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  • 1
    Book
    Book
    Amsterdam [u.a.] : Elsevier
    Type of Medium: Book
    Pages: 135 S , Ill., graph. Darst
    Series Statement: Progress in oceanography 85.2010,1/2
    Language: English
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  • 2
    Keywords: Life sciences ; Life Sciences ; Geobiology ; Aquatic ecology ; Marine sciences ; Freshwater ; Life sciences ; Geobiology ; Aquatic ecology ; Marine sciences ; Freshwater
    Description / Table of Contents: Preface to Global Ecology and Oceanography of Harmful Algal BlooHarmful algal Blooms and the Importance of Understanding their Ecology and Oceanography -- Establishment, Goals, and Legacy of the Global Ecology and Oceanography of Harmful Algal Blooms (GEOHAB) Program -- Changing Land, Sea- and Airscapes: Sources of Nutrient Pollution Affecting Habitat Suitability for Harmful Algae -- Harmful Algal Blooms in a Changing Ocean -- Nutrients and HABs: Dynamic Kinetics and Flexible Nutrition -- Mixotrophy in HABs: by Whom, on Whom, When, Why, and What Next -- The Role of Life Cycle Characteristics in Harmful Algal Bloom Dynamics -- Key Questions and Recent Research Advances on Harmful Algal Blooms in Stratified Systems -- Key Questions and Recent Research Advances on Harmful Algal Blooms in Fjords and Coastal Embayments -- Key Questions and Recent Research Advances on Harmful Algal Blooms in Eastern Boundary Upwelling Systems -- Key Questions and Recent Research Advances on Harmful Algal Blooms in Relation to Nutrients and Eutrophication -- Key Questions and Recent Research Advances on Harmful Algal Blooms in Benthic Systems -- Overview of Harmful Algal Blooms in Asia -- Harmful Algal Blooms in the Coastal Waters of China -- Green Tides of the Yellow Sea: Massive Free-floating Blooms of Ulva prolifera -- Ecological Drivers of Green Noctiluca Blooms in Two Monsoonally Driven Ecosystems -- Advancements and Continuing Challenges of Emerging Technologies and Tools for Detecting Harmful Algal Blooms, Their Antecedent Conditions and Toxins, and Applications in Predictive Models -- Recent Advances in Modelling of Harmful Algal Blooms -- Emerging HAB Research Issues in Freshwater Environments -- Mitigation and Control of HABs -- GlobalHAB: Fostering International Coordination on Harmful Algal Bloom Research in Aquatic Systems.
    Type of Medium: Online Resource
    Pages: Online-Ressource (XVI, 461 p. 71 illus., 60 illus. in color, online resource)
    ISBN: 9783319700694
    Series Statement: Ecological Studies, Analysis and Synthesis 232
    RVK:
    Language: English
    Note: Includes bibliographical references and index
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  • 3
    Online Resource
    Online Resource
    Cham :Springer International Publishing AG,
    Keywords: Algal blooms. ; Electronic books.
    Type of Medium: Online Resource
    Pages: 1 online resource (460 pages)
    Edition: 1st ed.
