For Observing Harmful Algal Blooms
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Effects of the Filter-Feeding Benthic Bivalve Corbicula Fluminea
water Article Effects of the Filter-Feeding Benthic Bivalve Corbicula fluminea on Plankton Community and Water Quality in Aquatic Ecosystems: A Mesocosm Study Yuqin Rong 1,2, Yali Tang 1,2,† , Lijuan Ren 1,2, William D Taylor 3 , Vladimir Razlutskij 4, Luigi Naselli-Flores 5 , Zhengwen Liu 1,6,7,* and Xiufeng Zhang 1,2,* 1 Department of Ecology and Institute of Hydrobiology, Jinan University, Guangzhou 510632, China; [email protected] (Y.R.); [email protected] (Y.T.); [email protected] (L.R.) 2 Engineering Research Center of Tropical and Subtropical Aquatic Ecological Engineering, Ministry of Education, Guangzhou 510632, China 3 Department of Biology, University of Waterloo, Waterloo, ON N2L 3G1, Canada; [email protected] 4 State Scientific and Production Amalgamation Scientific-Practical Center of the National Academy of Sciences of Belarus for Biological Resources, 220072 Minsk, Belarus; [email protected] 5 Department STEBICEF, University of Palermo, 90123 Palermo, Italy; [email protected] 6 Sino-Danish Centre for Education and Research (SDC), Beijing 100070, China 7 State Key Laboratory of Lake Science and Environment, Institute of Geography and Limnology, Chinese Academy of Sciences, Nanjing 210008, China * Correspondence: [email protected] (Z.L.); [email protected] (X.Z.) † The author contributed equally to this work. Abstract: The influence of filter-feeding bivalves on plankton communities, nutrients, and water Citation: Rong, Y.; Tang, Y.; Ren, L.; quality in a given aquatic ecosystem is so profound that they can be considered ecosystem engineers. Taylor, W.D; Razlutskij, V.; In a 70-day mesocosm experiment, we tested the hypothesis that Corbicula fluminea would change Naselli-Flores, L.; Liu, Z.; Zhang, X. -
Effects of Eutrophication on Stream Ecosystems
EFFECTS OF EUTROPHICATION ON STREAM ECOSYSTEMS Lei Zheng, PhD and Michael J. Paul, PhD Tetra Tech, Inc. Abstract This paper describes the effects of nutrient enrichment on the structure and function of stream ecosystems. It starts with the currently well documented direct effects of nutrient enrichment on algal biomass and the resulting impacts on stream chemistry. The paper continues with an explanation of the less well documented indirect ecological effects of nutrient enrichment on stream structure and function, including effects of excess growth on physical habitat, and alterations to aquatic life community structure from the microbial assemblage to fish and mammals. The paper also dicusses effects on the ecosystem level including changes to productivity, respiration, decomposition, carbon and other geochemical cycles. The paper ends by discussing the significance of these direct and indirect effects of nutrient enrichment on designated uses - especially recreational, aquatic life, and drinking water. 2 1. Introduction 1.1 Stream processes Streams are all flowing natural waters, regardless of size. To understand the processes that influence the pattern and character of streams and reduce natural variation of different streams, several stream classification systems (including ecoregional, fluvial geomorphological, and stream order classification) have been adopted by state and national programs. Ecoregional classification is based on geology, soils, geomorphology, dominant land uses, and natural vegetation (Omernik 1987). Fluvial geomorphological classification explains stream and slope processes through the application of physical principles. Rosgen (1994) classified stream channels in the United States into seven major stream types based on morphological characteristics, including entrenchment, gradient, width/depth ratio, and sinuosity in various land forms. -
The Plankton Lifeform Extraction Tool: a Digital Tool to Increase The
