A comparative assessment of human exposure to tetrabromobisphenol A and eight bisphenols including bisphenol A via indoor dust ingestion in twelve countries
Tetrabromobisphenol A (TBBPA) and eight bisphenol analogues (BPs) including bisphenol A (BPA) were determined in 388 indoor (including homes and microenvironments) dust samples collected from 12 countries (China, Colombia, Greece, India, Japan, Kuwait, Pakistan, Romania, Saudi Arabia, South Korea, U...
Saved in:
| Published in | Environment international Vol. 83; pp. 183 - 191 |
|---|---|
| Main Authors | , , , , , , , , , , , , |
| Format | Journal Article |
| Language | English |
| Published |
Netherlands
Elsevier Ltd
01.10.2015
|
| Subjects | |
| Online Access | Get full text |
Cover
Loading…
| Abstract | Tetrabromobisphenol A (TBBPA) and eight bisphenol analogues (BPs) including bisphenol A (BPA) were determined in 388 indoor (including homes and microenvironments) dust samples collected from 12 countries (China, Colombia, Greece, India, Japan, Kuwait, Pakistan, Romania, Saudi Arabia, South Korea, U.S., and Vietnam). The concentrations of TBBPA and sum of eight bisphenols (ƩBPs) in dust samples ranged from <1 to 3600 and from 13 to 110,000ng/g, respectively. The highest TBBPA concentrations in house dust were found in samples from Japan (median: 140ng/g), followed by South Korea (84ng/g) and China (23ng/g). The highest ∑BPs concentrations were found in Greece (median: 3900ng/g), Japan (2600ng/g) and the U.S. (2200ng/g). Significant variations in BPA concentrations were found in dust samples collected from various microenvironments in offices and homes. Concentrations of TBBPA in house dust were significantly correlated with BPA and ∑BPs. Among the nine target chemicals analyzed, BPA was the predominant compound in dust from all countries. The proportion of TBBPA in sum concentrations of nine phenolic compounds analyzed in this study was the highest in dust samples from China (27%) and the lowest in Greece (0.41%). The median estimated daily intake (EDI) of ∑BPs through dust ingestion was the highest in Greece (1.6–17ng/kgbw/day), Japan (1.3–16) and the U.S. (0.89–9.6) for various age groups. Nevertheless, in comparison with the reported BPA exposure doses through diet, dust ingestion accounted for less than 10% of the total exposure doses in China and the U.S. For TBBPA, the EDI for infants and toddlers ranged from 0.01 to 3.4ng/kgbw/day, and dust ingestion is an important pathway for exposure accounting for 3.8–35% (median) of exposure doses in China.
•TBBPA and bisphenols were measured in 388 indoor dust samples from 12 countries.•The contribution of house dust to daily intakes of TBBPA and BPA varied among countries.•Dust is an important source of TBBPA exposures in China, Japan and South Korea.•Dust ingestion accounted for 3.8–35% (median) of TBBPA exposure in China.•Contribution of dust to BPA intake is minor. |
|---|---|
| AbstractList | Tetrabromobisphenol A (TBBPA) and eight bisphenol analogues (BPs) including bisphenol A (BPA) were determined in 388 indoor (including homes and microenvironments) dust samples collected from 12 countries (China, Colombia, Greece, India, Japan, Kuwait, Pakistan, Romania, Saudi Arabia, South Korea, U.S., and Vietnam). The concentrations of TBBPA and sum of eight bisphenols (BPs) in dust samples ranged from <1 to 3600 and from 13 to 110,000ng/g, respectively. The highest TBBPA concentrations in house dust were found in samples from Japan (median: 140ng/g), followed by South Korea (84ng/g) and China (23ng/g). The highest capital sigma BPs concentrations were found in Greece (median: 3900ng/g), Japan (2600ng/g) and the U.S. (2200ng/g). Significant variations in BPA concentrations were found in dust samples collected from various microenvironments in offices and homes. Concentrations of TBBPA in house dust were significantly correlated with BPA and capital sigma BPs. Among the nine target chemicals analyzed, BPA was the predominant compound in dust from all countries. The proportion of TBBPA in sum concentrations of nine phenolic compounds analyzed in this study was the highest in dust samples from China (27%) and the lowest in Greece (0.41%). The median estimated daily intake (EDI) of capital sigma BPs through dust ingestion was the highest in Greece (1.6-17ng/kgbw/day), Japan (1.3-16) and the U.S. (0.89-9.6) for various age groups. Nevertheless, in comparison with the reported BPA exposure doses through