    ISBN: 9783319700694
    Series Statement: Ecological Studies ; v.232
    DDC: 363.738
    Language: English
    Note: Intro -- In Memoriam: Otto Ludwig Lange (1927-2017) -- Contents -- List of Abbreviations -- Part I: Introduction to Harmful Algal Blooms and the GEOHAB Programme -- Chapter 1: Introduction to the Global Ecology and Oceanography of Harmful Algal Blooms (GEOHAB) Synthesis -- References -- Chapter 2: Harmful Algal Blooms and the Importance of Understanding Their Ecology and Oceanography -- 2.1 Introduction -- 2.2 What Are Harmful Algal Blooms? -- 2.3 How Are HABs Harmful? -- 2.4 Where Do HABs Occur? -- 2.5 Why Are HABs Expanding? -- 2.6 Why the Need for Advancing Knowledge of HAB Ecology and Oceanography? -- 2.7 Conclusions and the Role of GEOHAB -- References -- Chapter 3: Establishment, Goals, and Legacy of the Global Ecology and Oceanography of Harmful Algal Blooms (GEOHAB) Programme -- 3.1 Introduction -- 3.2 History of GEOHAB -- 3.3 HABs in Upwelling Systems -- 3.4 HABs in Eutrophic Systems -- 3.5 HABs in Stratified Systems -- 3.6 HABs in Fjords and Coastal Embayments -- 3.7 HABs in Benthic Systems -- 3.8 GEOHAB Targeted, Regional, and National Research -- 3.9 Cross-Cutting and Framework Activities -- 3.10 GEOHAB Legacies -- References -- Part II: Global Changes and Harmful Algal Blooms -- Chapter 4: Changing Land-, Sea-, and Airscapes: Sources of Nutrient Pollution Affecting Habitat Suitability for Harmful Algae -- 4.1 Introduction -- 4.2 Land-Based Nutrient Pollution -- 4.3 Changing Seascapes -- 4.4 Coastal Typology and Anthropogenic Changes in Water Flow: Nutrient Retention Effects -- 4.5 Changing Airscapes -- 4.6 Eutrophication Potential and Global HAB Distribution -- 4.7 Future Projections: Millennium Ecosystem Assessment Scenarios -- 4.8 Future Projections: Global Ecosystem Modelling Approaches -- 4.9 Conclusions -- References -- Chapter 5: Harmful Algal Blooms in a Changing Ocean -- 5.1 Introduction. , 5.2 Direct Effects of Temperature on HABs -- 5.3 Direct Effects of Stratification on HABs -- 5.4 Altered Light Field Effects on HABs -- 5.5 Effects of Ocean Acidification on HABs -- 5.6 Effects of Nutrients on HABs -- 5.7 Grazer Effects on HABs -- 5.8 General Strategies to Accelerate Understanding of Climate Change Impacts on HABs -- References -- Part III: Adaptive Strategies and Harmful Algal Blooms -- Chapter 6: Nutrients and Harmful Algal Blooms: Dynamic Kinetics and Flexible Nutrition -- 6.1 Introduction -- 6.2 Limiting Nutrients -- 6.3 Optimal Nutrients -- 6.4 Dynamic Responses -- 6.5 Stoichiometry and Balancing Excess Nutrients -- 6.6 Mixotrophy -- 6.7 Conclusions -- References -- Chapter 7: Mixotrophy in Harmful Algal Blooms: By Whom, on Whom, When, Why, and What Next -- 7.1 Introduction -- 7.2 Mixotrophy Across the Spectrum of Nutrient Supply -- 7.3 Mixotrophs and Cellular Nutrient Stoichiometry -- 7.4 Mixotrophs and the Food Web -- 7.5 Inclusion of Mixotrophy in State-of-the-Art Ecosystem Modelling: The Rationale -- 7.6 Including Mixotrophy in State-of-the-Art Ecosystem Modelling: An Approach -- 7.7 Conclusions -- References -- Chapter 8: The Role of Life Cycle Characteristics in Harmful Algal Bloom Dynamics -- 8.1 Introduction -- 8.2 Dinoflagellates: Alexandrium fundyense and Pyrodinium bahamense -- 8.2.1 Life Cycle of Cyst-Forming Dinoflagellates -- 8.2.2 Bloom Dynamics -- 8.2.2.1 Major Study Areas -- 8.2.2.2 Cyst Distributions and Initiation of Planktonic Blooms -- 8.2.2.3 Bloom Development and Transport -- 8.2.2.4 Sexual Induction and Cyst Formation -- 8.3 Diatoms: Pseudo-nitzschia spp. -- 8.3.1 Life Cycle -- 8.3.2 Bloom Dynamics -- 8.3.3 Modelling of Life Cycle Transitions -- 8.4 Cyanobacteria: Nodularia spumigena -- 8.4.1 Life Cycle -- 8.4.2 Bloom Dynamics -- 8.4.3 Dispersal and Future Distribution -- 8.5 Synthesis and Recommendations. , References -- Part IV: Harmful Algal Blooms in Specific Habitats and Biomes -- Chapter 9: Key Questions and Recent Research Advances on Harmful Algal Blooms in Stratified Systems -- 9.1 Introduction -- 9.2 Key Questions 1: What Are the Turbulence Length Scales Relevant to Harmful Phytoplankton and the Formation of Thin Layers?... -- 9.3 Key Questions 2: What Are the Main Processes Controlling the Population Evolution of a Given Species, and How Does Their R... -- 9.3.1 Bloom Initiation -- 9.3.2 Bloom Maintenance -- 9.3.3 Bloom Decline and TL Erosion -- 9.4 Key Questions 3: How Can We Quantify Modifications in Turbulence by Phytoplankton Through Changes in the Viscosity of Its ... -- 9.5 Key Questions 4: What Nutritional Opportunities Do Thin Layers Provide to Phytoplankton, Especially to the Species Selecte... -- 9.6 Key Question 5: Are Allelopathy and ``Chemical Warfare´´ at Work In Situ Within TLs? -- 9.7 Conclusions and Next