Discussions https://doi.org/10.5194/essd-2021-171 Earth System Preprint. Discussion started: 21 July 2021 Science c Author(s) 2021. CC BY 4.0 License. Open Access Open Data The Plankton Lifeform Extraction Tool: A digital tool to increase the discoverability and usability of plankton time-series data Clare Ostle1*, Kevin Paxman1, Carolyn A. Graves2, Mathew Arnold1, Felipe Artigas3, Angus Atkinson4, Anaïs Aubert5, Malcolm Baptie6, Beth Bear7, Jacob Bedford8, Michael Best9, Eileen 5 Bresnan10, Rachel Brittain1, Derek Broughton1, Alexandre Budria5,11, Kathryn Cook12, Michelle Devlin7, George Graham1, Nick Halliday1, Pierre Hélaouët1, Marie Johansen13, David G. Johns1, Dan Lear1, Margarita Machairopoulou10, April McKinney14, Adam Mellor14, Alex Milligan7, Sophie Pitois7, Isabelle Rombouts5, Cordula Scherer15, Paul Tett16, Claire Widdicombe4, and Abigail McQuatters-Gollop8 1 10 The Marine Biological Association (MBA), The Laboratory, Citadel Hill, Plymouth, PL1 2PB, UK. 2 Centre for Environment Fisheries and Aquacu∑lture Science (Cefas), Weymouth, UK. 3 Université du Littoral Côte d’Opale, Université de Lille, CNRS UMR 8187 LOG, Laboratoire d’Océanologie et de Géosciences, Wimereux, France. 4 Plymouth Marine Laboratory, Prospect Place, Plymouth, PL1 3DH, UK. 5 15 Muséum National d’Histoire Naturelle (MNHN), CRESCO, 38 UMS Patrinat, Dinard, France. 6 Scottish Environment Protection Agency, Angus Smith Building, Maxim 6, Parklands Avenue, Eurocentral, Holytown, North Lanarkshire ML1 4WQ, UK. 7 Centre for Environment Fisheries and Aquaculture Science (Cefas), Lowestoft, UK. 8 Marine Conservation Research Group, University of Plymouth, Drake Circus, Plymouth, PL4 8AA, UK. 9 20 The Environment Agency, Kingfisher House, Goldhay Way, Peterborough, PE4 6HL, UK. 10 Marine Scotland Science, Marine Laboratory, 375 Victoria Road, Aberdeen, AB11 9DB, UK. -
Microscale Ecology Regulates Particulate Organic Matter Turnover in Model Marine Microbial Communities
ARTICLE DOI: 10.1038/s41467-018-05159-8 OPEN Microscale ecology regulates particulate organic matter turnover in model marine microbial communities Tim N. Enke1,2, Gabriel E. Leventhal 1, Matthew Metzger1, José T. Saavedra1 & Otto X. Cordero1 The degradation of particulate organic matter in the ocean is a central process in the global carbon cycle, the mode and tempo of which is determined by the bacterial communities that 1234567890():,; assemble on particle surfaces. Here, we find that the capacity of communities to degrade particles is highly dependent on community composition using a collection of marine bacteria cultured from different stages of succession on chitin microparticles. Different particle degrading taxa display characteristic particle half-lives that differ by ~170 h, comparable to the residence time of particles in the ocean’s mixed layer. Particle half-lives are in general longer in multispecies communities, where the growth of obligate cross-feeders hinders the ability of degraders to colonize and consume particles in a dose dependent manner. Our results suggest that the microscale community ecology of bacteria on particle surfaces can impact the rates of carbon turnover in the ocean. 1 Department of Civil and Environmental Engineering, Massachusetts Institute of Technology, Cambridge, MA 02139, USA. 2 Department of Environmental Systems Science, ETH Zurich, Zürich 8092, Switzerland. Correspondence and requests for materials should be addressed to O.X.C. (email: [email protected]) NATURE COMMUNICATIONS | (2018) 9:2743 | DOI: 10.1038/s41467-018-05159-8 | www.nature.com/naturecommunications 1 ARTICLE NATURE COMMUNICATIONS | DOI: 10.1038/s41467-018-05159-8 earning how the composition of ecological communities the North Pacific gyre20. -
Save the Reef
Save the Reef A member group of Lock the Gate Alliance www.savethereef.net.au Committee Secretary Senate Standing Committees on Environment and Communications PO Box 6100 Parliament House Canberra ACT 2600 Phone: +61 2 6277 3526 Fax: +61 2 6277 5818 [email protected] Submission to the Senate Inquiry on The adequacy of the Australian and Queensland Governments’ efforts to stop the rapid decline of the Great Barrier Reef, including but not limited to: Points a–k. Save the Reef would like to thank this committee for the opportunity to make a submission and would also like to speak further if there is an opportunity at any public hearings. The Great Barrier Reef is Australia’s greatest natural asset. It is a tourism mecca, a 6 billion dollar economic boon as well as a scientific wonderland. It is a World Heritage Listed property and an acknowledged world wonder. The Great Barrier Reef is part of Australia’s very identity. We are failing to protect the Great Barrier Reef. The efforts to stop the rapid decline of the Great Barrier Reef are grossly inadequate. It demonstrates that our current system for protecting the environment is broken. Environmental impact statements, conditions, offsets, regulations, enforcement and even the EPBC act, processes meant to protect the environment are being subverted and the impact is apparent. The holes in the “Swiss Cheese” are lining up and have allowed and are continuing to allow further destruction of the Great Barrier Reef when it needs our protection the most. The recent developments in Gladstone are a clear demonstration of the failure of our systems. -