diet, dust ingestion accounted for less than 10% of the total exposure doses in China and the U.S. For TBBPA, the EDI for infants and toddlers ranged from 0.01 to 3.4ng/kgbw/day, and dust ingestion is an important pathway for exposure accounting for 3.8-35% (median) of exposure doses in China. Tetrabromobisphenol A (TBBPA) and eight bisphenol analogues (BPs) including bisphenol A (BPA) were determined in 388 indoor (including homes and microenvironments) dust samples collected from 12 countries (China, Colombia, Greece, India, Japan, Kuwait, Pakistan, Romania, Saudi Arabia, South Korea, U.S., and Vietnam). The concentrations of TBBPA and sum of eight bisphenols (ƩBPs) in dust samples ranged from <1 to 3600 and from 13 to 110,000ng/g, respectively. The highest TBBPA concentrations in house dust were found in samples from Japan (median: 140ng/g), followed by South Korea (84ng/g) and China (23ng/g). The highest ∑BPs concentrations were found in Greece (median: 3900ng/g), Japan (2600ng/g) and the U.S. (2200ng/g). Significant variations in BPA concentrations were found in dust samples collected from various microenvironments in offices and homes. Concentrations of TBBPA in house dust were significantly correlated with BPA and ∑BPs. Among the nine target chemicals analyzed, BPA was the predominant compound in dust from all countries. The proportion of TBBPA in sum concentrations of nine phenolic compounds analyzed in this study was the highest in dust samples from China (27%) and the lowest in Greece (0.41%). The median estimated daily intake (EDI) of ∑BPs through dust ingestion was the highest in Greece (1.6–17ng/kgbw/day), Japan (1.3–16) and the U.S. (0.89–9.6) for various age groups. Nevertheless, in comparison with the reported BPA exposure doses through diet, dust ingestion accounted for less than 10% of the total exposure doses in China and the U.S. For TBBPA, the EDI for infants and toddlers ranged from 0.01 to 3.4ng/kgbw/day, and dust ingestion is an important pathway for exposure accounting for 3.8–35% (median) of exposure doses in China. •TBBPA and bisphenols were measured in 388 indoor dust samples from 12 countries.•The contribution of house dust to daily intakes of TBBPA and BPA varied among countries.•Dust is an important source of TBBPA exposures in China, Japan and South Korea.•Dust ingestion accounted for 3.8–35% (median) of TBBPA exposure in China.•Contribution of dust to BPA intake is minor. Tetrabromobisphenol A (TBBPA) and eight bisphenol analogues (BPs) including bisphenol A (BPA) were determined in 388 indoor (including homes and microenvironments) dust samples collected from 12 countries (China, Colombia, Greece, India, Japan, Kuwait, Pakistan, Romania, Saudi Arabia, South Korea, U.S., and Vietnam). The concentrations of TBBPA and sum of eight bisphenols (ƩBPs) in dust samples ranged from <1 to 3600 and from 13 to 110,000ng/g, respectively. The highest TBBPA concentrations in house dust were found in samples from Japan (median: 140ng/g), followed by South Korea (84ng/g) and China (23ng/g). The highest ∑BPs concentrations were found in Greece (median: 3900ng/g), Japan (2600ng/g) and the U.S. (2200ng/g). Significant variations in BPA concentrations were found in dust samples collected from various microenvironments in offices and homes. Concentrations of TBBPA in house dust were significantly correlated with BPA and ∑BPs. Among the nine target chemicals analyzed, BPA was the predominant compound in dust from all countries. The proportion of TBBPA in sum concentrations of nine phenolic compounds analyzed in this study was the highest in dust samples from China (27%) and the lowest in Greece (0.41%). The median estimated daily intake (EDI) of ∑BPs through dust ingestion was the highest in Greece (1.6–17ng/kgbw/day), Japan (1.3–16) and the U.S. (0.89–9.6) for various age groups. Nevertheless, in comparison with the reported BPA exposure doses through diet, dust ingestion accounted for less than 10% of the total exposure doses in China and the U.S. For TBBPA, the EDI for infants and toddlers ranged from 0.01 to 3.4ng/kgbw/day, and dust ingestion is an important pathway for exposure accounting for 3.8–35% (median) of exposure doses in China. Tetrabromobisphenol A (TBBPA) and eight bisphenol analogues (BPs) including bisphenol A (BPA) were determined in 388 indoor (including homes and microenvironments) dust samples collected from 12 countries (China, Colombia, Greece, India, Japan, Kuwait, Pakistan, Romania, Saudi