Arsenic removal by zero-valent iron: field, laboratory and modeling studies
Field and laboratory studies were conducted to elucidate the design factors and mechanisms of arsenic removal from contaminated ground water using zero-valent iron. Large scale, field pilot experiments demonstrated for more than 8 months that iron filing filters can efficiently remove arsenite from...
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Published in: | Water research (Oxford) Vol. 37; no. 6; pp. 1417 - 1425 |
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01-03-2003
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Abstract | Field and laboratory studies were conducted to elucidate the design factors and mechanisms of arsenic removal from contaminated ground water using zero-valent iron. Large scale, field pilot experiments demonstrated for more than 8 months that iron filing filters can efficiently remove arsenite from aqueous solutions to levels less than 10
μg/L. The maximum arsenic accumulation measured was 4.4
mg As/g of media. The iron filing filters leached significant quantities of iron (73% of the iron was leached). A critical design parameter of the system was found to be the hydraulic detention time of the water in the filter. TCLP analyses of the spent media indicated that the arsenic concentration in the leachate was two orders of magnitude lower than the 5
mg/L of TCLP for arsenic. Spectroscopic and laboratory arsenic leaching studies (alkaline extraction and TCLP) suggest that the arsenic surface precipitate is related to sulfur. The aging process (due to the longevity of the removal mechanism) makes the precipitation process virtually irreversible. A mathematical model was developed to simulate the removal process using a partitioning coefficient and a mass transfer process. Calibration of these parameters using the data for three columns revealed that the equilibrium-partitioning coefficient was the same for all three columns while the mass transfer coefficient was a function of the flow rate. The calibrated mass transfer coefficients are similar to those reported in the literature if they are normalized to the surface area of the media. |
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AbstractList | Field and laboratory studies were conducted to elucidate the design factors and mechanisms of arsenic removal from contaminated ground water using zero- valent iron. Large scale, field pilot experiments demonstrated for more than 8 months that iron filing filters can efficiently remove arsenite from aqueous solutions to levels less than 10 mu g/L. The maximum arsenic accumulation measured was 4.4 mg As/g of media. The iron filing filters leached significant quantities of iron (73% of the iron was leached). A critical design parameter of the system was found to be the hydraulic detention time of the water in the filter. TCLP analyses of the spent media indicated that the arsenic concentration in the leachate was two orders of magnitude lower than the 5 mg/L of TCLP for arsenic. Spectroscopic and laboratory arsenic leaching studies (alkaline extraction and TCLP) suggest that the arsenic surface precipitate is related to sulfur. The aging process (due to the longevity of the removal mechanism) makes the precipitation process virtually irreversible. A mathematical model was developed to simulate the removal process using a partitioning coefficient and a mass transfer process. Calibration of these parameters using the data for three columns revealed that the equilibrium- partitioning coefficient was the same for all three columns while the mass transfer coefficient was a function of the flow rate. The calibrated mass transfer coefficients are similar to those reported in the literature if they are normalized to the surface area of the media. Field and laboratory studies were conducted to elucidate the design factors and mechanisms of arsenic removal from contaminated ground water using zero-valent iron. Large scale, field pilot experiments demonstrated for more than 8 months that iron filing filters can efficiently remove arsenite from aqueous solutions to levels less than 10 micro g/L. The maximum arsenic accumulation measured was 4.4 mg As/g of media. The iron filing filters leached significant quantities of iron (73% of the iron was leached). A critical design parameter of the system was found to be the hydraulic detention time of the water in the filter. TCLP analyses of the spent media indicated that the arsenic concentration in the leachate was two orders of magnitude lower than the 5mg/L of TCLP for arsenic. Spectroscopic and laboratory arsenic leaching studies (alkaline extraction and TCLP) suggest that the arsenic surface precipitate is related to sulfur. The aging process (due to the longevity of the removal mechanism) makes the precipitation process virtually irreversible. A mathematical model was developed to simulate the removal