"owner_id":64309884,"coauthors_can_edit":true,"document_type":"paper","co_author_tags":[],"downloadable_attachments":[],"slug":"Rating_species_sensitivity_throughout_gradient_systems_a_consistent_approach_for_the_Baltic_Sea","translated_slug":"","page_count":null,"language":"en","content_type":"Work","owner":{"id":64309884,"first_name":"Darius","middle_initials":null,"last_name":"Daunys","page_name":"DariusDaunys","domain_name":"independent","created_at":"2017-05-15T05:34:19.853-07:00","display_name":"Darius Daunys","url":"https://independent.academia.edu/DariusDaunys"},"attachments":[],"research_interests":[{"id":402,"name":"Environmental Science","url":"https://www.academia.edu/Documents/in/Environmental_Science"},{"id":47884,"name":"Biological Sciences","url":"https://www.academia.edu/Documents/in/Biological_Sciences"},{"id":58054,"name":"Environmental Sciences","url":"https://www.academia.edu/Documents/in/Environmental_Sciences"},{"id":138744,"name":"Ecological Indicators","url":"https://www.academia.edu/Documents/in/Ecological_Indicators"},{"id":260118,"name":"CHEMICAL SCIENCES","url":"https://www.academia.edu/Documents/in/CHEMICAL_SCIENCES"},{"id":410933,"name":"Baltic Sea","url":"https://www.academia.edu/Documents/in/Baltic_Sea"}],"urls":[{"id":41019520,"url":"https://api.elsevier.com/content/article/PII:S1470160X15005324?httpAccept=text/xml"}]}, dispatcherData: dispatcherData }); 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Baltic Sea Environmental Proceedings No. 138. Information included in this publication or extracts thereof are free for citing on the condition that the complete reference of the publication is given as stated above.","grobid_abstract_attachment_id":113238184},"translated_abstract":null,"internal_url":"https://www.academia.edu/117361984/Red_List_of_Baltic_Sea_underwater_biotopes_habitats_and_biotope_complexes","translated_internal_url":"","created_at":"2024-04-11T10:54:30.478-07:00","preview_url":null,"current_user_can_edit":null,"current_user_is_owner":null,"owner_id":64309884,"coauthors_can_edit":true,"document_type":"paper","co_author_tags":[],"downloadable_attachments":[{"id":113238184,"title":"","file_type":"pdf","scribd_thumbnail_url":"https://attachments.academia-assets.com/113238184/thumbnails/1.jpg","file_name":"BSEP138.pdf","download_url":"https://www.academia.edu/attachments/113238184/download_file?st=MTczMjczMzU3MCw4LjIyMi4yMDguMTQ2&st=MTczMjczMzU3MCw4LjIyMi4yMDguMTQ2&","bulk_download_file_name":"Red_List_of_Baltic_Sea_underwater_biotop.pdf","bulk_download_url":"https://d1wqtxts1xzle7.cloudfront.net/113238184/BSEP138-libre.pdf?1712860378=\u0026response-content-disposition=attachment%3B+filename%3DRed_List_of_Baltic_Sea_underwater_biotop.pdf\u0026Expires=1732737170\u0026Signature=AuQM3ymZ-Ly1KNsowYBt4hLFf1pfPjizkMfHQzCdfsNKD7a1pfixqdzQ4vYTekvZuyYjkc9z-03s7OzQgSaoUHPWopImk5QPWmtpXpFjQsttPtbwD-IE~9o8A1sM6QqV82qGOfzrdu3X6uOkCqZSpkozWRAl1iXP~-RI4J4x6xhbpeR6C3w8w~i7YuXEj2Wuxu8dzWGD9uoYFWiqjBejwA5dkqK8rtpFbCjmvEJtFZQOoGCzWUDXovwx5c6FjAgaqZgkd-rC51sjhgxiYWr-vs2qE7x8BWuQgu~JuHBUt2Q5utMFCBoaBgGxlWcRODfn~2YOPlhQZ8nfbcw89TeYXQ__\u0026Key-Pair-Id=APKAJLOHF5GGSLRBV4ZA"}],"slug":"Red_List_of_Baltic_Sea_underwater_biotopes_habitats_and_biotope_complexes","translated_slug":"","page_count":74,"language":"en","content_type":"Work","owner":{"id":64309884,"first_name":"Darius","middle_initials":null,"last_name":"Daunys","page_name":"DariusDaunys","domain_name":"independent","created_at":"2017-05-15T05:34:19.853-07:00","display_name":"Darius