Arabia, South Korea, U.S., and Vietnam). The concentrations of TBBPA and sum of eight bisphenols (ƩBPs) in dust samples ranged from <1 to 3600 and from 13 to 110,000 ng/g, respectively. The highest TBBPA concentrations in house dust were found in samples from Japan (median: 140 ng/g), followed by South Korea (84 ng/g) and China (23 ng/g). The highest ∑BPs concentrations were found in Greece (median: 3900 ng/g), Japan (2600 ng/g) and the U.S. (2200 ng/g). Significant variations in BPA concentrations were found in dust samples collected from various microenvironments in offices and homes. Concentrations of TBBPA in house dust were significantly correlated with BPA and ∑BPs. Among the nine target chemicals analyzed, BPA was the predominant compound in dust from all countries. The proportion of TBBPA in sum concentrations of nine phenolic compounds analyzed in this study was the highest in dust samples from China (27%) and the lowest in Greece (0.41%). The median estimated daily intake (EDI) of ∑BPs through dust ingestion was the highest in Greece (1.6-17 ng/kg bw/day), Japan (1.3-16) and the U.S. (0.89-9.6) for various age groups. Nevertheless, in comparison with the reported BPA exposure doses through diet, dust ingestion accounted for less than 10% of the total exposure doses in China and the U.S. For TBBPA, the EDI for infants and toddlers ranged from 0.01 to 3.4 ng/kg bw/day, and dust ingestion is an important pathway for exposure accounting for 3.8-35% (median) of exposure doses in China.Tetrabromobisphenol A (TBBPA) and eight bisphenol analogues (BPs) including bisphenol A (BPA) were determined in 388 indoor (including homes and microenvironments) dust samples collected from 12 countries (China, Colombia, Greece, India, Japan, Kuwait, Pakistan, Romania, Saudi Arabia, South Korea, U.S., and Vietnam). The concentrations of TBBPA and sum of eight bisphenols (ƩBPs) in dust samples ranged from <1 to 3600 and from 13 to 110,000 ng/g, respectively. The highest TBBPA concentrations in house dust were found in samples from Japan (median: 140 ng/g), followed by South Korea (84 ng/g) and China (23 ng/g). The highest ∑BPs concentrations were found in Greece (median: 3900 ng/g), Japan (2600 ng/g) and the U.S. (2200 ng/g). Significant variations in BPA concentrations were found in dust samples collected from various microenvironments in offices and homes. Concentrations of TBBPA in house dust were significantly correlated with BPA and ∑BPs. Among the nine target chemicals analyzed, BPA was the predominant compound in dust from all countries. The proportion of TBBPA in sum concentrations of nine phenolic compounds analyzed in this study was the highest in dust samples from China (27%) and the lowest in Greece (0.41%). The median estimated daily intake (EDI) of ∑BPs through dust ingestion was the highest in Greece (1.6-17 ng/kg bw/day), Japan (1.3-16) and the U.S. (0.89-9.6) for various age groups. Nevertheless, in comparison with the reported BPA exposure doses through diet, dust ingestion accounted for less than 10% of the total exposure doses in China and the U.S. For TBBPA, the EDI for infants and toddlers ranged from 0.01 to 3.4 ng/kg bw/day, and dust ingestion is an important pathway for exposure accounting for 3.8-35% (median) of exposure doses in China. Tetrabromobisphenol A (TBBPA) and eight bisphenol analogues (BPs) including bisphenol A (BPA) were determined in 388 indoor (including homes and microenvironments) dust samples collected from 12 countries (China, Colombia, Greece, India, Japan, Kuwait, Pakistan, Romania, Saudi Arabia, South Korea, U.S., and Vietnam). The concentrations of TBBPA and sum of eight bisphenols (ƩBPs) in dust samples ranged from <1 to 3600 and from 13 to 110,000 ng/g, respectively. The highest TBBPA concentrations in house dust were found in samples from Japan (median: 140 ng/g), followed by South Korea (84 ng/g) and China (23 ng/g). The highest ∑BPs concentrations were found in Greece (median: 3900 ng/g), Japan (2600 ng/g) and the U.S. (2200 ng/g). Significant variations in BPA concentrations were found in dust samples collected from various microenvironments in offices and homes. Concentrations of TBBPA in house dust were significantly correlated with BPA and ∑BPs. Among the nine target chemicals analyzed, BPA was the predominant compound in dust from all countries. The proportion of TBBPA in sum concentrations of nine phenolic compounds analyzed in this study was the highest in dust samples from China (27%) and the lowest in Greece (0.41%). The median estimated daily intake (EDI) of ∑BPs through dust ingestion was the highest in Greece (1.6-17 ng/kg bw/day), Japan (1.3-16) and the U.S. (0.89-9.6) for various age groups. Nevertheless, in comparison with the reported BPA exposure doses through diet, dust ingestion accounted for less than 10% of the total exposure doses in China and the U.S. For TBBPA, the EDI for infants and toddlers ranged from 0.01 to 3.4 ng/kg bw/day, and dust ingestion is an important pathway for exposure accounting for 3.8-35% (median) of exposure doses in China. |
