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  • lotic  (2)
  • Cyanobacteria  (1)
  • Electronic books.  (1)
  • 1
    Online Resource
    Online Resource
    Newark :John Wiley & Sons, Incorporated,
    Keywords: Toxic algae. ; Electronic books.
    Type of Medium: Online Resource
    Pages: 1 online resource (699 pages)
    Edition: 1st ed.
    ISBN: 9781118994696
    Language: English
    Note: Harmful Algal Blooms: A Compendium Desk Reference -- Contents -- List of Contributors -- Acknowledgments -- Introduction -- Chapter 1: Causes of Harmful Algal Blooms -- 1.1 Introduction -- 1.2 ``Getting There´´: The Classic Perspective on Introduced Species and Links to Cultural Eutrophication -- 1.2.1 Introduced Species -- 1.2.2 Anthropogenically Introduced Nutrients -- 1.3 ``Being There´´: Blooms and Why They Succeed -- 1.3.1 Nutrient-Related HAB -- 1.3.2 Resource Ratios, Nutrient Stoichiometry, and Optimal Nutrient Ratios -- 1.3.3 Diversity in Use of Forms of Nitrogen -- 1.3.4 Toxicity -- 1.3.5 Mixotrophy: Use of ``Packaged´´ and Dissolved Particulate Nutrients -- 1.3.6 Other Adaptations -- 1.4 ``Staying There´´: Links to Physical Structure and Climate -- 1.4.1 Physical Structure: Large-Scale and Small-Scale Natural Hydrological Features -- 1.4.2 Physical Dynamics: Anthropogenic Hydrological Changes -- 1.4.3 Reinforcing Feedbacks -- 1.4.3.1 Trophic Disruptions -- 1.4.3.2 Biogeochemical Alterations -- 1.4.4 Climate Change -- 1.5 Conclusions -- Acknowledgments -- References -- Chapter 2: Detection and Surveillance of Harmful Algal Bloom Species and Toxins -- 2.1 Introduction -- 2.2 Organism Detection -- 2.2.1 Visual/Optical -- 2.2.1.1 Light Microscopy (LM)/Utermöhl's -- 2.2.1.2 Light Microscopy/Flow Cytometry -- 2.2.1.3 In Vivo Fluorometry -- 2.2.1.4 Spectral Absorbance/Spectroradiometry -- 2.2.2 Molecular -- 2.2.2.1 Whole Cell Format -- 2.2.2.1.1 Antibodies -- 2.2.2.1.2 FISH -- 2.2.2.1.3 Flow Cytometry with FISH, CARD FISH, and Solid-Phase Cytometry -- 2.2.2.1.4 CARD FISH on a Slide or in Suspension for Liquid Flow Cytometry -- 2.2.2.1.5 CARD FISH on a Filter or in Suspension for Solid-Phase Cytometry -- 2.2.2.2 Cell-Free Format -- 2.2.2.2.1 Sandwich Hybridization Assay (SHA). , 2.2.2.2.2 Microarrays (Slide-Based, Microelectrode-Based, Luminex, etc.) -- 2.2.2.2.3 Biosensors -- 2.2.2.2.4 qPCR -- 2.3 Toxin Detection -- 2.3.1 In Vivo Assays -- 2.3.1.1 Rat Bioassay -- 2.3.1.2 Mouse Bioassay -- 2.3.1.2.1 AOAC Mouse Bioassay for Paralytic Shellfish Toxins -- 2.3.1.2.2 APHA Mouse Bioassay for Neurotoxin Shellfish Poisons -- 2.3.1.2.3 Mouse Bioassay for Lipophilic Shellfish Toxins -- 2.3.1.2.4 Perspectives -- 2.3.2 In Vitro Assays -- 2.3.2.1 Functional Assays -- 2.3.2.1.1 Receptor Binding Assays -- 2.3.2.1.2 Enzyme Inhibition Assays -- 2.3.2.1.3 Cell-Based (Cytotoxicity) Assays (CBAs) -- 2.3.2.2 Structural Assays -- 2.3.2.2.1 Immunoassays -- 2.3.2.2.2 Molecularly Imprinted Polymers (MIPs) -- 2.3.2.2.3 Aptamers -- 2.3.2.3 Biosensors -- 2.3.3 Analytical Techniques -- 2.3.3.1 High-Performance Liquid Chromatography with Optical Detection (UV or FLD) -- 2.3.3.1.1 Domoic Acid -- 2.3.3.1.2 Paralytic Shellfish Toxins -- 2.3.3.1.3 Other Toxin Classes -- 2.3.3.2 