Evaluation on bioaccessibility of arsenic in the arsenic-contaminated soil
Abstract Korea Ministry of Environment regulates the soil quality based on the pseudo-total content of metals extracted by aqua-regia, and the concentration of metals has been used in the risk assessment of the contaminated site. The pseudo-total content of metals can be accepted conservatively as a...
Ausführliche Beschreibung
Gespeichert in:
| Autor*in: |
Min, Su-Jin [verfasserIn] |
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| Format: |
E-Artikel |
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| Sprache: |
Englisch |
| Erschienen: |
2019 |
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| Schlagwörter: |
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| Anmerkung: |
© The Korean Institute of Chemical Engineers 2019 |
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| Übergeordnetes Werk: |
Enthalten in: The Korean journal of chemical engineering - Seoul : Inst., 1984, 36(2019), 11 vom: Nov., Seite 1780-1784 |
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| Übergeordnetes Werk: |
volume:36 ; year:2019 ; number:11 ; month:11 ; pages:1780-1784 |
| Links: |
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| DOI / URN: |
10.1007/s11814-019-0383-y |
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SPR02252522X |
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| 245 | 1 | 0 | |a Evaluation on bioaccessibility of arsenic in the arsenic-contaminated soil |
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| 520 | |a Abstract Korea Ministry of Environment regulates the soil quality based on the pseudo-total content of metals extracted by aqua-regia, and the concentration of metals has been used in the risk assessment of the contaminated site. The pseudo-total content of metals can be accepted conservatively as a potentially risky concentration of metals in the soil. However, only some portion of metals in the soil are absorbed by plants, animals, and human beings, and the pseudo-total content used in the risk assessment tend to overestimate the risk of metal contamination. Therefore, the pseudo-total content does not reflect the real risk of the contamination. Bioavailability and bioaccessibility can be alternatives for the pseudo-total content to estimate the reasonable risk. Bioaccessible concentration can be analyzed as in-vitro by the amounts of metals extracted in the gastrointestinal situation, and the bioaccessible concentration is the maximum amount of metals to be absorbed. The bioaccessible concentration of As was evaluated, compared with the pseudo-total concentration of As, and the correlation between the concentration of As and physicochemical properties of soil was analyzed. The bioaccessible concentration can be estimated by the labile fractions of As, and Si, Al, and Mn content decrease the bioaccessible concentration of As. | ||
| 650 | 4 | |a Bioaccessibility |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Arsenic |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Fractionation |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Risk Assessment |7 (dpeaa)DE-He213 | |
| 700 | 1 | |a Kim, Hye-Bin |4 aut | |
| 700 | 1 | |a Kim, Seon-Hee |4 aut | |
| 700 | 1 | |a Baek, Kitae |4 aut | |
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10.1007/s11814-019-0383-y doi (DE-627)SPR02252522X (SPR)s11814-019-0383-y-e DE-627 ger DE-627 rakwb eng Min, Su-Jin verfasserin aut Evaluation on bioaccessibility of arsenic in the arsenic-contaminated soil 2019 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © The Korean Institute of Chemical Engineers 2019 Abstract Korea Ministry of Environment regulates the soil quality based on the pseudo-total content of metals extracted by aqua-regia, and the concentration of metals has been used in the risk assessment of the contaminated site. The pseudo-total content of metals can be accepted conservatively as a potentially risky concentration of metals in the soil. However, only some portion of metals in the soil are absorbed by plants, animals, and human beings, and the pseudo-total content used in the risk assessment tend to overestimate the risk of metal contamination. Therefore, the pseudo-total content does not reflect the real risk of the contamination. Bioavailability and bioaccessibility can be alternatives for the pseudo-total content to estimate the reasonable risk. Bioaccessible concentration can be analyzed as in-vitro by the amounts of metals extracted in the gastrointestinal situation, and the bioaccessible concentration is the maximum amount of metals to be absorbed. The bioaccessible concentration of As was evaluated, compared with the pseudo-total concentration of As, and the correlation between the concentration of As and physicochemical properties of soil was analyzed. The bioaccessible concentration can be estimated by the labile fractions of As, and Si, Al, and Mn content decrease the bioaccessible concentration of As. Bioaccessibility (dpeaa)DE-He213 Arsenic (dpeaa)DE-He213 Fractionation (dpeaa)DE-He213 Risk Assessment (dpeaa)DE-He213 Kim, Hye-Bin aut Kim, Seon-Hee aut Baek, Kitae aut Enthalten in The Korean journal of chemical engineering Seoul : Inst., 1984 36(2019), 11 vom: Nov., Seite 1780-1784 (DE-627)391337246 (DE-600)2152566-3 1975-7220 nnns volume:36 year:2019 number:11 month:11 pages:1780-1784 https://dx.doi.org/10.1007/s11814-019-0383-y lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 36 2019 11 11 1780-1784 |