| Author | Gevao, Bondi Covaci, Adrian Wang, Wei Minh, Tu Binh Malarvannan, Govindan Kumosani, Taha A. Moon, Hyo-Bang Nakata, Haruhiko Johnson-Restrepo, Boris Abualnaja, Khalid O. Asimakopoulos, Alexandros G. Sinha, Ravindra K. Kannan, Kurunthachalam |
| Author_xml | – sequence: 1 givenname: Wei surname: Wang fullname: Wang, Wei organization: Wadsworth Center, New York State Department of Health, Department of Environmental Health Sciences, School of Public Health, State University of New York at Albany, Empire State Plaza, P.O. Box 509, Albany, NY 12201-0509, United States – sequence: 2 givenname: Khalid O. surname: Abualnaja fullname: Abualnaja, Khalid O. organization: Biochemistry Department, Faculty of Science, Experimental Biochemistry Unit, King Fahd Medical Research Center, Bioactive Natural Products Research Group, King Abdulaziz University, Jeddah, Saudi Arabia – sequence: 3 givenname: Alexandros G. surname: Asimakopoulos fullname: Asimakopoulos, Alexandros G. organization: Wadsworth Center, New York State Department of Health, Department of Environmental Health Sciences, School of Public Health, State University of New York at Albany, Empire State Plaza, P.O. Box 509, Albany, NY 12201-0509, United States – sequence: 4 givenname: Adrian surname: Covaci fullname: Covaci, Adrian organization: Toxicological Center, University of Antwerp, Universiteitsplein 1, 2610 Wilrijk-Antwerp, Belgium – sequence: 5 givenname: Bondi surname: Gevao fullname: Gevao, Bondi organization: Environmental Management Program, Environment and Life Sciences Center, Kuwait Institute for Scientific Research, P.O. Box 24885, Safat, 13109, Kuwait – sequence: 6 givenname: Boris surname: Johnson-Restrepo fullname: Johnson-Restrepo, Boris organization: Environmental and Chemistry Group, Sede San Pablo, University of Cartagena, Cartagena, Bolívar 130015, Colombia – sequence: 7 givenname: Taha A. surname: Kumosani fullname: Kumosani, Taha A. organization: Biochemistry Department, Faculty of Science, Experimental Biochemistry Unit, King Fahd Medical Research Center, Bioactive Natural Products Research Group, King Abdulaziz University, Jeddah, Saudi Arabia – sequence: 8 givenname: Govindan surname: Malarvannan fullname: Malarvannan, Govindan organization: Toxicological Center, University of Antwerp, Universiteitsplein 1, 2610 Wilrijk-Antwerp, Belgium – sequence: 9 givenname: Tu Binh surname: Minh fullname: Minh, Tu Binh organization: Faculty of Chemistry, Hanoi University of Science, Vietnam National University, Hanoi, 19 Le Thanh Tong, Hoan Kiem, Hanoi, Viet Nam – sequence: 10 givenname: Hyo-Bang surname: Moon fullname: Moon, Hyo-Bang organization: Department of Marine Sciences and Convergent Technology, College of Science and Technology, Hanyang University, Ansan, South Korea – sequence: 11 givenname: Haruhiko surname: Nakata fullname: Nakata, Haruhiko organization: Graduate School of Science and Technology, Kumamoto University, 2-39-1 Kurokami, Kumamoto 860-8555, Japan – sequence: 12 givenname: Ravindra K. surname: Sinha fullname: Sinha, Ravindra K. organization: Department of Zoology, Patna University, Patna 800 005, India – sequence: 13 givenname: Kurunthachalam surname: Kannan fullname: Kannan, Kurunthachalam email: Kurunthachalam.kannan@health.ny.gov organization: Wadsworth Center, New York State Department of Health, Department of Environmental Health Sciences, School of Public Health, State University of New York at Albany, Empire State Plaza, P.O. Box 509, Albany, NY 12201-0509, United States |
| BackLink | https://www.ncbi.nlm.nih.gov/pubmed/26177148$$D View this record in MEDLINE/PubMed |
