Analysis of DDT and its metabolites in soil and water samples obtained in the vicinity of a closed-down factory in Bangladesh using various extraction methods

This study was conducted to monitor the spread of dichlorodiphenyltrichloroethane (DDT) and its metabolites (dichlorodiphenyldichloroethylene (DDE), dichlorodiphenyldichloroethane (DDD)) in soil and water to regions surrounding a closed DDT factory in Bangladesh. This fulfillment was accomplished us...

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Veröffentlicht in:Environmental monitoring and assessment 2015-12, Vol.187 (12), p.743-12, Article 743
Hauptverfasser: Al Mahmud, M. N. U, Khalil, Farzana, Rahman, Md. Musfiqur, Mamun, M. I. R, Shoeb, Mohammad, Abd El-Aty, A. M, Park, Jong-Hyouk, Shin, Ho-Chul, Nahar, Nilufar, Shim, Jae-Han
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container_issue 12
container_start_page 743
container_title Environmental monitoring and assessment
container_volume 187
creator Al Mahmud, M. N. U
Khalil, Farzana
Rahman, Md. Musfiqur
Mamun, M. I. R
Shoeb, Mohammad
Abd El-Aty, A. M
Park, Jong-Hyouk
Shin, Ho-Chul
Nahar, Nilufar
Shim, Jae-Han
description This study was conducted to monitor the spread of dichlorodiphenyltrichloroethane (DDT) and its metabolites (dichlorodiphenyldichloroethylene (DDE), dichlorodiphenyldichloroethane (DDD)) in soil and water to regions surrounding a closed DDT factory in Bangladesh. This fulfillment was accomplished using inter-method and inter-laboratory validation studies. DDTs (DDT and its metabolites) from soil samples were extracted using microwave-assisted extraction (MAE), supercritical fluid extraction (SFE), and solvent extraction (SE). Inter-laboratory calibration was assessed by SE, and all methods were validated by intra- and inter-day accuracy (expressed as recovery %) and precision (expressed as relative standard deviation (RSD)) in the same laboratory, at three fortified concentrations (n = 4). DDTs extracted from water samples by liquid-liquid partitioning and all samples were analyzed by gas chromatography (GC)-electron capture detector (ECD) and confirmed by GC/mass spectrometry (GC/MS). Linearities expressed as determination coefficients (R ²) were ≥0.995 for matrix-matched calibrations. The recovery rate was in the range of 72–120 and 83–110 %, with
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N. U ; Khalil, Farzana ; Rahman, Md. Musfiqur ; Mamun, M. I. R ; Shoeb, Mohammad ; Abd El-Aty, A. M ; Park, Jong-Hyouk ; Shin, Ho-Chul ; Nahar, Nilufar ; Shim, Jae-Han</creator><creatorcontrib>Al Mahmud, M. N. U ; Khalil, Farzana ; Rahman, Md. Musfiqur ; Mamun, M. I. R ; Shoeb, Mohammad ; Abd El-Aty, A. M ; Park, Jong-Hyouk ; Shin, Ho-Chul ; Nahar, Nilufar ; Shim, Jae-Han</creatorcontrib><description>This study was conducted to monitor the spread of dichlorodiphenyltrichloroethane (DDT) and its metabolites (dichlorodiphenyldichloroethylene (DDE), dichlorodiphenyldichloroethane (DDD)) in soil and water to regions surrounding a closed DDT factory in Bangladesh. This fulfillment was accomplished using inter-method and inter-laboratory validation studies. DDTs (DDT and its metabolites) from soil samples were extracted using microwave-assisted extraction (MAE), supercritical fluid extraction (SFE), and solvent extraction (SE). Inter-laboratory calibration was assessed by SE, and all methods were validated by intra- and inter-day accuracy (expressed as recovery %) and precision (expressed as relative standard deviation (RSD)) in the same laboratory, at three fortified concentrations (n = 4). DDTs