Plankton Community Composition, Organic Carbon and Thorium-234 Particle Size Distributions, and Particle Export in the Sargasso Sea
Journal of Marine Research, 67, 845–868, 2009 Plankton community composition, organic carbon and thorium-234 particle size distributions, and particle export in the Sargasso Sea by H. S. Brew1, S. B. Moran1,2, M. W. Lomas3 and A. B. Burd4 ABSTRACT Measurements of plankton community composition (eight planktonic groups), particle size- fractionated (10, 20, 53, 70, and 100-m Nitex screens) distributions of organic carbon (OC) and 234Th, and particle export of OC and 234Th are reported over a seasonal cycle (2006–2007) from the Bermuda Atlantic Time-Series (BATS) site. Results indicate a convergence of the particle size distributions of OC and 234Th during the winter-spring bloom period (January–March, 2007). The observed convergence of these particle size distributions is directly correlated to the depth-integrated abundance of autotrophic pico-eukaryotes (r ϭ 0.97, P Ͻ 0.05) and, to a lesser extent, Synechococcus (r ϭ 0.85, P ϭ 0.14). In addition, there are positive correlations between the sediment trap flux of OC and 234Th at 150 m and the depth-integrated abundance of pico-eukaryotes (r ϭ 0.94, P ϭ 0.06 for OC, and r ϭ 0.98, P Ͻ 0.05 for 234Th) and Synechococcus (r ϭ 0.95, P ϭ 0.05 for OC, and r ϭ 0.94, P ϭ 0.06 for 234Th). An implication of these observations and recent modeling studies (Richardson and Jackson, 2007) is that, although small in size, pico-plankton may influence large particle export from the surface waters of the subtropical Atlantic. -
A View of Physical Mechanisms for Transporting Harmful Algal Blooms to T Massachusetts Bay ⁎ Yu Zhanga, , Changsheng Chenb, Pengfei Xueb,1, Robert C
Marine Pollution Bulletin 154 (2020) 111048 Contents lists available at ScienceDirect Marine Pollution Bulletin journal homepage: www.elsevier.com/locate/marpolbul A view of physical mechanisms for transporting harmful algal blooms to T Massachusetts Bay ⁎ Yu Zhanga, , Changsheng Chenb, Pengfei Xueb,1, Robert C. Beardsleyc, Peter J.S. Franksd a College of Marine Sciences, Shanghai Ocean University, Shanghai 201306, PR China b School for Marine Science and Technology, University of Massachusetts-Dartmouth, New Bedford, MA 02744, USA c Department of Physical Oceanography, Woods Hole Oceanographic Institution, Woods Hole, MA 02543, USA d Integrative Oceanography Division, Scripps Institution of Oceanography, University of California San Diego, La Jolla, CA 92093, USA ARTICLE INFO ABSTRACT Keywords: Physical dynamics of Harmful Algal Blooms in Massachusetts Bay in May 2005 and 2008 were examined by the Harmful algal bloom simulated results. Reverse particle-tracking experiments suggest that the toxic phytoplankton mainly originated Massachusetts Bay from the Bay of Fundy in 2005 and the western Maine coastal region and its local rivers in 2008. Mechanism Ocean modeling studies suggest that the phytoplankton were advected by the Gulf of Maine Coastal Current (GMCC). In 2005, Lagrangian flow Nor'easters increased the cross-shelf surface elevation gradient over the northwestern shelf. This intensified the Eastern and Western MCC to form a strong along-shelf current from the Bay of Fundy to Massachusetts Bay. In 2008, both Eastern and Western MCC were established with a partial separation around Penobscot Bay before the outbreak of the bloom. The northeastward winds were too weak to cancel or reverse the cross-shelf sea surface gradient, so that the Western MCC carried the algae along the slope into Massachusetts Bay. -
Sample Chapter Algal Blooms