| BookMark | eNqNks1uEzEUhS1URNPCGyDkJZsJ_onHMyyQoooCUiU2sLZsz3XiaMYOtieFd-Fh6yilQixoF9a9sr9zdOVzL9BZiAEQek3JkhLavtstIRx8KEtGqFiSdlnLM7SgneRNKwU5Q4uKkWZFGTlHFznvCCFs1YkX6Jy1VEq66hbo9xrbOO110sUfAOucIecJQsHR4e086YDh5z7mOQEuERcoSZsUp2h83m8hxBGvsQ4DBr_ZFvxwm7EPdpwHHzb4b_TgdX0ZYkx4mHOp_QZy8THUDpdbGOsQNs6hJA_5JXru9Jjh1X29RN-vP367-tzcfP305Wp901jBZGla1reiNUZL03MzSCmFcAMF5gbmgEFPDW8FlxaMJq7n2mnuhHWdEcRpZ_glenvy3af4Y67zqMlnC-OoA8Q5K1Z_jjMp-v5RlEpOSNuvCH0CSpk8nqe4EiE573pe0Tf36GwmGNQ--UmnX-pPpBVYnQCbYs4J3ANCiTpujtqp0-ao4-Yo0qpaquz9PzLriz4mUxP342PiDycx1JQOHpLK1kOwMPgEtqgh-v8b3AF7B-UF |
| CitedBy_id | crossref_primary_10_1080_10934529_2015_1128749 crossref_primary_10_1016_j_chemosphere_2020_126422 crossref_primary_10_1016_j_ecoenv_2019_02_002 crossref_primary_10_1016_j_envpol_2018_10_115 crossref_primary_10_1016_j_envint_2020_106078 crossref_primary_10_1016_j_envint_2022_107722 crossref_primary_10_1016_j_envpol_2018_12_084 crossref_primary_10_1016_j_chemosphere_2023_140451 crossref_primary_10_1007_s00216_021_03863_x crossref_primary_10_1016_j_scitotenv_2019_133834 crossref_primary_10_1039_D0AY01118E crossref_primary_10_1007_s10653_023_01620_w crossref_primary_10_1038_srep38000 crossref_primary_10_1007_s10163_018_0745_2 crossref_primary_10_1016_j_emcon_2020_12_001 crossref_primary_10_3390_ijms241713281 crossref_primary_10_1016_j_envpol_2020_115425 crossref_primary_10_1016_j_chemosphere_2022_137565 crossref_primary_10_1016_j_envpol_2022_119586 crossref_primary_10_1007_s00604_021_04779_0 crossref_primary_10_1016_j_emcon_2016_03_006 crossref_primary_10_1016_j_scitotenv_2019_05_264 crossref_primary_10_1021_acssuschemeng_6b01318 crossref_primary_10_1016_j_envint_2016_05_026 crossref_primary_10_1002_advs_201600493 crossref_primary_10_1007_s11356_015_6031_0 crossref_primary_10_1021_acs_est_4c03131 crossref_primary_10_1021_acsanm_8b02119 crossref_primary_10_1016_j_cbpc_2022_109527 crossref_primary_10_1007_s11356_024_34095_y crossref_primary_10_1016_j_envint_2018_09_043 crossref_primary_10_1007_s00604_020_4119_9 crossref_primary_10_1016_j_chemosphere_2017_08_038 crossref_primary_10_1016_j_chemosphere_2023_138270 crossref_primary_10_1016_j_envint_2024_109005 crossref_primary_10_3390_molecules28062505 crossref_primary_10_1016_j_aca_2015_12_034 crossref_primary_10_1016_j_emcon_2019_05_002 crossref_primary_10_3390_ijerph19084600 crossref_primary_10_1016_j_envpol_2022_120424 crossref_primary_10_1016_j_envres_2020_109499 crossref_primary_10_1007_s11356_021_13943_1 crossref_primary_10_1016_j_bios_2021_113106 crossref_primary_10_1021_acs_est_3c10132 crossref_primary_10_3390_molecules27154832 crossref_primary_10_1177_0748233720928165 crossref_primary_10_1021_acs_est_1c00195 crossref_primary_10_1021_acs_estlett_5c00204 crossref_primary_10_1016_j_taap_2015_09_012 crossref_primary_10_1016_j_tox_2018_10_002 crossref_primary_10_1371_journal_pone_0157622 crossref_primary_10_1016_j_envpol_2016_06_021 crossref_primary_10_1021_envhealth_3c00202 crossref_primary_10_1364_JOSAB_35_0000C8 crossref_primary_10_1016_j_crtox_2022_100079 crossref_primary_10_1007_s11356_024_32455_2 crossref_primary_10_1021_acs_est_8b03129 crossref_primary_10_1080_10807039_2022_2101429 crossref_primary_10_1016_j_scitotenv_2017_11_049 crossref_primary_10_1021_acs_est_0c07587 crossref_primary_10_1016_j_envint_2016_04_013 crossref_primary_10_1002_jssc_202300006 crossref_primary_10_1016_j_wasman_2017_07_033 crossref_primary_10_1016_j_envint_2017_12_014 crossref_primary_10_3390_suschem2020020 crossref_primary_10_1016_j_molstruc_2017_01_055 crossref_primary_10_1016_j_scitotenv_2019_136100 crossref_primary_10_1016_j_envpol_2022_120012 crossref_primary_10_1016_j_cub_2018_06_070 crossref_primary_10_1016_j_scitotenv_2023_162374 crossref_primary_10_1016_j_ecoenv_2019_01_114 crossref_primary_10_3390_ijerph182111055 crossref_primary_10_1016_j_envint_2017_02_006 crossref_primary_10_3390_ijms21103529 crossref_primary_10_2139_ssrn_3995258 crossref_primary_10_1021_acs_est_9b01749 crossref_primary_10_1021_acs_est_6b05718 crossref_primary_10_1002_tox_23657 crossref_primary_10_1021_acs_est_3c00836 crossref_primary_10_1016_j_chemosphere_2018_07_125 crossref_primary_10_1016_j_envint_2019_104921 crossref_primary_10_1016_j_envpol_2018_03_015 crossref_primary_10_1016_j_envpol_2021_117475 crossref_primary_10_1016_j_ecoenv_2019_01_126 crossref_primary_10_1016_j_scitotenv_2022_160089 crossref_primary_10_1016_j_ecoenv_2025_118045 crossref_primary_10_3390_toxics9020034 crossref_primary_10_1016_j_scitotenv_2024_170833 crossref_primary_10_1007_s10661_023_11977_1 crossref_primary_10_1007_s42770_023_00950_2 crossref_primary_10_1021_acs_est_1c04621 crossref_primary_10_1021_acs_est_6b02771 