extracted from water samples by liquid-liquid partitioning and all samples were analyzed by gas chromatography (GC)-electron capture detector (ECD) and confirmed by GC/mass spectrometry (GC/MS). Linearities expressed as determination coefficients (R ²) were ≥0.995 for matrix-matched calibrations. The recovery rate was in the range of 72–120 and 83–110 %, with &lt;15 % RSD in soil and water, respectively. The limit of quantification (LOQ) was 0.0165 mg kg⁻¹ in soil and 0.132 μg L⁻¹ in water. Greater quantities of DDTs were extracted from soil using the MAE and SE techniques than with the SFE method. Higher amounts of DDTs were discovered in the southern (2.2–936 × 10² mg kg⁻¹) or southwestern (86.3–2067 × 10² mg kg⁻¹) direction from the factory than in the eastern direction (1.0–48.6 × 10² mg kg⁻¹). An exception was the soil sample collected 50 ft (15.24 m) east (2904 × 10² mg kg⁻¹) of the factory. The spread of DDTs in the water bodies (0.59–3.01 μg L⁻¹) was approximately equal in all directions. 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N. U</creatorcontrib><creatorcontrib>Khalil, Farzana</creatorcontrib><creatorcontrib>Rahman, Md. Musfiqur</creatorcontrib><creatorcontrib>Mamun, M. I. R</creatorcontrib><creatorcontrib>Shoeb, Mohammad</creatorcontrib><creatorcontrib>Abd El-Aty, A. M</creatorcontrib><creatorcontrib>Park, Jong-Hyouk</creatorcontrib><creatorcontrib>Shin, Ho-Chul</creatorcontrib><creatorcontrib>Nahar, Nilufar</creatorcontrib><creatorcontrib>Shim, Jae-Han</creatorcontrib><title>Analysis of DDT and its metabolites in soil and water samples obtained in the vicinity of a closed-down factory in Bangladesh using various extraction methods</title><title>Environmental monitoring and assessment</title><addtitle>Environ Monit Assess</addtitle><addtitle>Environ Monit Assess</addtitle><description>This study was conducted to monitor the spread of dichlorodiphenyltrichloroethane (DDT) and its metabolites (dichlorodiphenyldichloroethylene (DDE), dichlorodiphenyldichloroethane (DDD)) in soil and water to regions surrounding a closed DDT factory in Bangladesh. This fulfillment was accomplished using inter-method and inter-laboratory validation studies. DDTs (DDT and its metabolites) from soil samples were extracted using microwave-assisted extraction (MAE), supercritical fluid extraction (SFE), and solvent extraction (SE). Inter-laboratory calibration was assessed by SE, and all methods were validated by intra- and inter-day accuracy (expressed as recovery %) and precision (expressed as relative standard deviation (RSD)) in the same laboratory, at three fortified concentrations (n = 4). DDTs extracted from water samples by liquid-liquid partitioning and all samples were analyzed by gas chromatography (GC)-electron capture detector (ECD) and confirmed by GC/mass spectrometry (GC/MS). Linearities expressed as determination coefficients (R ²) were ≥0.995 for matrix-matched calibrations. The recovery rate was in the range of 72–120 and 83–110 %, with &lt;15 % RSD in soil and water, respectively. The limit of quantification (LOQ) was 0.0165 mg kg⁻¹ in soil and 0.132 μg L⁻¹ in water. Greater quantities of DDTs were extracted from soil using the MAE and SE techniques than with the SFE method. Higher amounts of DDTs were discovered in the southern (2.2–936 × 10² mg kg⁻¹) or southwestern (86.3–2067 × 10² mg kg⁻¹) direction from the factory than in the eastern direction (1.0–48.6 × 10² mg kg⁻¹). An exception was the soil sample collected 50 ft (15.24 m) east (2904 × 10² mg kg⁻¹) of the factory. The spread of DDTs in the water bodies (0.59–3.01 μg L⁻¹) was approximately equal in all directions. We concluded that DDTs might have been dumped randomly around the warehouse after the closing of the factory.