Liquid Chromatography-Mass Spectrometry (LC-MS) and Liquid Chromatography-Tandem Mass Spectrometry (LC-MS/MS) -- 2.3.3.2.1 Lipophilic Toxins -- 2.3.3.2.2 Paralytic Shellfish Toxins -- 2.3.3.2.3 Other Toxin Classes -- 2.3.3.3 Other Analytical Methods: Capillary Electrophoresis (CE), Matrix-Assisted Laser Desorption Ionization-Time of Flight (MALDI-TOF), and Laser Ablation Electrospray Ionization (LAESI) -- 2.3.3.4 Perspectives -- 2.4 Autonomous, In Situ Technologies -- 2.4.1 Environmental Sample Processor (McLane Research Laboratories) -- 2.4.2 Imaging Flow Cytobot (McLane Research Laboratories) -- 2.4.3 Optical Phytoplankton Discriminator (aka BreveBuster -- Mote Marine Laboratory) -- 2.4.4 CytoBuoy (CytoBuoy b.v.) -- 2.4.5 SPATT Passive Samplers -- 2.5 Conclusions and Future Prospects -- Disclaimer -- References and Further Reading. , Chapter 3: Modeling Marine Harmful Algal Blooms: Current Status and Future Prospects -- 3.1 Introduction -- 3.2 Building Models to Describe Ecological Events -- 3.3 Limitations to What Models Can Do, and Why -- 3.3.1 Building Models -- 3.3.2 Model Complexity -- 3.3.3 The Need for Data -- 3.3.4 Validating Models -- 3.4 Modeling T-HAB and ED-HAB Events -- 3.5 How Good Are Current HAB Models? -- 3.6 Future Modeling of T-HAB and ED-HAB: Managing Expectations -- 3.7 Improving Our Capabilities -- 3.7.1 Changes in the Biological-Modeling Interface -- Acknowledgments -- References -- Chapter 4: Harmful Algal Blooms and Shellfish -- 4.1 Introduction -- 4.2 Major Shellfish Poisonings -- 4.2.1 Paralytic Shellfish Poisoning (PSP) -- 4.2.2 Diarrheic Shellfish Poisoning (DSP) -- 4.2.3 Neurotoxic Shellfish Poisoning (NSP) -- 4.2.4 Amnesic Shellfish Poisoning (ASP) -- 4.2.5 Azaspiracid Shellfish Poisoning (AZP) -- 4.3 Other Toxins: Pectenotoxins (PTX) and Yessotoxins (YTX) -- 4.4 Emerging Shellfish Poisonings -- 4.5 Toxin Uptake, Accumulation, and Depuration -- 4.6 Shellfish Contamination in North America -- 4.6.1 Bivalves -- 4.6.1.1 Paralytic Shellfish Contamination -- 4.6.1.2 Diarrheic Shellfish Contamination -- 4.6.1.3 Neurotoxic Shellfish Contamination -- 4.6.1.4 Amnesic Shellfish Contamination -- 4.6.2 Gastropods -- 4.6.3 Crustaceans -- 4.7 Impacts on Shellfish -- 4.8 Conclusions and Perspectives -- References and Further Reading -- Chapter 5: Vulnerabilities of Marine Mammals to Harmful Algal Blooms -- 5.1 Introduction -- 5.2 Overview of Algal Toxins -- 5.2.1 Brevetoxins -- 5.2.2 Ciguatoxins -- 5.2.3 Diarrhetic Shellfish Poisoning Toxins -- 5.2.4 Domoic Acid -- 5.2.5 Paralytic Shellfish Toxins -- 5.2.6 Other Algal and Cyanobacterial Toxins -- 5.3 Impacts of Algal Toxins Specific to Marine Mammals. , 5.3.1 The Effects of Toxin Exposure Depend on Animal Physiology and Behavior -- 5.3.2 Emerging Issues: Non-acute and Multiple Toxin Exposure -- 5.3.3 Prospects for Managing Impacts of HAB -- 5.4 Considerations for the Evaluation of HAB Toxins in Marine Mammals -- 5.4.1 Sampling Marine Mammals for HAB Toxin Analysis -- 5.4.2 Priority Needs for Investigating HAB Toxin Involvement in Marine Mammal Morbidity and Mortality -- Abbreviations -- References and Further Reading -- Chapter 6: Interactions between Seabirds and Harmful Algal Blooms -- 