Steps -- References -- Chapter 10: Key Questions and Recent Research Advances on Harmful Algal Blooms in Fjords and Coastal Embayments -- 10.1 Introduction -- 10.2 Key Question 1: Are There Definable Adaptive Strategies for HAB Species in Confined and Semi-confined Systems? -- 10.3 Key Question 2: What Is the Importance of Life History Transitions and Cyst Distribution in Bloom Initiation and Maintena... -- 10.4 Key Question 3: How Do Physical Dispersion and Aggregation Processes Within a Semi-confined Basin Affect HAB Growth and D... -- 10.5 Key Question 4: What Is the Relative Contribution of Nutrient Flux and Supply Ratios to HAB Dynamics in Eutrophic Versus ... -- 10.6 Key Question 5: What Is the Importance of Spatial Scale and Retention Time in the Expression and Effects of Allelochemica... -- 10.7 Key Question 6: How Do Embayment Morphology, Bathymetry and Hydrodynamics Affect HAB Dynamics?. , 10.8 Key Question 7: Are the Effects of Human Activities (e.g. Aquaculture) and Global Climate Change on HAB Dynamics Magnifie... -- 10.9 Future Research Priorities -- References -- Chapter 11: Key Questions and Recent Research Advances on Harmful Algal Blooms in Eastern Boundary Upwelling Systems -- 11.1 Introduction -- 11.2 Key Question 1: Are There Definable Adaptive Strategies that Characterize HAB Species in Upwelling Systems? -- 11.3 Key Question 2: What Seeding Strategies Persist Within Upwelling Regions and Are They Consistent Among Regions? -- 11.4 Key Question 3: How Do Small-Scale Physical Processes Affect HAB Growth and Dispersion in Upwelling Systems? -- 11.5 Key Question 4: How Do Nutrient Supply Type and Ratios Determine HAB Population Dynamics in Upwelling Systems? -- 11.6 Key Question 5: What Is the Role of Genetic Predisposition Versus Environmental Conditions in Toxin Production in Differe... -- 11.7 Key Question 6: How Does Coastal Morphology and Bathymetry Affect HAB Dynamics in Upwelling Systems? -- 11.8 Key Question 7: What Is the Relative Importance of Cross-Shelf and Along-Shore Advection for HABs in Different Upwelling ... -- 11.9 Key Question 8: Are Climate Indicators Predictive of HAB Events in Upwelling Systems? -- 11.10 HAB Prediction -- 11.11 Conclusions -- References -- Chapter 12: Key Questions and Recent Research Advances on Harmful Algal Blooms in Relation to Nutrients and Eutrophication -- 12.1 Introduction -- 12.2 Key Question 1: Are There Clusters or Specific Types of HAB Species that Are Indicative of Global HAB Increases? -- 12.3 Key Question 2: To What Extent Do Residence Time and Other Physical Processes Impact the Relationship Between Nutrient Lo... -- 12.4 Key Question 3: How Do Feedbacks and Interactions Between Nutrients and the Planktonic, Microbial Food Web Impact HABs an. , 12.5 Key Question 4.0: Do Anthropogenic Alterations of the Food Web, Including Overfishing and Aquaculture Activities, Synergi... -- 12.6 Key Question 5: How Do Anthropogenic Changes in Land Use, Agricultural Use of Fertilizer, NOx Emissions from Vehicles, an... -- 12.7 Key Question 6: How Do the Stoichiometry and Quality of These Nutrient Sources Regulate the Biological Response, Includin... -- 12.8 Key Question 7: Do Climate Change and Climate Variability Have Impacts on Ecosystems that Augment the Impacts of Eutrophi... -- 12.9 Conclusions -- References -- Chapter 13: Key Questions and Recent Research Advances on Harmful Algal Blooms in Benthic Systems -- 13.1 Introduction -- 13.2 Key Question 1: What Is the Biogeography and Biodiversity of BHABs and the Relationships Among Distributions of BHAB Spec... -- 13.2.1 Gambierdiscus -- 13.2.2 Ostreopsis -- 13.3 Key Question 2: What Are the Relationships Between Eutrophication and Nutrient Transformation Pathways and BHAB Populatio... -- 13.3.1 Gambierdiscus -- 13.3.2 Ostreopsis -- 13.4 Key Question 3: Are There Particular Characteristics and Adaptations of BHAB Species That Determine When and Where They O... -- 13.4.1 Gambierdiscus -- 13.4.2 Ostreopsis -- 13.5 Key Question 4: Are There Mechanisms Underlying BHAB Population and Community Dynamics Across Ecosystem Types That Are Re... -- 13.6 Key Question 5: What New Observation and Modelling Approaches Are Available to Help in the Detection and Prediction of BH... -- 13.7 BHAB Toxins -- 13.7.1 Gambierdiscus -- 13.7.2 Ostreopsis -- 13.8 Impacts on Human Health -- 13.8.1 Health Disorders Associated with Gambierdiscus Outbreaks -- 13.8.2 Health Disorders Associated with Ostreopsis Outbreaks -- 13.9 Summary and Recommendations -- References -- Part V: Spotlight on Harmful Algal Blooms in Asia -- Chapter 14: Overview of Harmful Algal Blooms in Asia. , 14.1 Introduction.
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  • 4
    Publication Date: 2021-02-08
