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      Global marine biosecurity and ship lay-ups: intensifying effects of trade disruptions

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          Abstract

          Recent global trade disruptions, due to blockage of the Suez Canal and cascading effects of COVID-19, have altered the movement patterns of commercial ships and may increase worldwide invasions of marine non-indigenous species. Organisms settle on the hulls and underwater surfaces of vessels and can accumulate rapidly, especially when vessels remain stationary during lay-ups and delays. Once present, organisms can persist on vessels for long-periods (months to years), with the potential to release propagules and seed invasions as ships visit ports across the global transportation network. Shipborne propagules also may be released in increasing numbers during extended vessel residence times at port or anchor. Thus, the large scale of shipping disruptions, impacting thousands of vessels and geographic locations and still on-going for over two years, may elevate invasion rates in coastal ecosystems in the absence of policy and management efforts to prevent this outcome. Concerted international and national biosecurity actions, mobilizing existing frameworks and tools with due diligence, are urgently needed to address a critical gap and abate the associated invasion risks.

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          Invasion of Coastal Marine Communities in North America: Apparent Patterns, Processes, and Biases

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            Trends in the detection of aquatic non-indigenous species across global marine, estuarine and freshwater ecosystems: A 50-year perspective

            Aim: The introduction of aquatic non-indigenous species (ANS) has become a major driver for global changes in species biogeography. We examined spatial patterns and temporal trends of ANS detections since 1965 to inform conservation policy and management. Location: Global. Methods: We assembled an extensive dataset of first records of detection of ANS (1965–2015) across 49 aquatic ecosystems, including the (a) year of first collection, (b) population status and (c) potential pathway(s) of introduction. Data were analysed at global and regional levels to assess patterns of detection rate, richness and transport pathways. Results: An annual mean of 43 (±16 SD) primary detections of ANS occurred–one new detection every 8.4 days for 50 years. The global rate of detections was relatively stable during 1965–1995, but increased rapidly after this time, peaking at roughly 66 primary detections per year during 2005–2010 and then declining marginally. Detection rates were variable within and across regions through time. Arthropods, molluscs and fishes were the most frequently reported ANS. Most ANS were likely introduced as stowaways in ships’ ballast water or biofouling, although direct evidence is typically absent. Main conclusions: This synthesis highlights the magnitude of recent ANS detections, yet almost certainly represents an underestimate as many ANS go unreported due to limited search effort and diminishing taxonomic expertise. Temporal rates of detection are also confounded by reporting lags, likely contributing to the lower detection rate observed in recent years. There is a critical need to implement standardized, repeated methods across regions and taxa to improve the quality of global-scale comparisons and sustain core measures over longer time-scales. It will be fundamental to fill in knowledge gaps given that invasion data representing broad regions of the world's oceans are not yet readily available and to maintain knowledge pipelines for adaptive management.
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              Fouling and ships' hulls: how changing circumstances and spawning events may result in the spread of exotic species.

              Organisms fouling ships' hulls are continually in transit worldwide. Although effective antifouling paints incorporating organotins have considerably reduced fouling biomass these paints have a limited period of effectiveness, which may be less than the ships' inter-docking period, depending on sea temperature and abrasion. Vessels immersed over several years can allow fouling communities to develop and spread beyond their native distribution. This process of establishment is not fully understood. This review proposes that short rapid turn-around of vessels with mature attached biota can result in synchronized spawnings and production of sufficient zygotes to form a founder population. Spawning may be induced by changes in temperature or salinity on entry into a port, according to season. The diversity of taxa in transit on ships' hulls includes commercial molluscs, which have the potential to transmit their diseases or pests to port regions. Several factors may act in the further enhancement of exotic species establishment including changes of in-port berthing regions to more marine conditions. Ships today are generally larger, and faster, and have a high frequency of port visits thereby increasing the number of spawning opportunities, perhaps with a larger inoculum size. With trade expansion, new trading routes, political events and changes in climate, new pathways for invasion will emerge. Greater controls on industrial discharges, improved treatments of urban wastes and better management of waste runoff into rivers as well as a phasing out of organotin antifoulants will mean a reduced toxicity in port regions. This may enable a smaller inoculum to colonize by creating opportunities for establishment not present in the previous 25 years. Some invaders will have unwanted consequences for the environment, economies and human health.
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                Author and article information

                Contributors
                ruizg@si.edu
                Journal
                Biol Invasions
                Biol Invasions
                Biological Invasions
                Springer International Publishing (Cham )
                1387-3547
                1573-1464
                14 July 2022
                14 July 2022
                : 1-6
                Affiliations
                [1 ]GRID grid.419533.9, ISNI 0000 0000 8612 0361, Smithsonian Environmental Research Center, ; Edgewater, MD USA
                [2 ]GRID grid.12136.37, ISNI 0000 0004 1937 0546, The Steinhardt Museum of Natural History and Israel National Center for Biodiversity Studies, Tel Aviv University, ; Tel Aviv, Israel
                [3 ]GRID grid.418703.9, ISNI 0000 0001 0740 4700, Cawthron Institute, ; Nelson, New Zealand
                [4 ]GRID grid.10939.32, ISNI 0000 0001 0943 7661, Pärnu College, , University of Tartu, ; Pärnu, Estonia
                [5 ]GRID grid.5170.3, ISNI 0000 0001 2181 8870, National Institute of Aquatic Resources, Technical University of Denmark, ; Lyngby, Denmark
                [6 ]GRID grid.291951.7, ISNI 0000 0000 8750 413X, Chesapeake Biological Laboratory, , University of Maryland Center for Environmental Science, ; Solomons, Maryland, USA
                [7 ]GRID grid.447119.e, ISNI 0000 0001 2182 6272, Williams College-Mystic Seaport Ocean and Coastal Studies Program, ; Mystic, CT USA
                Author information
                http://orcid.org/0000-0003-2499-441X
                Article
                2870
                10.1007/s10530-022-02870-y
                9281272
                69e70681-5a59-4c9a-98f9-2f0e9d3e8f76
                © This is a U.S. Government work and not under copyright protection in the US; foreign copyright protection may apply 2022

                Open AccessThis article is licensed under a Creative Commons Attribution 4.0 International License, which permits use, sharing, adaptation, distribution and reproduction in any medium or format, as long as you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons licence, and indicate if changes were made. The images or other third party material in this article are included in the article's Creative Commons licence, unless indicated otherwise in a credit line to the material. If material is not included in the article's Creative Commons licence and your intended use is not permitted by statutory regulation or exceeds the permitted use, you will need to obtain permission directly from the copyright holder. To view a copy of this licence, visit http://creativecommons.org/licenses/by/4.0/.

                History
                : 17 December 2021
                : 28 June 2022
                Categories
                Perspectives and Paradigms

                biofouling,biosecurity,covid-19,trade disruptions,shipping,suez canal

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