Daunys","url":"https://independent.academia.edu/DariusDaunys"},"attachments":[{"id":113238184,"title":"","file_type":"pdf","scribd_thumbnail_url":"https://attachments.academia-assets.com/113238184/thumbnails/1.jpg","file_name":"BSEP138.pdf","download_url":"https://www.academia.edu/attachments/113238184/download_file?st=MTczMjczMzU3MCw4LjIyMi4yMDguMTQ2&st=MTczMjczMzU3MCw4LjIyMi4yMDguMTQ2&","bulk_download_file_name":"Red_List_of_Baltic_Sea_underwater_biotop.pdf","bulk_download_url":"https://d1wqtxts1xzle7.cloudfront.net/113238184/BSEP138-libre.pdf?1712860378=\u0026response-content-disposition=attachment%3B+filename%3DRed_List_of_Baltic_Sea_underwater_biotop.pdf\u0026Expires=1732737170\u0026Signature=AuQM3ymZ-Ly1KNsowYBt4hLFf1pfPjizkMfHQzCdfsNKD7a1pfixqdzQ4vYTekvZuyYjkc9z-03s7OzQgSaoUHPWopImk5QPWmtpXpFjQsttPtbwD-IE~9o8A1sM6QqV82qGOfzrdu3X6uOkCqZSpkozWRAl1iXP~-RI4J4x6xhbpeR6C3w8w~i7YuXEj2Wuxu8dzWGD9uoYFWiqjBejwA5dkqK8rtpFbCjmvEJtFZQOoGCzWUDXovwx5c6FjAgaqZgkd-rC51sjhgxiYWr-vs2qE7x8BWuQgu~JuHBUt2Q5utMFCBoaBgGxlWcRODfn~2YOPlhQZ8nfbcw89TeYXQ__\u0026Key-Pair-Id=APKAJLOHF5GGSLRBV4ZA"}],"research_interests":[],"urls":[]}, dispatcherData: dispatcherData }); $(this).data('initialized', true); } }); $a.trackClickSource(".js-work-strip-work-link", "profile_work_strip") }); </script> <div class="js-work-strip profile--work_container" data-work-id="117361983"><div class="profile--work_thumbnail hidden-xs"><a class="js-work-strip-work-link" data-click-track="profile-work-strip-thumbnail" href="https://www.academia.edu/117361983/Long_term_macrozoobenthos_changes_in_a_shallow_boreal_lagoon_Comparison_of_a_recent_biodiversity_inventory_with_historical_data"><img alt="Research paper thumbnail of Long-term macrozoobenthos changes in a shallow boreal lagoon: Comparison of a recent biodiversity inventory with historical data" class="work-thumbnail" src="https://attachments.academia-assets.com/113238187/thumbnails/1.jpg" /></a></div><div class="wp-workCard wp-workCard_itemContainer"><div class="wp-workCard_item wp-workCard--title"><a class="js-work-strip-work-link text-gray-darker" data-click-track="profile-work-strip-title" href="https://www.academia.edu/117361983/Long_term_macrozoobenthos_changes_in_a_shallow_boreal_lagoon_Comparison_of_a_recent_biodiversity_inventory_with_historical_data">Long-term macrozoobenthos changes in a shallow boreal lagoon: Comparison of a recent biodiversity inventory with historical data</a></div><div class="wp-workCard_item"><span>Limnologica</span><span>, 2007</span></div><div class="wp-workCard_item wp-workCard--actions"><span class="work-strip-bookmark-button-container"></span><a id="662d166c6fe20cd791bbeeea1ace71c4" class="wp-workCard--action" rel="nofollow" data-click-track="profile-work-strip-download" data-download="{"attachment_id":113238187,"asset_id":117361983,"asset_type":"Work","button_location":"profile"}" href="https://www.academia.edu/attachments/113238187/download_file?st=MTczMjczMzU3MCw4LjIyMi4yMDguMTQ2&st=MTczMjczMzU3MCw4LjIyMi4yMDguMTQ2&s=profile"><span><i class="fa fa-arrow-down"></i></span><span>Download</span></a><span class="wp-workCard--action visible-if-viewed-by-owner inline-block" style="display: none;"><span class="js-profile-work-strip-edit-button-wrapper profile-work-strip-edit-button-wrapper" data-work-id="117361983"><a class="js-profile-work-strip-edit-button" tabindex="0"><span><i class="fa fa-pencil"></i></span><span>Edit</span></a></span></span><span id="work-strip-rankings-button-container"></span></div><div class="wp-workCard_item wp-workCard--stats"><span><span><span class="js-view-count view-count u-mr2x" data-work-id="117361983"><i class="fa fa-spinner fa-spin"></i></span><script>$(function () { var workId = 117361983; 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In this paper, two historical biodiversity datasets (from 1920s and 1950s) and results from the recent inventory are used to trace the long-term changes of the macrozoobenthos in the eutrophic boreal lagoon of the Baltic Sea. In comparison of datasets the highest congruence was obtained for molluscs and malacostracan crustaceans, which also had a similar level of taxonomic emphasis between studies. Considering inconsistencies