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      Coagulant plus ballast technique provides a rapid mitigation of cyanobacterial nuisance

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          Abstract

          Cyanobacteria blooms are a risk to environmental health and public safety due to the potent toxins certain cyanobacteria can produce. These nuisance organisms can be removed from water bodies by biomass flocculation and sedimentation. Here, we studied the efficacy of combinations of a low dose coagulant (poly-aluminium chloride—PAC—or chitosan) with different ballast compounds (red soil, bauxite, gravel, aluminium modified zeolite and lanthanum modified bentonite) to remove cyanobacterial biomass from water collected in Funil Reservoir (Brazil). We tested the effect of different cyanobacterial biomass concentrations on removal efficiency. We also examined if zeta potential was altered by treatments. Addition of low doses of PAC and chitosan (1–8 mg Al L -1) to the cyanobacterial suspensions caused flock formation, but did not settle the cyanobacteria. When those low dose coagulants were combined with ballast, effective settling in a dose-dependent way up to 99.7% removal of the flocks could be achieved without any effect on the zeta potential and thus without potential membrane damage. Removal efficacy was influenced by the cyanobacterial biomass and at higher biomass more ballast was needed to achieve good removal. The combined coagulant-ballast technique provides a promising alternative to algaecides in lakes, ponds and reservoirs.

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          Most cited references55

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          Eutrophication and harmful algal blooms: A scientific consensus

          In January 2003, the US Environmental Protection Agency sponsored a “roundtable discussion” to develop a consensus on the relationship between eutrophication and harmful algal blooms (HABs), specifically targeting those relationships for which management actions may be appropriate. Academic, federal, and state agency representatives were in attendance. The following seven statements were unanimously adopted by attendees based on review and analysis of current as well as pertinent previous data: 1) Degraded water quality from increased nutrient pollution promotes the development and persistence of many HABs and is one of the reasons for their expansion in the U.S. and the world; 2) The composition – not just the total quantity – of the nutrient pool impacts HABs; 3) High biomass blooms must have exogenous nutrients to be sustained; 4) Both chronic and episodic nutrient delivery promote HAB development; 5) Recently developed tools and techniques are already improving the detection of some HABs, and emerging technologies are rapidly advancing toward operational status for the prediction of HABs and their toxins; 6) Experimental studies are critical to further the understanding of the role of nutrients in HAB expression, and will strengthen prediction and mitigation of HABs; and 7) Management of nutrient inputs to the watershed can lead to significant reduction in HABs. Supporting evidence and pertinent examples for each consensus statement is provided herein.
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            Cyanobacterial toxins: risk management for health protection.

            This paper reviews the occurrence and properties of cyanobacterial toxins, with reference to the recognition and management of the human health risks which they may present. Mass populations of toxin-producing cyanobacteria in natural and controlled waterbodies include blooms and scums of planktonic species, and mats and biofilms of benthic species. Toxic cyanobacterial populations have been reported in freshwaters in over 45 countries, and in numerous brackish, coastal, and marine environments. The principal toxigenic genera are listed. Known sources of the families of cyanobacterial toxins (hepato-, neuro-, and cytotoxins, irritants, and gastrointestinal toxins) are briefly discussed. Key procedures in the risk management of cyanobacterial toxins and cells are reviewed, including derivations (where sufficient data are available) of tolerable daily intakes (TDIs) and guideline values (GVs) with reference to the toxins in drinking water, and guideline levels for toxigenic cyanobacteria in bathing waters. Uncertainties and some gaps in knowledge are also discussed, including the importance of exposure media (animal and plant foods), in addition to potable and recreational waters. Finally, we present an outline of steps to develop and implement risk management strategies for cyanobacterial cells and toxins in waterbodies, with recent applications and the integration of Hazard Assessment Critical Control Point (HACCP) principles.
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              Eutrophication of aquatic ecosystems: bistability and soil phosphorus.