ALGAL BLOOMS 7 Observations and Remote Sensing. http://dx.doi.org/10.1109/ energy and material transport through the food web, and JSTARS.2013.2265255. they also play an important role in the vertical flux of Pack, R. T., Brooks, V., Young, J., Vilaca, N., Vatslid, S., Rindle, P., material out of the surface waters. These blooms are Kurz, S., Parrish, C. E., Craig, R., and Smith, P. W., 2012. An “ ” overview of ALS technology. In Renslow, M. S. (ed.), Manual distinguished from those that are deemed harmful. of Airborne Topographic Lidar. Bethesda: ASPRS Press. Algae form harmful algal blooms, or HABs, when either Sithole, G., and Vosselman, G., 2004. Experimental comparison of they accumulate in massive amounts that alone cause filter algorithms for bare-Earth extraction from airborne laser harm to the ecosystem or the composition of the algal scanning point clouds. ISPRS Journal of Photogrammetry and community shifts to species that make compounds Remote Sensing, 59,85–101. (including toxins) that disrupt the normal food web or to Shan, J., and Toth, C., 2009. Topographic Laser Ranging and Scanning: Principles and Processes. Boca Raton: CRC Press. species that can harm human consumers (Glibert and Slatton, K. C., Carter, W. E., Shrestha, R. L., and Dietrich, W., 2007. Pitcher, 2001). HABs are a broad and pervasive problem, Airborne laser swath mapping: achieving the resolution and affecting estuaries, coasts, and freshwaters throughout the accuracy required for geosurficial research. Geophysical world, with effects on ecosystems and human health, and Research Letters, 34,1–5. on economies, when these events occur. This entry Wehr, A., and Lohr, U., 1999. -
Open Ocean Dead-Zones in the Tropical J I Northeast Atlantic
Discussion Paper | Discussion Paper | Discussion Paper | Discussion Paper | Biogeosciences Discuss., 11, 17391–17411, 2014 www.biogeosciences-discuss.net/11/17391/2014/ doi:10.5194/bgd-11-17391-2014 BGD © Author(s) 2014. CC Attribution 3.0 License. 11, 17391–17411, 2014 This discussion paper is/has been under review for the journal Biogeosciences (BG). Open ocean Please refer to the corresponding final paper in BG if available. dead-zones Open ocean dead-zone in the tropical J. Karstensen et al. North Atlantic Ocean Title Page 1 1 1 1 1 2 J. Karstensen , B. Fiedler , F. Schütte , P. Brandt , A. Körtzinger , G. Fischer , Abstract Introduction R. Zantopp1, J. Hahn1, M. Visbeck1, and D. Wallace3 Conclusions References 1GEOMAR Helmholtz Centre for Ocean Research Kiel, Kiel, Germany Tables Figures 2Faculty of Geosciences and MARUM, University of Bremen, Bremen, Germany 3Halifax Marine Research Institute (HMRI), Halifax, Canada J I Received: 3 November 2014 – Accepted: 13 November 2014 – Published: 12 December 2014 J I Correspondence to: J. Karstensen ([email protected]) Back Close Published by Copernicus Publications on behalf of the European Geosciences Union. Full Screen / Esc Printer-friendly Version Interactive Discussion 17391 Discussion Paper | Discussion Paper | Discussion Paper | Discussion Paper | Abstract BGD The intermittent appearances of low oxygen environments are a particular thread for marine ecosystems. Here we present first observations of unexpected low (< 11, 17391–17411, 2014 2 µmolkg−1) oxygen environments in the open waters of the eastern tropical North −1 5 Atlantic, a region where typically oxygen concentration does not fall below 40 µmolkg . Open ocean The low oxygen zones are created just below the mixed-layer, in the euphotic zone of dead-zones high productive cyclonic and anticyclonic-modewater eddies. -
Harmful Algal Bloom Response Program
What are HABs? • Blue-green algae are bacteria that grow in water, contain chlorophyll, and can photosynthesize. They are not a new occurrence. WHEN IN DOUBT, STAY OUT! Kansas Department of Health • When these bacteria reproduce rapidly, For additional information: and Environment it can create a Harmful Algal Bloom (HAB). Please visit • HABs can sometimes produce toxins www.kdheks.gov/algae-illness. Harmful that affect people, pets, livestock, and Or call the KDHE HAB Hotline at wildlife. The toxins can affect the skin, 785-296-1664. liver, and nervous system. Algal Bloom • People and animals may be exposed to toxins via ingestion, skin contact, or Response inhalation of contaminated water. Program • The most common human health effects from HABs can include vomiting, diarrhea, skin rashes, eye irritation, and respiratory symptoms. • Boiling water does not remove or Department of Health inactivate toxins from blue-green algae, and Environment and there is no known antidote. • Animal deaths due to HAB toxins have Department of Health been documented, so: and Environment When in doubt, stay out! To protect