6.1 Introduction -- 6.2 Historical Interactions between HAB and Seabirds -- 6.2.1 Paralytic Shellfish Poisoning (PSP) -- 6.2.2 Neurotoxic Shellfish Poisoning (NSP) -- 6.2.3 Amnesic Shellfish Poisoning -- 6.2.4 Akashiwo sanguinea -- 6.2.5 Diarrheic Shellfish Poisoning (DSP) -- 6.2.6 CyanoHAB -- 6.3 Improved Monitoring and Establishment of Causality -- 6.3.1 Coordinating Monitoring and Pathology to Confirm Relationships between HAB and Seabird Mortality -- 6.3.2 Seabirds as Biological Indicators -- 6.4 Implications for Conservation -- References -- Chapter 7: Food Web and Ecosystem Impacts of Harmful Algae -- 7.1 Introduction -- 7.2 Approaches, Pitfalls, Progress, and Goals -- 7.3 High-Biomass Algal Blooms -- 7.4 Emerging Recognition of the Roles of Allelochemicals -- 7.4.1 Microalgae -- 7.4.2 Thalloid Macroalgae -- 7.4.3 Filamentous Mat-Forming Macroalgae -- 7.5 Toxigenic Algae in Aquatic Food Webs -- 7.5.1 Toxic Microcystis aeruginosa Blooms across North America -- 7.5.2 Toxic Prymnesium parvum Blooms and Fish Communities in Two Texas Rivers -- 7.5.3 Toxic Pseudo-nitzschia Blooms in Coastal Upwelling Areas -- 7.5.4 Toxic Alexandrium Blooms in the Northeast -- 7.5.5 Toxic Karenia brevis Blooms along the Florida Coast -- 7.6 Ecosystem-Disruptive Algal Blooms -- 7.7 Future Directions. , Appendix A: Scientific Names for Organisms Listed by Common Name in This Chapter, Also Indicating Species Affected by Karenia brevis (Kb) -- References and Further Reading -- Chapter 8: Assessing the Economic Consequences of Harmful Algal Blooms: A Summary of Existing Literature, Research Methods, Data, and Information Gaps -- 8.1 Introduction -- 8.2 Overview -- 8.3 Research Methodologies -- 8.4 Sources and Types of Data -- 8.5 Spatial and Temporal Scopes -- 8.6 Nature of the Hazard -- 8.7 Current Research Gaps -- 8.8 Conclusion -- Acknowledgments -- References and Further Reading -- Chapter 9: Public Health and Epidemiology -- 9.1 Introduction -- 9.2 What Is Public Health and Epidemiology? -- 9.3 HAB and Human Illness -- 9.3.1 Paralytic Shellfish Poisoning (PSP) -- 9.3.1.1 Exposure -- 9.3.1.2 Clinical Symptoms -- 9.3.1.3 Treatment -- 9.3.2 Amnesic Shellfish Poisoning (ASP) -- 9.3.2.1 Exposure -- 9.3.2.2 Clinical Syndrome -- 9.3.2.3 Treatment -- 9.3.3 Neurotoxic Shellfish Poisoning (NSP) -- 9.3.3.1 Exposure -- 9.3.3.2 Clinical Illness -- 9.3.3.3 Treatment -- 9.3.4 Brevetoxin Inhalation Syndrome (BIS) -- 9.3.4.1 Exposure -- 9.3.4.2 Clinical Illness -- 9.3.4.3 Treatment -- 9.3.5 Diarrhetic Shellfish Poisoning (DSP) -- 9.3.5.1 Exposure -- 9.3.5.2 Clinical Syndrome -- 9.3.5.3 Treatment -- 9.3.6 Ciguatera Fish Poisoning (CFP) -- 9.3.6.1 Exposure -- 9.3.6.2 Clinical Illness -- 9.3.6.3 Treatment -- 9.3.7 Azaspiracid Shellfish Poisoning (AZP) -- 9.3.7.1 Exposure -- 9.3.7.2 Clinical Syndrome -- 9.3.7.3 Treatment -- 9.3.8 Toxic Cyanobacteria -- 9.3.8.1 Exposure -- 9.3.8.2 Clinical Syndromes -- 9.3.8.3 Treatment -- 9.4 The HAB Manager's Role in Preventing HAB-Related Illnesses -- 9.4.1 HAB Management Exemplars -- 9.4.2 The Native American Perspective from Washington State, USA: Domoic Acid and Paralytic Shellfish Toxins -- 9.4.2.1 Background. , 9.4.2.2 Tribal Capacity and Inclusion.
