Mobility and redox transformation of arsenic during treatment of artificially recharged groundwater for drinking water production
Autor: | Fabienne Battaglia-Brunet, Arslan Ahmad, Prosun Bhattacharya, Wim A. Oorthuizen, Albert van der Wal, Leo Heijnen, Brent Pieterse, Luuk de Waal |
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Přispěvatelé: | Bureau de Recherches Géologiques et Minières (BRGM) (BRGM) |
Jazyk: | angličtina |
Rok vydání: | 2020 |
Předmět: |
Environmental Engineering
0208 environmental biotechnology chemistry.chemical_element [SDU.STU]Sciences of the Universe [physics]/Earth Sciences 02 engineering and technology 010501 environmental sciences 01 natural sciences Chloride Ferric Compounds Slow sand filter Arsenic Water Purification chemistry.chemical_compound Rapid sand filter medicine Drinking water Waste Management and Disposal Effluent Groundwater ComputingMilieux_MISCELLANEOUS 0105 earth and related environmental sciences Water Science and Technology Civil and Structural Engineering WIMEK Fe(III)(oxyhydr)oxides Ecological Modeling Drinking Water Silicon Dioxide Pollution 6. Clean water 020801 environmental engineering Potassium permanganate chemistry [SDU]Sciences of the Universe [physics] Environmental chemistry Rapid sand filtration Environmental Technology Ferric Milieutechnologie Water treatment Oxidation-Reduction Co-precipitation Filtration Water Pollutants Chemical medicine.drug |
Zdroj: | Water Research Water Research, IWA Publishing, 2020, 178, pp.115826. ⟨10.1016/j.watres.2020.115826⟩ Water Research 178 (2020) Water Research, 178 |
ISSN: | 0043-1354 |
Popis: | In this study we investigate opportunities for reducing arsenic (As) to low levels, below 1 μg/L in produced drinking water from artificially infiltrated groundwater. We observe that rapid sand filtration is the most important treatment step for the oxidation and removal of As at water treatment plants which use artificially recharged groundwater as source. Removal of As is mainly due to As co-precipitation with Fe(III)(oxyhydr)oxides, which shows higher efficiency in rapid sand filter beds compared to aeration and supernatant storage. This is due to an accelerated oxidation of As(III) to As(V) in the filter bed which may be caused by the manganese oxides and/or As(III) oxidizing bacteria, as both are found in the coating of rapid sand filter media grains by chemical analysis and taxonomic profiling of the bacterial communities. Arsenic removal does not take place in treatment steps such as granular activated carbon filtration, ultrafiltration or slow sand filtration, due to a lack of hydrolyzing iron in their influent and a lack of adsorption affinity between As and the filtration surfaces. Further, we found that As reduction to below 1 μg/L can be effectively achieved at water treatment plants either by treating the influent of rapid sand filters by dosing potassium permanganate in combination with ferric chloride or by treating the effluent of rapid sand filters with ferric chloride dosing only. Finally, we observe that reducing the pH is an effective measure for increasing As co-precipitation with Fe(III)(oxyhydr)oxides, but only when the oxidized arsenic, As(V), is the predominant species in water. |
Databáze: | OpenAIRE |
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