and improve the health and environment of all Kansans. How else is KDHE working to What causes HABs? HAB Advisory Levels prevent HABs? Blue-green algae are a natural part of water- Threshold Levels based ecosystems. They become a problem Harmful Algal Blooms thrive in the presence when nutrients (phosphorus and nitrogen) are Watch Warning Closure of excess nutrients such as nitrogen and present in concentrations above what would phosphorus. Thus, KDHE continually works to occur naturally. Under these conditions, algae blue green reduce nutrient input and improve overall can grow very quickly to extreme numbers, cell counts 80,000 250,000 10,000,000 water quality through a series of interrelated resulting in a Harmful Algal Bloom. -
Multi-System Analysis of Nitrogen Use by Phytoplankton and Heterotrophic Bacteria
W&M ScholarWorks Dissertations, Theses, and Masters Projects Theses, Dissertations, & Master Projects 2009 Multi-system analysis of nitrogen use by phytoplankton and heterotrophic bacteria Paul B. Bradley College of William and Mary - Virginia Institute of Marine Science Follow this and additional works at: https://scholarworks.wm.edu/etd Part of the Biogeochemistry Commons, and the Marine Biology Commons Recommended Citation Bradley, Paul B., "Multi-system analysis of nitrogen use by phytoplankton and heterotrophic bacteria" (2009). Dissertations, Theses, and Masters Projects. Paper 1539616580. https://dx.doi.org/doi:10.25773/v5-8hgt-2180 This Dissertation is brought to you for free and open access by the Theses, Dissertations, & Master Projects at W&M ScholarWorks. It has been accepted for inclusion in Dissertations, Theses, and Masters Projects by an authorized administrator of W&M ScholarWorks. For more information, please contact [email protected]. Multi-System Analysis of Nitrogen Use by Phytoplankton and Heterotrophic Bacteria A Dissertation Presented to The Faculty of the School of Marine Science The College of William and Mary in Virginia In Partial Fulfillment of the Requirements for the Degree of Doctor of Philosophy by Paul B Bradley 2008 APPROVAL SHEET This dissertation is submitted in partial fulfillment of the requirements for the degree of Doctor of Philosophy r-/~p~J~ "--\ Paul B Bradle~ Approved, August 2008 eborah A. Bronk, Ph. Committee Chair/Advisor ~vVV Hugh W. Ducklow, Ph.D. ~gc~ Iris . Anderson, Ph.D. Lisa~~but Campbell, P . Department of Oceanography Texas A&M University College Station, Texas 11 DEDICATION Ami querida esposa, Silvia, por tu amor, apoyo, y paciencia durante esta aventura que has compartido conmigo, y A mi hijo, Dominic, por tu sonrisa y tus carcajadas, que pueden alegrar hasta el mas melanc61ico de los dias 111 TABLE OF CONTENTS Page ACKNOWLEDGEMENTS ....................................................................... -
Harmful Algal Bloom Online Resources
Harmful Algal Bloom Online Resources General Information • CDC Harmful Algal Bloom-Associated Illnesses Website • CDC Harmful Algal Blooms Feature • EPA CyanoHABs Website • EPA Harmful Algal Blooms & Cyanobacteria Research Website • NOAA Harmful Algal Bloom Website • NOAA Harmful Algal Bloom and Hypoxia Research Control Act Harmful Algal Bloom Monitoring and Tracking • EPA Cyanobacteria Assessment Network (CyAN) Project • NCCOS Harmful Algal Bloom Research Website • NOAA Harmful Algal Bloom Forecasts • USGS Summary of Cyanobacteria Monitoring and Assessments in USGS Water Science Centers • WHO Toxic Cyanobacteria in water: A guide to their public health consequences, monitoring, and management Harmful Algal Blooms and Drinking Water • AWWA Assessment of Blue-Green Algal Toxins in Raw and Finished Drinking Water • EPA Guidelines and Recommendations • EPA Harmful Algal Bloom & Drinking Water Treatment Website • EPA Algal Toxin Risk Assessment and Management Strategic Plan for Drinking Water Document • USGS Drinking Water Exposure to Chemical and Pathogenic Contaminants: Algal Toxins and Water Quality Website Open Water Resources • CDC Healthy Swimming Website - Oceans, Lakes, Rivers • EPA State Resources Website • EPA Beach Act Website • EPA Beach Advisory and Closing On-line Notification (BEACON) • USG Guidelines for Design and Sampling for Cyanobacterial Toxin and Taste-and-Odor Studies in Lakes and Reservoirs • NALMS Inland HAB Program • NOAA Illinois-Indiana and Michigan Sea Grant Beach Manager’s Manual • USGS Field and Laboratory Guide