              Eutrophication (the overenrichment of aquatic ecosystems with nutrients leading to algal blooms and anoxic events) is a persistent condition of surface waters and a widespread environmental problem. Some lakes have recovered after sources of nutrients were reduced. In others, recycling of phosphorus from sediments enriched by years of high nutrient inputs causes lakes to remain eutrophic even after external inputs of phosphorus are decreased. Slow flux of phosphorus from overfertilized soils may be even more important for maintaining eutrophication of lakes in agricultural regions. This type of eutrophication is not reversible unless there are substantial changes in soil management. Technologies for rapidly reducing phosphorus content of overenriched soils, or reducing erosion rates, are needed to improve water quality.
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                Author and article information

                Contributors
                Role: Editor
                Journal
                PLoS One
                PLoS ONE
                plos
                plosone
                PLoS ONE
                Public Library of Science (San Francisco, CA USA )
                1932-6203
                9 June 2017
                2017
                : 12
                : 6
                : e0178976
                Affiliations
                [1 ]Laboratory of Ecology and Physiology of Phytoplankton, Department of Plant Biology, University of Rio de Janeiro State, Rio de Janeiro, Brazil
                [2 ]Aquatic Ecology & Water Quality Management Group, Department of Environmental Sciences, Wageningen University, Wageningen, The Netherlands
                [3 ]Museu Nacional, Federal University of Rio de Janeiro, Rio de Janeiro, Brazil
                [4 ]Chemistry Institute, University of Rio de Janeiro State, Rio de Janeiro, Rio de Janeiro, Brasil
                [5 ]Department of Aquatic Ecology, Netherlands Institute of Ecology (NIOO-KNAW), Wageningen, The Netherlands
                Natural Environment Research Council, UNITED KINGDOM
                Author notes

                Competing Interests: The authors have declared that no competing interests exist.

                • Conceptualization: ML NN MMM.

                • Formal analysis: NN ML MMM FO.

                • Funding acquisition: VH ML MMM.

                • Investigation: NN MMu LM MMi EL.

                • Methodology: NN ML MMM.

                • Writing – original draft: NN ML MMM LM MMu MMi FO VH EL.

                • Writing – review & editing: NN ML MMM LM MMu MMi FO VH EL.

                Author information
                http://orcid.org/0000-0001-5301-9408
                Article
                PONE-D-17-06914
                10.1371/journal.pone.0178976
                5466316
                28598977
                b0de4a3f-8190-4b78-a9d3-5922925ab8bf
                © 2017 Noyma et al

                This is an open access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.

                History
                : 20 February 2017
                : 22 May 2017
                Page count
                Figures: 5, Tables: 2, Pages: 16
                Funding
                Funded by: funder-id http://dx.doi.org/10.13039/501100003593, Conselho Nacional de Desenvolvimento Científico e Tecnológico;
                Award ID: 400408/2014-7
                Funded by: funder-id http://dx.doi.org/10.13039/501100004586, Fundação Carlos Chagas Filho de Amparo à Pesquisa do Estado do Rio de Janeiro;
                Award ID: 111.267/2014
                This study was sponsored by Conselho Nacional de Desenvolvimento Científico e Tecnológico (CNPq) through a Science without Borders Grant (400408/2014-7) and by Fudação de Apoio a Pesquisa do Estado do Rio de Janeiro (FAPERJ—111.267/2014). The funders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.
                Categories
                Research Article
                Biology and Life Sciences
                Organisms
                Bacteria
                Cyanobacteria
                Earth Sciences
                Marine and Aquatic Sciences
                Oceanography
                Water Columns
                Earth Sciences
                Hydrology
                Surface Water
                Physical Sciences
                Chemistry
                Chemical Compounds
                Chlorides
                Biology and Life Sciences
                Toxicology
                Toxic Agents
                Toxins
                Medicine and Health Sciences
                Pathology and Laboratory Medicine
                Toxicology
                Toxic Agents
                Toxins
                Physical Sciences
                Materials Science
                Materials by Structure
                Zeolites
                Physical Sciences
                Chemistry
                Chemical Elements
                Lanthanum
                Biology and Life Sciences
                Physiology
                Physiological Processes
                Tissue Repair
                Lysis (Medicine)
                Medicine and Health Sciences
                Physiology
                Physiological Processes
                Tissue Repair
                Lysis (Medicine)
                Custom metadata
                All relevant data are within the paper and its Supporting Information files.

                Uncategorized
                Uncategorized

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