    Description: As plastic waste pollutes the oceans and fish stocks decline, unseen below the surface another problem grows: deoxygenation. Breitburg et al. review the evidence for the downward trajectory of oxygen levels in increasing areas of the open ocean and coastal waters. Rising nutrient loads coupled with climate change—each resulting from human activities—are changing ocean biogeochemistry and increasing oxygen consumption. This results in destabilization of sediments and fundamental shifts in the availability of key nutrients. In the short term, some compensatory effects may result in improvements in local fisheries, such as in cases where stocks are squeezed between the surface and elevated oxygen minimum zones. In the longer term, these conditions are unsustainable and may result in ecosystem collapses, which ultimately will cause societal and economic harm.
    Type: Article , PeerReviewed
    Format: text
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  • 5
    Publication Date: 2024-02-07
    Description: Highlights: • The epoch of the Anthropocene, a period during which human activity has been the dominant influence on climate and the environment, has witnessed a decline in oxygen concentrations and an expansion of oxygen-depleted environments in both coastal and open ocean systems since the middle of the 20th century. • This review paper provides a synthesis of system-specific drivers of low oxygen in a range of case studies representing marine systems in the open ocean, on continental shelves, in enclosed seas and in the coastal environment. • Identification of similar and contrasting responses within and across system types and corresponding oxygen regimes is shown to be informative both in understanding and isolating key controlling processes and provides a sound basis for predicting change under anticipated future conditions. • Case studies were selected to achieve a balance in system diversity and global coverage. • Each case study describes system attributes, including the present-day oxygen environment and known trends in oxygen concentrations over time. • Central to each case study is the identification of the physical and biogeochemical processes that determine oxygen concentrations through the tradeoff between ventilation and respiration. • Spatial distributions of oxygen and time series of oxygen data provide the opportunity to identify trends in oxygen availability and have allowed various drivers of low oxygen to be distinguished through correlative and causative relationships. • Deoxygenation results from a complex interplay of hydrographic and biogeochemical processes and the superposition of these processes, some additive and others subtractive, makes attribution to any particular driver challenging. • System-specific models are therefore required to achieve a quantitative understanding of these processes and of the feedbacks between processes at varying scales. Abstract: The epoch of the Anthropocene, a period during which human activity has been the dominant influence on climate and the environment, has witnessed a decline in oxygen concentrations and an expansion of oxygen-depleted environments in both coastal and open ocean systems since the middle of the 20th century. This paper provides a review of system-specific drivers of low oxygen in a range of case studies representing marine systems in the open ocean, on continental shelves, in enclosed seas and in the coastal environment. Identification of similar and contrasting responses within and across system types and corresponding oxygen regimes is shown to be informative both in understanding and isolating key controlling processes and provides a sound basis for predicting change under anticipated future conditions. Case studies were selected to achieve a balance in system diversity and global coverage. Each case study describes system attributes, including the present-day oxygen environment and known trends in oxygen concentrations over time. Central to each case study is the identification of the physical and biogeochemical processes that determine oxygen concentrations through the tradeoff between ventilation and respiration. Spatial distributions of oxygen and time series of oxygen data provide the opportunity to identify trends in oxygen availability and have allowed various drivers of low oxygen to be distinguished through correlative and causative relationships. Deoxygenation results from a complex interplay of hydrographic and biogeochemical processes and the superposition of these processes, some additive and others subtractive, makes attribution to any particular driver challenging. System-specific models are therefore required to achieve a quantitative understanding of these processes and of the feedbacks between processes at varying scales.