| spelling |
10.1007/s11814-019-0383-y doi (DE-627)SPR02252522X (SPR)s11814-019-0383-y-e DE-627 ger DE-627 rakwb eng Min, Su-Jin verfasserin aut Evaluation on bioaccessibility of arsenic in the arsenic-contaminated soil 2019 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © The Korean Institute of Chemical Engineers 2019 Abstract Korea Ministry of Environment regulates the soil quality based on the pseudo-total content of metals extracted by aqua-regia, and the concentration of metals has been used in the risk assessment of the contaminated site. The pseudo-total content of metals can be accepted conservatively as a potentially risky concentration of metals in the soil. However, only some portion of metals in the soil are absorbed by plants, animals, and human beings, and the pseudo-total content used in the risk assessment tend to overestimate the risk of metal contamination. Therefore, the pseudo-total content does not reflect the real risk of the contamination. Bioavailability and bioaccessibility can be alternatives for the pseudo-total content to estimate the reasonable risk. Bioaccessible concentration can be analyzed as in-vitro by the amounts of metals extracted in the gastrointestinal situation, and the bioaccessible concentration is the maximum amount of metals to be absorbed. The bioaccessible concentration of As was evaluated, compared with the pseudo-total concentration of As, and the correlation between the concentration of As and physicochemical properties of soil was analyzed. The bioaccessible concentration can be estimated by the labile fractions of As, and Si, Al, and Mn content decrease the bioaccessible concentration of As. Bioaccessibility (dpeaa)DE-He213 Arsenic (dpeaa)DE-He213 Fractionation (dpeaa)DE-He213 Risk Assessment (dpeaa)DE-He213 Kim, Hye-Bin aut Kim, Seon-Hee aut Baek, Kitae aut Enthalten in The Korean journal of chemical engineering Seoul : Inst., 1984 36(2019), 11 vom: Nov., Seite 1780-1784 (DE-627)391337246 (DE-600)2152566-3 1975-7220 nnns volume:36 year:2019 number:11 month:11 pages:1780-1784 https://dx.doi.org/10.1007/s11814-019-0383-y lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 36 2019 11 11 1780-1784 |
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10.1007/s11814-019-0383-y doi (DE-627)SPR02252522X (SPR)s11814-019-0383-y-e DE-627 ger DE-627 rakwb eng Min, Su-Jin verfasserin aut Evaluation on bioaccessibility of arsenic in the arsenic-contaminated soil 2019 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © The Korean Institute of Chemical Engineers 2019 Abstract Korea Ministry of Environment regulates the soil quality based on the pseudo-total content of metals extracted by aqua-regia, and the concentration of metals has been used in the risk assessment of the contaminated site. The pseudo-total content of metals can be accepted conservatively as a potentially risky concentration of metals in the soil. However, only some portion of metals in the soil are absorbed by plants, animals, and human beings, and the pseudo-total content used in the risk assessment tend to overestimate the risk of metal contamination. Therefore, the pseudo-total content does not reflect the real risk of the contamination. Bioavailability and bioaccessibility can be alternatives for the pseudo-total content to estimate the reasonable risk. Bioaccessible concentration can be analyzed as in-vitro by the amounts of metals extracted in the gastrointestinal situation, and the bioaccessible concentration is the maximum amount of metals to be absorbed. The bioaccessible concentration of As was evaluated, compared with the pseudo-total concentration of As, and the correlation between the concentration of As and physicochemical properties of soil was analyzed. The bioaccessible concentration can be estimated by the labile fractions of As, and Si, Al, and Mn content decrease the bioaccessible concentration of As. Bioaccessibility (dpeaa)DE-He213 Arsenic (dpeaa)DE-He213 Fractionation (dpeaa)DE-He213 Risk Assessment (dpeaa)DE-He213 Kim, Hye-Bin aut Kim, Seon-Hee aut Baek, Kitae aut Enthalten in The Korean journal of chemical engineering Seoul : Inst., 1984 36(2019), 11 vom: Nov., Seite 1780-1784 (DE-627)391337246 (DE-600)2152566-3 1975-7220 nnns volume:36 year:2019 number:11 month:11 pages:1780-1784 https://dx.doi.org/10.1007/s11814-019-0383-y lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 36 2019 11 11 1780-1784 |