crossref_primary_10_1016_j_scitotenv_2022_154444 crossref_primary_10_1016_j_fct_2021_112671 crossref_primary_10_1289_EHP6641 crossref_primary_10_1016_j_envres_2020_110172 crossref_primary_10_1016_j_chemosphere_2020_129273 crossref_primary_10_3390_molecules26216515 crossref_primary_10_1016_j_envpol_2018_07_115 crossref_primary_10_3390_ijms22179443 crossref_primary_10_1016_j_ecoenv_2019_109904 crossref_primary_10_1007_s00204_022_03259_5 crossref_primary_10_1007_s11356_022_22895_z crossref_primary_10_1021_acssuschemeng_0c09276 crossref_primary_10_1016_j_jclepro_2020_124668 crossref_primary_10_1016_j_scitotenv_2021_150210 crossref_primary_10_1016_j_envint_2019_105314 crossref_primary_10_1016_j_scitotenv_2021_148013 crossref_primary_10_1038_s41598_017_00570_5 crossref_primary_10_1016_j_snb_2016_05_153 crossref_primary_10_3390_app11041837 crossref_primary_10_3390_ijerph17113813 crossref_primary_10_1016_j_scitotenv_2017_09_194 crossref_primary_10_1515_reveh_2021_0036 crossref_primary_10_1016_j_ecoenv_2022_113397 crossref_primary_10_1021_acs_est_5b05387 crossref_primary_10_1016_j_chemosphere_2022_134088 crossref_primary_10_1021_acs_chemrestox_9b00528 crossref_primary_10_3390_toxics12070448 crossref_primary_10_1016_j_envpol_2024_125186 crossref_primary_10_1016_j_isci_2018_04_014 crossref_primary_10_1021_acs_est_7b00701 crossref_primary_10_1039_D1EW00545F crossref_primary_10_1016_j_chemosphere_2016_01_023 crossref_primary_10_1016_j_ijheh_2015_08_004 crossref_primary_10_1016_j_jhazmat_2025_137934 crossref_primary_10_1007_s11356_023_25497_5 crossref_primary_10_1016_j_chemosphere_2020_126816 crossref_primary_10_1039_c9tx00055k crossref_primary_10_1016_j_envint_2018_11_005 crossref_primary_10_1016_j_brainresbull_2020_01_015 crossref_primary_10_1007_s11356_022_22890_4 crossref_primary_10_1016_j_envpol_2018_06_087 crossref_primary_10_1016_j_scitotenv_2021_148796 crossref_primary_10_1016_j_envpol_2017_12_093 crossref_primary_10_1021_acsomega_8b00824 crossref_primary_10_3390_toxics11121000 crossref_primary_10_4491_eer_2018_005 crossref_primary_10_1016_j_envpol_2019_07_067 crossref_primary_10_1021_acs_est_8b04154 crossref_primary_10_1016_j_chemosphere_2018_04_105 crossref_primary_10_1530_ERC_16_0175 crossref_primary_10_1016_j_emcon_2017_11_001 crossref_primary_10_1016_j_scitotenv_2018_11_403 crossref_primary_10_1016_j_scitotenv_2019_02_449 crossref_primary_10_1021_acs_est_9b02090 crossref_primary_10_1016_j_scitotenv_2023_168012 crossref_primary_10_1038_s41598_023_36441_5 crossref_primary_10_1021_acs_est_6b00032 crossref_primary_10_1016_j_envint_2021_106893 crossref_primary_10_3390_toxics9070146 crossref_primary_10_1016_j_chemosphere_2019_01_095 crossref_primary_10_1007_s00204_023_03659_1 crossref_primary_10_1002_rcm_7633 crossref_primary_10_1016_j_chemosphere_2021_130232 crossref_primary_10_1016_j_carbpol_2020_116731 crossref_primary_10_1016_j_fct_2017_05_053 crossref_primary_10_1080_10643389_2019_1681051 crossref_primary_10_1016_j_chemosphere_2018_05_032 crossref_primary_10_1007_s11356_021_14496_z crossref_primary_10_1016_j_chemosphere_2017_11_125 crossref_primary_10_1016_j_envpol_2020_114879 crossref_primary_10_1016_j_scitotenv_2016_06_062 crossref_primary_10_1016_j_envint_2021_106547 crossref_primary_10_1016_j_scitotenv_2018_10_271 crossref_primary_10_1080_10807039_2018_1435255 crossref_primary_10_1016_j_jenvman_2022_116601 crossref_primary_10_1016_j_chemosphere_2022_137037 crossref_primary_10_1016_j_fct_2018_02_021 crossref_primary_10_1016_j_scitotenv_2017_03_200 crossref_primary_10_1093_toxsci_kfz059 crossref_primary_10_1016_j_scitotenv_2020_140856 crossref_primary_10_1016_j_watres_2019_06_046 crossref_primary_10_1039_C6AY00774K crossref_primary_10_1007_s12649_023_02316_z crossref_primary_10_1016_j_envint_2024_108690 crossref_primary_10_1007_s00244_019_00663_4 crossref_primary_10_1016_j_chemosphere_2017_05_070 crossref_primary_10_1016_j_chemosphere_2021_132218 crossref_primary_10_1016_j_envint_2019_105178 crossref_primary_10_1016_j_envint_2021_106840 crossref_primary_10_1021_acs_est_7b02114 crossref_primary_10_1016_j_microc_2019_104392 crossref_primary_10_1016_j_talanta_2020_120713 crossref_primary_10_1016_j_ecoenv_2017_09_048 crossref_primary_10_1289_EHP1329 crossref_primary_10_1016_j_chemosphere_2016_02_038 crossref_primary_10_1039_D4VA00132J crossref_primary_10_1016_j_marenvres_2022_105839 crossref_primary_10_1038_s41370_022_00425_w crossref_primary_10_3390_environments12020040 crossref_primary_10_1016_j_envint_2024_109091 