</description><subject>Atmospheric Protection/Air Quality Control/Air Pollution</subject><subject>Bangladesh</subject><subject>Chromatography</subject><subject>Chromatography, Gas</subject><subject>Collaboration</subject><subject>DDD</subject><subject>DDD (pesticide)</subject><subject>DDE</subject><subject>DDE (pesticide)</subject><subject>DDT</subject><subject>DDT (pesticide)</subject><subject>DDT - analysis</subject><subject>Dichlorodiphenyl Dichloroethylene - analysis</subject><subject>Earth and Environmental Science</subject><subject>Ecology</subject><subject>Ecotoxicology</subject><subject>Environment</subject><subject>Environmental Management</subject><subject>Environmental monitoring</subject><subject>Environmental Monitoring - methods</subject><subject>Environmental research</subject><subject>Food contamination &amp; poisoning</subject><subject>Gas chromatography</subject><subject>gas chromatography-mass spectrometry</subject><subject>Hydrocarbons, Chlorinated - analysis</subject><subject>Laboratories</subject><subject>Life sciences</subject><subject>Mass spectrometry</subject><subject>Metabolites</subject><subject>Methods</subject><subject>microwave treatment</subject><subject>Monitoring/Environmental Analysis</subject><subject>Nitrous oxide</subject><subject>Pesticides</subject><subject>Sediments</subject><subject>Soil - chemistry</subject><subject>Soil Pollutants - analysis</subject><subject>soil sampling</subject><subject>Soils</subject><subject>Solvent extraction</subject><subject>Solvent extraction processes</subject><subject>solvents</subject><subject>supercritical fluid extraction</subject><subject>surface water</subject><subject>Veterinary medicine</subject><subject>Water</subject><subject>Water analysis</subject><subject>Water Pollutants, Chemical - analysis</subject><subject>Water sampling</subject><issn>0167-6369</issn><issn>1573-2959</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2015</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><sourceid>ABUWG</sourceid><sourceid>AFKRA</sourceid><sourceid>AZQEC</sourceid><sourceid>BENPR</sourceid><sourceid>CCPQU</sourceid><sourceid>DWQXO</sourceid><sourceid>GNUQQ</sourceid><recordid>eNp9kk9vFSEUxYnR2Gf1A7hREjduRoEZ4LGsrf-SJi5s14QZ4D2aGXhymdb3ZfysMk41xoULwuL8zrnkHhB6TskbSoh8C5QIQRtCedMpwRv1AG0ol23DFFcP0YZQIRvRCnWCngDcEEKU7NRjdMIE54pzuUE_zqIZjxAAJ48vLq6wiRaHAnhyxfRpDMUBDhFDCuMv7c4UlzGY6TBWJfXFhOjsgpS9w7dhCDGU45Jm8DAmcLax6S5ib4aS8nEB35m4G411sMczhLjDtyaHNAN230uuWEhxGb9PFp6iR96M4J7d36fo-sP7q_NPzeWXj5_Pzy6boVOqNFI46zvhW2a3hPRcMt931EvTDr0ZjPPKyt7ZCrdSsY7IlhFmves6RRTvTXuKXq-5h5y-zQ6KngIMbhxNdPVlmm7Jtl2OrOirf9CbNOe6xUrV7fKtkpRXiq7UkBNAdl4fcphMPmpK9FKeXsvTtTy9lKdV9by4T577ydk_jt9tVYCtAFQp7lz-a_R_Ul-uJm-SNrscQF9_ZfVrEEKZIFS2PwEyRrBG</recordid><startdate>20151201</startdate><enddate>20151201</enddate><creator>Al Mahmud, M. 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N. U ; Khalil, Farzana ; Rahman, Md. Musfiqur ; Mamun, M. I. R ; Shoeb, Mohammad ; Abd El-Aty, A. 