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10.1007/s11814-019-0383-y doi (DE-627)SPR02252522X (SPR)s11814-019-0383-y-e DE-627 ger DE-627 rakwb eng Min, Su-Jin verfasserin aut Evaluation on bioaccessibility of arsenic in the arsenic-contaminated soil 2019 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © The Korean Institute of Chemical Engineers 2019 Abstract Korea Ministry of Environment regulates the soil quality based on the pseudo-total content of metals extracted by aqua-regia, and the concentration of metals has been used in the risk assessment of the contaminated site. The pseudo-total content of metals can be accepted conservatively as a potentially risky concentration of metals in the soil. However, only some portion of metals in the soil are absorbed by plants, animals, and human beings, and the pseudo-total content used in the risk assessment tend to overestimate the risk of metal contamination. Therefore, the pseudo-total content does not reflect the real risk of the contamination. Bioavailability and bioaccessibility can be alternatives for the pseudo-total content to estimate the reasonable risk. Bioaccessible concentration can be analyzed as in-vitro by the amounts of metals extracted in the gastrointestinal situation, and the bioaccessible concentration is the maximum amount of metals to be absorbed. The bioaccessible concentration of As was evaluated, compared with the pseudo-total concentration of As, and the correlation between the concentration of As and physicochemical properties of soil was analyzed. The bioaccessible concentration can be estimated by the labile fractions of As, and Si, Al, and Mn content decrease the bioaccessible concentration of As. Bioaccessibility (dpeaa)DE-He213 Arsenic (dpeaa)DE-He213 Fractionation (dpeaa)DE-He213 Risk Assessment (dpeaa)DE-He213 Kim, Hye-Bin aut Kim, Seon-Hee aut Baek, Kitae aut Enthalten in The Korean journal of chemical engineering Seoul : Inst., 1984 36(2019), 11 vom: Nov., Seite 1780-1784 (DE-627)391337246 (DE-600)2152566-3 1975-7220 nnns volume:36 year:2019 number:11 month:11 pages:1780-1784 https://dx.doi.org/10.1007/s11814-019-0383-y lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 36 2019 11 11 1780-1784 |
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10.1007/s11814-019-0383-y doi (DE-627)SPR02252522X (SPR)s11814-019-0383-y-e DE-627 ger DE-627 rakwb eng Min, Su-Jin verfasserin aut Evaluation on bioaccessibility of arsenic in the arsenic-contaminated soil 2019 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © The Korean Institute of Chemical Engineers 2019 Abstract Korea Ministry of Environment regulates the soil quality based on the pseudo-total content of metals extracted by aqua-regia, and the concentration of metals has been used in the risk assessment of the contaminated site. The pseudo-total content of metals can be accepted conservatively as a potentially risky concentration of metals in the soil. However, only some portion of metals in the soil are absorbed by plants, animals, and human beings, and the pseudo-total content used in the risk assessment tend to overestimate the risk of metal contamination. Therefore, the pseudo-total content does not reflect the real risk of the contamination. Bioavailability and bioaccessibility can be alternatives for the pseudo-total content to estimate the reasonable risk. Bioaccessible concentration can be analyzed as in-vitro by the amounts of metals extracted in the gastrointestinal situation, and the bioaccessible concentration is the maximum amount of metals to be absorbed. The bioaccessible concentration of As was evaluated, compared with the pseudo-total concentration of As, and the correlation between the concentration of As and physicochemical properties of soil was analyzed. The bioaccessible concentration can be estimated by the labile fractions of As, and Si, Al, and Mn content decrease the bioaccessible concentration of As. Bioaccessibility (dpeaa)DE-He213 Arsenic (dpeaa)DE-He213 Fractionation (dpeaa)DE-He213 Risk Assessment (dpeaa)DE-He213 Kim, Hye-Bin aut Kim, Seon-Hee aut Baek, Kitae aut Enthalten in The Korean journal of chemical engineering Seoul : Inst., 1984 36(2019), 11 vom: Nov., Seite 1780-1784 (DE-627)391337246 (DE-600)2152566-3 1975-7220 nnns volume:36 year:2019 number:11 month:11 pages:1780-1784 https://dx.doi.org/10.1007/s11814-019-0383-y lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 36 2019 11 11 1780-1784 |
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Enthalten in The Korean journal of chemical engineering 36(2019), 11 vom: Nov., Seite 1780-1784 volume:36 year:2019 number:11 month:11 pages:1780-1784 |
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Min, Su-Jin |
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Evaluation on bioaccessibility of arsenic in the arsenic-contaminated soil Bioaccessibility (dpeaa)DE-He213 Arsenic (dpeaa)DE-He213 Fractionation (dpeaa)DE-He213 Risk Assessment (dpeaa)DE-He213 |
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Evaluation on bioaccessibility of arsenic in the arsenic-contaminated soil |
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Min, Su-Jin Kim, Hye-Bin Kim, Seon-Hee Baek, Kitae |