crossref_primary_10_1002_jat_3947 crossref_primary_10_1021_acs_est_0c04494 crossref_primary_10_1016_j_ecoenv_2018_11_101 crossref_primary_10_1016_j_envres_2021_112594 crossref_primary_10_1016_j_envint_2021_106848 crossref_primary_10_3390_ma16196500 crossref_primary_10_1016_j_envint_2017_08_011 crossref_primary_10_1016_j_chemosphere_2022_133701 crossref_primary_10_1016_j_chemosphere_2020_126715 crossref_primary_10_1016_j_chemosphere_2018_02_040 crossref_primary_10_1016_j_envres_2019_109012 crossref_primary_10_1016_j_emcon_2020_08_003 crossref_primary_10_1016_j_envpol_2024_123393 crossref_primary_10_1016_j_chemosphere_2024_143798 crossref_primary_10_1016_j_chemosphere_2016_08_062 crossref_primary_10_1016_j_chemosphere_2021_130016 crossref_primary_10_1016_j_chemosphere_2020_125987 crossref_primary_10_1016_j_envint_2019_105397 crossref_primary_10_1016_j_envres_2019_108726 crossref_primary_10_1016_j_envres_2023_117172 crossref_primary_10_1016_j_chemosphere_2024_143790 crossref_primary_10_1021_acs_est_0c02188 crossref_primary_10_1016_j_chemosphere_2023_137935 crossref_primary_10_1016_j_scitotenv_2023_166307 crossref_primary_10_1016_j_etap_2016_10_018 crossref_primary_10_1016_j_envres_2021_112366 crossref_primary_10_1016_j_scitotenv_2022_157774 crossref_primary_10_1016_j_chroma_2022_463489 crossref_primary_10_1016_j_ecoenv_2022_113430 crossref_primary_10_1016_j_chemosphere_2018_02_179 |
| Cites_doi | 10.1016/j.scitotenv.2013.04.059 10.1016/j.envint.2015.01.008 10.1177/0192623314557335 10.1016/S0300-483X(02)00442-0 10.1016/j.atmosenv.2013.03.007 10.1021/es2002106 10.1080/19440049.2013.868611 10.1021/es8035626 10.1016/j.scitotenv.2013.04.003 10.1016/j.envpol.2012.04.009 10.1007/s00244-010-9634-y 10.1021/es303879n 10.1016/j.chemosphere.2005.11.055 10.1016/j.jhazmat.2013.04.039 10.1016/j.chemosphere.2014.03.114 10.1021/es302004w 10.1016/j.chemosphere.2009.02.068 10.1016/j.fct.2012.07.059 10.1016/S0006-291X(02)00262-0 10.1016/j.chroma.2008.08.035 10.1016/j.chemosphere.2014.09.011 10.1016/j.mce.2005.01.013 10.1016/j.chemosphere.2009.05.024 10.1016/j.atmosenv.2011.02.019 10.1038/jes.2011.11 10.1021/es8029957 10.1021/es301334j 10.1016/j.atmosenv.2013.04.071 10.1016/j.chemosphere.2006.05.136 10.1016/S0197-0186(03)00044-5 10.1038/jes.2010.9 10.1021/jf400445n 10.1016/j.envpol.2013.11.023 10.1021/es300876n 10.1016/j.tox.2007.12.009 10.2174/1385272819666140804230205 10.1016/j.jchromb.2013.11.009 10.1038/sj.jea.7500165 10.1021/es801110a 10.1016/j.chemosphere.2009.03.006 |
| ContentType | Journal Article |
| Copyright | 2015 Elsevier Ltd Copyright © 2015 Elsevier Ltd. All rights reserved. |
| Copyright_xml | – notice: 2015 Elsevier Ltd – notice: Copyright © 2015 Elsevier Ltd. All rights reserved. |
| DBID | AAYXX CITATION CGR CUY CVF ECM EIF NPM 7X8 7ST 7U7 C1K SOI 7SU 8FD FR3 KR7 7S9 L.6 |
| DOI | 10.1016/j.envint.2015.06.015 |
| DatabaseName | CrossRef Medline MEDLINE MEDLINE (Ovid) MEDLINE MEDLINE PubMed MEDLINE - Academic Environment Abstracts Toxicology Abstracts Environmental Sciences and Pollution Management Environment Abstracts Environmental Engineering Abstracts Technology Research Database Engineering Research Database Civil Engineering Abstracts AGRICOLA AGRICOLA - Academic |
| DatabaseTitle | CrossRef MEDLINE Medline Complete MEDLINE with Full Text PubMed MEDLINE (Ovid) MEDLINE - Academic Toxicology Abstracts Environment Abstracts Environmental Sciences and Pollution Management Civil Engineering Abstracts Engineering Research Database Technology Research Database Environmental Engineering Abstracts AGRICOLA AGRICOLA - Academic |
| DatabaseTitleList | Toxicology Abstracts AGRICOLA MEDLINE - Academic MEDLINE Civil Engineering Abstracts |
| Database_xml | – sequence: 1 dbid: NPM name: PubMed url: https://proxy.k.utb.cz/login?url=http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed sourceTypes: Index Database – sequence: 2 dbid: EIF name: MEDLINE url: https://proxy.k.utb.cz/login?url=https://www.webofscience.com/wos/medline/basic-search sourceTypes: Index Database |
| DeliveryMethod | fulltext_linktorsrc |
| Discipline | Engineering Public Health Environmental Sciences |
| EISSN | 1873-6750 |
| EndPage | 191 |
| ExternalDocumentID | 26177148 10_1016_j_envint_2015_06_015 S0160412015300039 |
| Genre | Research Support, U.S. Gov't, P.H.S Journal Article Comparative Study |
| GeographicLocations | Saudi Arabia Colombia Korea, Rep Pakistan Romania MED, Greece China, People's Rep ISEW, Vietnam Kuwait INW, Japan India Greece South Korea Vietnam United States China Japan |