process using a partitioning coefficient and a mass transfer process. Calibration of these parameters using the data for three columns revealed that the equilibrium-partitioning coefficient was the same for all three columns while the mass transfer coefficient was a function of the flow rate. The calibrated mass transfer coefficients are similar to those reported in the literature if they are normalized to the surface area of the media. Field and laboratory experiments were conducted to evaluate the use of zero-valent iron filtration to remove arsenic from groundwater. In the field, a pilot system was tested at a Superfund Site in Maine, while shorter-duration experiments were performed in the laboratory to examine the surface loading versus volumetric loading of the system and to ascertain how As was partitioned within the system. Spectroscopic studies were carried out to identify the binding relationships of As with other elements at the Fe super(0) surface. A mathematical models was also developed to investigate the design factors for scaling up the technology. Results from the field study revealed that an As removal efficiency of greater than 99% could be maintained for more than eight months without maintenance, but the Fe filing filters leached significant quantities of Fe over time. The As concentration in the spent media was much lower than regulated limits and could be disposed of safely. The spectroscopic studies revealed that As was associated with the surface of the Fe filing and was associated mostly with sulfur. Field and laboratory studies were conducted to elucidate the design factors and mechanisms of arsenic removal from contaminated ground water using zero-valent iron. Large scale, field pilot experiments demonstrated for more than 8 months that iron filing filters can efficiently remove arsenite from aqueous solutions to levels less than 10 μg/L. The maximum arsenic accumulation measured was 4.4 mg As/g of media. The iron filing filters leached significant quantities of iron (73% of the iron was leached). A critical design parameter of the system was found to be the hydraulic detention time of the water in the filter. TCLP analyses of the spent media indicated that the arsenic concentration in the leachate was two orders of magnitude lower than the 5 mg/L of TCLP for arsenic. Spectroscopic and laboratory arsenic leaching studies (alkaline extraction and TCLP) suggest that the arsenic surface precipitate is related to sulfur. The aging process (due to the longevity of the removal mechanism) makes the precipitation process virtually irreversible. A mathematical model was developed to simulate the removal process using a partitioning coefficient and a mass transfer process. Calibration of these parameters using the data for three columns revealed that the equilibrium-partitioning coefficient was the same for all three columns while the mass transfer coefficient was a function of the flow rate. The calibrated mass transfer coefficients are similar to those reported in the literature if they are normalized to the surface area of the media. |
Author | Lackovic, Jeffrey A Dobbs, Gregory M Nikolaidis, Nikolaos P |
Author_xml | – sequence: 1 givenname: Nikolaos P surname: Nikolaidis fullname: Nikolaidis, Nikolaos P email: nnikolai@mred.tuc.gr organization: Department of Environmental Engineering, Technical University of Crete, University Campus Chania, Crete 73100, Greece – sequence: 2 givenname: Gregory M surname: Dobbs fullname: Dobbs, Gregory M organization: United Technologies Research Center, United Technolgies, East Hartford, CT 06108, USA – sequence: 3 givenname: Jeffrey A surname: Lackovic fullname: Lackovic, Jeffrey A organization: Environmental Research Institute, The University of Connecticut, Storrs, CT 06269-2037, USA |
BackLink | https://www.ncbi.nlm.nih.gov/pubmed/12598205$$D View this record in MEDLINE/PubMed |
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Snippet | Field and laboratory studies were conducted to elucidate the design factors and mechanisms of arsenic removal from contaminated ground water using zero-valent... Field and laboratory experiments were conducted to evaluate the use of zero-valent iron filtration to remove arsenic from groundwater. In the field, a pilot... Field and laboratory studies were conducted to elucidate the design factors and mechanisms of arsenic removal from contaminated ground water using zero- valent... |
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SubjectTerms | Arsenic Arsenic - chemistry Arsenic - isolation & purification Environmental Monitoring Filtration Iron - chemistry Modeling Models, Theoretical Soil Pollutants - isolation & purification Water Pollutants - isolation & purification Water treatment technology Zero valent iron |
Title | Arsenic removal by zero-valent iron: field, laboratory and modeling studies |
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