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evaluation on bioaccessibility of arsenic in the arsenic-contaminated soil |
| title_auth |
Evaluation on bioaccessibility of arsenic in the arsenic-contaminated soil |
| abstract |
Abstract Korea Ministry of Environment regulates the soil quality based on the pseudo-total content of metals extracted by aqua-regia, and the concentration of metals has been used in the risk assessment of the contaminated site. The pseudo-total content of metals can be accepted conservatively as a potentially risky concentration of metals in the soil. However, only some portion of metals in the soil are absorbed by plants, animals, and human beings, and the pseudo-total content used in the risk assessment tend to overestimate the risk of metal contamination. Therefore, the pseudo-total content does not reflect the real risk of the contamination. Bioavailability and bioaccessibility can be alternatives for the pseudo-total content to estimate the reasonable risk. Bioaccessible concentration can be analyzed as in-vitro by the amounts of metals extracted in the gastrointestinal situation, and the bioaccessible concentration is the maximum amount of metals to be absorbed. The bioaccessible concentration of As was evaluated, compared with the pseudo-total concentration of As, and the correlation between the concentration of As and physicochemical properties of soil was analyzed. The bioaccessible concentration can be estimated by the labile fractions of As, and Si, Al, and Mn content decrease the bioaccessible concentration of As. © The Korean Institute of Chemical Engineers 2019 |
| abstractGer |
Abstract Korea Ministry of Environment regulates the soil quality based on the pseudo-total content of metals extracted by aqua-regia, and the concentration of metals has been used in the risk assessment of the contaminated site. The pseudo-total content of metals can be accepted conservatively as a potentially risky concentration of metals in the soil. However, only some portion of metals in the soil are absorbed by plants, animals, and human beings, and the pseudo-total content used in the risk assessment tend to overestimate the risk of metal contamination. Therefore, the pseudo-total content does not reflect the real risk of the contamination. Bioavailability and bioaccessibility can be alternatives for the pseudo-total content to estimate the reasonable risk. Bioaccessible concentration can be analyzed as in-vitro by the amounts of metals extracted in the gastrointestinal situation, and the bioaccessible concentration is the maximum amount of metals to be absorbed. The bioaccessible concentration of As was evaluated, compared with the pseudo-total concentration of As, and the correlation between the concentration of As and physicochemical properties of soil was analyzed. The bioaccessible concentration can be estimated by the labile fractions of As, and Si, Al, and Mn content decrease the bioaccessible concentration of As. © The Korean Institute of Chemical Engineers 2019 |
| abstract_unstemmed |
Abstract Korea Ministry of Environment regulates the soil quality based on the pseudo-total content of metals extracted by aqua-regia, and the concentration of metals has been used in the risk assessment of the contaminated site. The pseudo-total content of metals can be accepted conservatively as a potentially risky concentration of metals in the soil. However, only some portion of metals in the soil are absorbed by plants, animals, and human beings, and the pseudo-total content used in the risk assessment tend to overestimate the risk of metal contamination. Therefore, the pseudo-total content does not reflect the real risk of the contamination. Bioavailability and bioaccessibility can be alternatives for the pseudo-total content to estimate the reasonable risk. Bioaccessible concentration can be analyzed as in-vitro by the amounts of metals extracted in the gastrointestinal situation, and the bioaccessible concentration is the maximum amount of metals to be absorbed. The bioaccessible concentration of As was evaluated, compared with the pseudo-total concentration of As, and the correlation between the concentration of As and physicochemical properties of soil was analyzed. The bioaccessible concentration can be estimated by the labile fractions of As, and Si, Al, and Mn content decrease the bioaccessible concentration of As. © The Korean Institute of Chemical Engineers 2019 |
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11 |
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Evaluation on bioaccessibility of arsenic in the arsenic-contaminated soil |
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https://dx.doi.org/10.1007/s11814-019-0383-y |
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Kim, Hye-Bin Kim, Seon-Hee Baek, Kitae |
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| doi_str |
10.1007/s11814-019-0383-y |
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2024-07-03T13:27:11.993Z |
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|
| score |
7.4003525 |