    Type: Article , PeerReviewed , info:eu-repo/semantics/article
    Format: text
    Format: text
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  • 6
    Publication Date: 2019-07-17
    Description: A unialgal culture of a Pseudo-nitzschia species dominant in the plankton of Algoa Bay in the spring of 2012 was established by isolation of clonal chains of cells. Identification of the species as Pseudo-nitzschia multiseries was based on frustule morphometrics provided by light and scanning electron microscopy, and confirmed by phylogenetic analysis of the LSU rDNA gene. Cultures were shown to produce domoic acid (DA) as measured by ELISA and LC/MS-MS methods, and levels of cellular DA were ∼0.1 pg cell–1. Although it is recognised as a cosmopolitan species, these observations provide the first account of this toxic diatom in the coastal waters of South Africa.
    Repository Name: EPIC Alfred Wegener Institut
    Type: Article , isiRev
    Format: application/pdf
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  • 7
    Publication Date: 2022-05-25
    Description: Author Posting. © Oceanography Society, 2010. This article is posted here by permission of Oceanography Society for personal use, not for redistribution. The definitive version was published in Oceanography 23, no. 3 (2010): 72-85.
    Description: Harmful algal blooms (HABs) have become an important subdiscipline within oceanography. Heightened attention to this topic as well as significant research advances reflect the global nature of the problem and the development of strong national and international programs for HAB research and management. The planning, communication, coordination, and capacity-building activities of the Intergovernmental Oceanographic Commission (IOC) have been a key factor in this growth. Here, we highlight selected advances in science and management capacity for HABs and document the impressive growth of the field in the context of activities supported directly or indirectly by IOC. As we look to the future, the field has significant momentum and stability. Nevertheless, it will require scientific guidance and coordination going forward. With an appropriate commitment of resources from member states, the IOC HAB program can continue to be a major factor in the sustained growth of this important scientific discipline and its delivery of improved observation and management systems.
    Description: Supported in part by the following grants to D.M. Anderson: NOAA Cooperative Agreement NA17RJ1223, NOAA Grant NA09NOS4260212, NIEHS Grant 1 P50 ES01274201, and NSF Grants OCE-0430724 and OCE-0911031.
    Repository Name: Woods Hole Open Access Server
    Type: Article
    Format: application/pdf
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  • 8
    Publication Date: 2021-05-19
    Description: We provide a review of Harmful Algal Blooms (HABs) within the Canary Current Large Marine Ecosystem (CCLME). As yet all documented HABs within the region have been associated with the production of one or another toxin. The diversity of harmful algae recorded within the region is similar to that found in other eastern boundary upwelling systems, and includes those species responsible for paralytic shellfish poisoning, diarrhetic shellfish poisoning, amnesic shellfish poisoning and azaspiracid poisoning. Also present off Northwest Africa, but generally absent from the other major upwelling systems, are those species responsible for ciguatera fish poisoning and microcystin-producing cyanobacterial blooms. Their presence is afforded by the subtropical habitat provided by the island archipelagos found within the CCLME. It is intended that this brief review will provide the foundation and stimulus for further studies of the ecology and dynamics of HABs, of their toxins, and of the public health and socioeconomic impacts of HABs within this region.