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  • 2
    ISSN: 1573-5117
    Keywords: Rhode Island ; streams ; lotic ; riparian shading
    Source: Springer Online Journal Archives 1860-2000
    Topics: Biology
    Notes: Abstract Thirteen physical and chemical characteristics of five softwater streams in Rhode Island, U.S.A. were examined biweekly to monthly for seventeen months. One first-order, two second-order and two third-order streams were included in the study. The mean annual temperature ranged from 9.4 °C in the spring-fed headwater stream to 14 °C in an open, third-order stream, with seasonal fluctuations of 14.5 ° to 28.0 °C. The heavily shaded first-order stream generally received less than 30% incident light at its surface throughout the year. By contrast, the other streams either were unshaded or were associated with distinct periodicity of incident light quantity due to seasonality of the tree canopy. The mean annual current velocity ranged from 22 to 100 cm s−1 among the streams, pH ranged from 3.7 to 6.4, and specific conductance was generally less than 50 µS cm−1. The first-order stream was associated with lowest mean annual temperature, current velocity, light penetration and nitrate, as well as relatively high and constant silica concentrations. Temperature was negatively correlated with current speed in second- and third-order streams, and temperature was also negatively correlated with light in shaded streams. There was a general pattern in all streams for decreasing pH following precipitation events. Concentrations of total phophorus, nitrate-nitrogen, ammonium-nitrogen and silica were among the lowest reported for lotic systems.
    Type of Medium: Electronic Resource
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  • 3
    ISSN: 1573-5117
    Keywords: Rhode Island ; streams ; lotic ; macroalgae
    Source: Springer Online Journal Archives 1860-2000
    Topics: Biology
    Notes: Abstract Forty stream segments in Rhode Island, U.S.A., were examined seasonally from June 1979 to March 1982. Thirty-nine species of macroalgae were collected, respresenting 25 genera. The composition of the lotic flora was 54% green algae, 31% red algae, 5% blue-green algae, 5% xanthophytes, 3% chrysophytes and 3% diatoms. The majority of these taxa (85%) were filamentous. From a biweekly examination of five stream segments, macroalgal communities could be grouped according to light regime. Species in unshaded streams exhibited little seasonality, whereas in streams shaded by one or more layers of riparian canopy, maxima in species numbers and abundance occurred during colder seasons. The most widespread and abundant species were the blue-green alga Phormidium retzii, the green alga Draparnaldia acuta, and the diatom Eunotia pectinalis. P. retzii and E. pectinalis were aseasonal annuals, while D. acuta was primarily a winter-spring form. It appears that pH is a major factor affecting broad geographic distribution patterns of stream macroalgae, whereas the light regime established by overhanging canopy is an important factor which influences localized abundance and seasonality of lotic macroalgal communities. Niche pre-emption appears to be a common mode of resource space division among stream macroalgae in Rhode Island. E. pectinalis is the strongly developed dominant in this drainage system.
    Type of Medium: Electronic Resource
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  • 4
    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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