in methodology and taxonomic determination, only few species extinctions in these groups did likely occur during the last 100 years. Two amphipod species (Gammarus pulex and Gammarus lacustris) were not found during the recent survey, whereas five new species of this taxonomic group occurred in the lagoon since 1950s. The causes of these extinctions remain unclear; however displacement by established new amphipods cannot be excluded. Theodoxus fluviatilis was recently recorded in the very restricted area of the lagoon, while in earlier studies the species was mentioned as common and widely distributed in the water body. On the other hand, 10 gastropod species and 9 bivalves were reported for the first time in the lagoon and most likely have been overlooked in earlier surveys. Approximately 10% of the species have their origin outside the Baltic Sea basin and the number of invasions considerably exceeds the number of likely extinctions. 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To comparatively analyze the effects of an exotic and a native polychaete burrower on sediment-water exchanges, two laboratory experiments were performed. In the first experiment, the invasive spionid polychaete Marenzelleria neglecta was added to defaunated sediments and fluxes of the inert tracer (bromide, Br−) were measured to quantify the effects of irrigation by the worm on the tracer transport. In the second experiment, M. neglecta or the native polychaete Hediste diversicolor were introduced to a relatively diverse Baltic soft-bottom macrofauna community. The effect of species on fluxes of reactive solutes (ammonium, NH4+, and phosphate, PO43−) and transport rates of Br− was estimated. The results indicate different invasion effects depending on the characteristics of the recipient habitat. 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To comparatively analyze the effects of an exotic and a native polychaete burrower on sediment-water exchanges, two laboratory experiments were performed. In the first experiment, the invasive spionid polychaete Marenzelleria neglecta was added to defaunated sediments and fluxes of the inert tracer (bromide, Br−) were measured to quantify the effects of irrigation by the worm on the tracer transport. In the second experiment, M. neglecta or the native polychaete Hediste diversicolor were introduced to a relatively diverse Baltic soft-bottom macrofauna community. The effect of species on fluxes of reactive solutes (ammonium, NH4+, and phosphate, PO43−) and transport rates of Br− was estimated. The results indicate different invasion effects depending on the characteristics of the recipient habitat. I...","publisher":"MDPI AG","publication_date":{"day":null,"month":null,"year":2019,"errors":{}},"publication_name":"Water"},"translated_abstract":"Different irrigation or ventilation strategies by macrofauna may provide a competitive advantage to tolerant species invading impacted benthic systems and alter benthic-pelagic coupling. To comparatively analyze the effects of an exotic and a native polychaete burrower on sediment-water exchanges, two laboratory experiments were performed. In the first experiment, the invasive spionid polychaete Marenzelleria neglecta was added to defaunated sediments and fluxes of the inert tracer (bromide, Br−) were measured to quantify the effects of irrigation by the worm on the tracer transport. In the second experiment, M. neglecta or the native polychaete Hediste diversicolor were introduced to a relatively diverse Baltic soft-bottom macrofauna community. The effect of species on fluxes of reactive solutes (ammonium, NH4+, and phosphate, PO43−) and transport rates of Br− was estimated. The results indicate different invasion effects depending on the characteristics of the recipient habitat. 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