    Description: Published
    Keywords: Amnesic shellfish poisoning ; Azaspiracid poisoning ; Ciguatera fish poisoning ; CCLME ; ASFA15::P::Paralytic shellfish poisoning ; ASFA15::D::Diarrhetic shellfish poisoning
    Repository Name: AquaDocs
    Type: Report Section , Refereed
    Format: pp. 175-182
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  • 9
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    ELSEVIER SCIENCE BV
    In:  EPIC3Harmful Algae, ELSEVIER SCIENCE BV, 20, pp. 30-41, ISSN: 1568-9883
    Publication Date: 2019-07-17
    Description: The variability of toxigenic phytoplankton and the consequent uptake and loss of toxins by the mussel Choromytilus meridionalis was investigated in the southern Benguela at the event scale (3-10 days) in response to the upwelling-downwelling cycle. Phytoplankton and mussel samples were collected daily (20 March-11 April 2007) from a mooring station (32.04 degrees S; 18.26 degrees E) located 3.5 km offshore of Lambert's Bay, within the St Helena Bay region. Rapid changes in phytoplankton assemblages incorporated three groups of toxigenic phytoplankton: (1) the dinoflagellate Alexandrium catenella; (2) several species of Dinophysis, including Dinophysis acuminata, Dinophysis fortii, Dinophysis hastata and Dinophysis rotundata; and (3) members of the diatom genus Pseudo-nitzschia. Analysis of phytoplankton concentrates by LC-MS/MS or LC-FD provided information on the toxin composition and calculated toxicity of each group. Several additional in vitro assays were used for the analysis of toxins in mussels (ELISA, RBA, MBA for PSP toxins; and ELISA for DSP toxins). Good correspondence was observed between methods except for the MBA, which provided significantly lower (approximately 2-fold) estimates of PSP toxins. PSP and DSP toxins both exceeded the regulatory limits in Choromytilis meridionalis, but ASP toxins were undetected. Differences were observed in the composition of both PSP and DSP toxins in C meridionalis from that of the ingested dinoflagellates (PSP toxins showed an increase in SIX, C1,2, and traces of dcSTX and GTX1,4 and a decrease in NEO; DSP toxins showed an increased in DTX1, and traces of PTX2sa, and a decrease in OA). The rate of loss of PSP toxins following dispersal of the A. catenella boom was 0.12 d(-1). Variation in the loss rates of different PSP toxins contributed to the change in toxin profile in C. meridionalis. Prediction of net toxicity in shellfish of the nearshore environment in the southern Benguela is limited due to rapid phytoplankton community changes, high variability in cellular toxicity, and the selective uptake and loss of toxins, and/or transformation of toxins.
    Repository Name: EPIC Alfred Wegener Institut
    Type: Article , isiRev
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  • 10
    Publication Date: 2022-05-26
    Description: Author Posting. © Elsevier B.V., 2008. This is the author's version of the work. It is posted here by permission of Elsevier B.V. for personal use, not for redistribution. The definitive version was published in Marine Pollution Bulletin 56 (2008): 1049-1056, doi:10.1016/j.marpolbul.2008.03.010.
    Description: The proposed plan for enrichment of the Sulu Sea, Philippines, a region of rich marine biodiversity, with thousands of tonnes of urea in order to stimulate algal blooms and sequester carbon is flawed for multiple reasons. Urea is preferentially used as a nitrogen source by some cyanobacteria and dinoflagellates, many of which are neutrally or positively buoyant. Biological pumps to the deep sea are classically leaky, and the inefficient burial of new biomass makes the estimation of a net loss of carbon from the atmosphere questionable at best. The potential for growth of toxic dinoflagellates is also high, as many grow well on urea and some even increase their toxicity when grown on urea. Many toxic dinoflagellates form cysts which can settle to the sediment and germinate in subsequent years, forming new blooms even without further fertilization. If large-scale blooms do occur, it is likely that they will contribute to hypoxia in the bottom waters upon decomposition. Lastly, urea production requires fossil fuel usage, further limiting the potential for net carbon sequestration. The environmental and economic impacts are potentially great and need to be rigorously assessed.
    Description: This paper was developed under the Global Ecology and Oceanography of Harmful Algal Blooms (GEOHAB) core research project on HABs and Eutrophication and the GEOHAB regional focus on HABs in Asia. GEOHAB is supported by the International Oceanographic Commission (IOC) of UNESCO and by the Scientific Committee on Oceanic Research (SCOR), which are, in turn, supported by multiple agencies, including NSF and NOAA of the USA.
    Keywords: Urea dumping ; Ocean fertilization ; Carbon credits ; Sulu Sea ; Carbon sequestration ; Harmful algae ; Toxic dinoflagellates ; Cyanobacteria ; Hypoxia
    Repository Name: Woods Hole Open Access Server
    Type: Preprint
    Format: application/pdf
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