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M</au><au>Park, Jong-Hyouk</au><au>Shin, Ho-Chul</au><au>Nahar, Nilufar</au><au>Shim, Jae-Han</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Analysis of DDT and its metabolites in soil and water samples obtained in the vicinity of a closed-down factory in Bangladesh using various extraction methods</atitle><jtitle>Environmental monitoring and assessment</jtitle><stitle>Environ Monit Assess</stitle><addtitle>Environ Monit Assess</addtitle><date>2015-12-01</date><risdate>2015</risdate><volume>187</volume><issue>12</issue><spage>743</spage><epage>12</epage><pages>743-12</pages><artnum>743</artnum><issn>0167-6369</issn><eissn>1573-2959</eissn><abstract>This study was conducted to monitor the spread of dichlorodiphenyltrichloroethane (DDT) and its metabolites (dichlorodiphenyldichloroethylene (DDE), dichlorodiphenyldichloroethane (DDD)) in soil and water to regions surrounding a closed DDT factory in Bangladesh. This fulfillment was accomplished using inter-method and inter-laboratory validation studies. DDTs (DDT and its metabolites) from soil samples were extracted using microwave-assisted extraction (MAE), supercritical fluid extraction (SFE), and solvent extraction (SE). Inter-laboratory calibration was assessed by SE, and all methods were validated by intra- and inter-day accuracy (expressed as recovery %) and precision (expressed as relative standard deviation (RSD)) in the same laboratory, at three fortified concentrations (n = 4). DDTs extracted from water samples by liquid-liquid partitioning and all samples were analyzed by gas chromatography (GC)-electron capture detector (ECD) and confirmed by GC/mass spectrometry (GC/MS). Linearities expressed as determination coefficients (R ²) were ≥0.995 for matrix-matched calibrations. The recovery rate was in the range of 72–120 and 83–110 %, with &lt;15 % RSD in soil and water, respectively. The limit of quantification (LOQ) was 0.0165 mg kg⁻¹ in soil and 0.132 μg L⁻¹ in water. Greater quantities of DDTs were extracted from soil using the MAE and SE techniques than with the SFE method. Higher amounts of DDTs were discovered in the southern (2.2–936 × 10² mg kg⁻¹) or southwestern (86.3–2067 × 10² mg kg⁻¹) direction from the factory than in the eastern direction (1.0–48.6 × 10² mg kg⁻¹). An exception was the soil sample collected 50 ft (15.24 m) east (2904 × 10² mg kg⁻¹) of the factory. The spread of DDTs in the water bodies (0.59–3.01 μg L⁻¹) was approximately equal in all directions. We concluded that DDTs might have been dumped randomly around the warehouse after the closing of the factory.</abstract><cop>Cham</cop><pub>Springer International Publishing</pub><pmid>26559557</pmid><doi>10.1007/s10661-015-4965-9</doi><tpages>12</tpages></addata></record>
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subjects Atmospheric Protection/Air Quality Control/Air Pollution
Bangladesh
Chromatography
Chromatography, Gas
Collaboration
DDD
DDD (pesticide)
DDE
DDE (pesticide)
DDT
DDT (pesticide)
DDT - analysis
Dichlorodiphenyl Dichloroethylene - analysis
Earth and Environmental Science
Ecology
Ecotoxicology
Environment
Environmental Management
Environmental monitoring
Environmental Monitoring - methods
Environmental research
Food contamination & poisoning
Gas chromatography
gas chromatography-mass spectrometry
Hydrocarbons, Chlorinated - analysis
Laboratories
Life sciences
Mass spectrometry
Metabolites
Methods
microwave treatment
Monitoring/Environmental Analysis
Nitrous oxide
Pesticides
Sediments
Soil - chemistry
Soil Pollutants - analysis
soil sampling
Soils
Solvent extraction
Solvent extraction processes
solvents
supercritical fluid extraction
surface water
Veterinary medicine
Water
Water analysis
Water Pollutants, Chemical - analysis
Water sampling
title Analysis of DDT and its metabolites in soil and water samples obtained in the vicinity of a closed-down factory in Bangladesh using various extraction methods
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