| GeographicLocations_xml | – name: MED, Greece – name: Saudi Arabia – name: Korea, Rep – name: Romania – name: Colombia – name: Pakistan – name: China, People's Rep – name: India – name: Kuwait – name: INW, Japan – name: ISEW, Vietnam – name: Vietnam – name: South Korea – name: Japan – name: China – name: United States – name: Greece |
| GrantInformation_xml | – fundername: NCEH CDC HHS grantid: 1U38EH000464-01 |
| GroupedDBID | --- --K --M .~1 0R~ 0SF 1B1 1RT 1~. 1~5 29G 4.4 457 4G. 53G 5GY 5VS 7-5 71M 8P~ 9JM AABNK AACTN AAEDT AAEDW AAFWJ AAIAV AAIKJ AAKOC AALRI AAOAW AAQFI AAQXK AAXUO ABEFU ABFNM ABFYP ABJNI ABLST ABMAC ABXDB ABYKQ ACDAQ ACGFS ACRLP ADEZE ADMUD AEBSH AEKER AENEX AFKWA AFPKN AFTJW AFXIZ AGHFR AGUBO AGYEJ AHEUO AHHHB AIEXJ AIKHN AITUG AJBFU AJOXV AKIFW ALMA_UNASSIGNED_HOLDINGS AMFUW AMRAJ ASPBG AVWKF AXJTR AZFZN BKOJK BLECG BLXMC CS3 DU5 EBS EFJIC EFLBG EJD EO8 EO9 EP2 EP3 F5P FDB FEDTE FGOYB FIRID FNPLU FYGXN G-2 G-Q GBLVA GROUPED_DOAJ HMC HVGLF HZ~ IHE J1W K-O KCYFY KOM LY9 M41 MO0 N9A NCXOZ O-L O9- OAUVE OK1 OZT P-8 P-9 P2P PC. Q38 R2- RIG RNS ROL RPZ SCC SDF SDG SDP SEN SES SEW SSJ SSZ T5K TN5 WUQ XPP ~02 ~G- AAHBH AATTM AAXKI AAYWO AAYXX ABWVN ACRPL ACVFH ADCNI ADNMO ADVLN AEGFY AEIPS AEUPX AFJKZ AFPUW AGCQF AGQPQ AGRNS AIGII AIIUN AKBMS AKRWK AKYEP ANKPU APXCP BNPGV CITATION SSH CGR CUY CVF ECM EIF NPM 7X8 EFKBS 7ST 7U7 C1K SOI 7SU 8FD FR3 KR7 7S9 L.6 |
| ID | FETCH-LOGICAL-c527t-629656bba7b93bd77755fd1e2fd2fe2e91b36537ceba0f93afa3f5cf8b50fafb3 |
| IEDL.DBID | .~1 |
| ISSN | 0160-4120 1873-6750 |
| IngestDate | Fri Jul 11 04:07:12 EDT 2025 Mon Jul 21 11:14:47 EDT 2025 Fri Jul 11 00:03:38 EDT 2025 Tue Aug 05 10:20:01 EDT 2025 Wed Feb 19 01:59:07 EST 2025 Thu Apr 24 23:02:41 EDT 2025 Tue Jul 01 01:23:08 EDT 2025 Fri Feb 23 02:31:09 EST 2024 |
| IsPeerReviewed | true |
| IsScholarly | true |
| Keywords | BPA TBBPA Microenvironment Indoor dust Human exposure |
| Language | English |
| License | Copyright © 2015 Elsevier Ltd. All rights reserved. |
| LinkModel | DirectLink |
| MergedId | FETCHMERGED-LOGICAL-c527t-629656bba7b93bd77755fd1e2fd2fe2e91b36537ceba0f93afa3f5cf8b50fafb3 |
| Notes | ObjectType-Article-2 SourceType-Scholarly Journals-1 ObjectType-Feature-1 content type line 23 ObjectType-Article-1 ObjectType-Feature-2 |
| PMID | 26177148 |
| PQID | 1705733893 |
| PQPubID | 23479 |
| PageCount | 9 |
| ParticipantIDs | proquest_miscellaneous_2000327599 proquest_miscellaneous_1730069401 proquest_miscellaneous_1712771279 proquest_miscellaneous_1705733893 pubmed_primary_26177148 crossref_primary_10_1016_j_envint_2015_06_015 crossref_citationtrail_10_1016_j_envint_2015_06_015 elsevier_sciencedirect_doi_10_1016_j_envint_2015_06_015 |
| ProviderPackageCode | CITATION AAYXX |
| PublicationCentury | 2000 |
| PublicationDate | 2015-10-01 |
| PublicationDateYYYYMMDD | 2015-10-01 |
| PublicationDate_xml | – month: 10 year: 2015 text: 2015-10-01 day: 01 |
| PublicationDecade | 2010 |
| PublicationPlace | Netherlands |
| PublicationPlace_xml | – name: Netherlands |
| PublicationTitle | Environment international |
| PublicationTitleAlternate | Environ Int |
| PublicationYear | 2015 |
| Publisher | Elsevier Ltd |
| Publisher_xml | – name: Elsevier Ltd |
| References | US EPA (bb0205) 2008 Zhou, Kramer, Calafat, Ye (bb0245) 2014; 944 Wang, Wu, Huang, Kang, Cheung, Wong (bb0235) 2013; 261 Lorber, Schecter, Paepke, Shropshire, Christensen, Birnbaum (bb0145) 2015; 77 Takigami, Suzuki, Hirai, Sakai (bb0190) 2009; 76 Kitamura, Jinno, Ohta, Kuroki, Fujimoto (bb0095) 2002; 293 Liao, Liu, Alomirah, Loi, Mohd, Moon, Nakata, Kannan (bb0130) 2012; 46 Wang, Huang, Zheng, Cheung, Wong (bb0230) 2013; 463–464 Klepeis, Nelson, Ott, Robinson, Tsang, Switzer, Behar, Hern, Engelmann (bb0100) 2001; 11 Strack, Detzel, Wahl, Kuch, Krug (bb0180) 2007; 67 Suzuki, Nose, Takigami, Takahashi, Sakai (bb0185) 2006; 68 Johnson-Restrepo, Kannan (bb0085) 2009; 76 Geens, Aerts, Berthot, Bourguignon, Goeyens, Lecomte, Maghuin-Rogister, Pironnet, Pussemier, Scippo, Loco, Covaci (bb0050) 2012; 50 Mariussen, Fonnuma (bb0155) 2003; 43 Guo, Kannan (bb0080) 2011; 45 Lakind, Naiman (bb0105) 2011; 21 Ghisari, Bonefeld-Jorgensen (bb0065) 2005; 244 Wang, Huang, Wu, Kang, Wang, Cheung, Wong (bb0225) 2013; 77 Liao, Liu, Kannan (bb0135) 2012; 46 Batterman, Chernyak, Jia, Godwin, Charles (bb0010) 2009; 43 Gevao, Al-Bahloul, Al-Ghadban, Al-Omair, Ali, Zafar, Helaleh (bb0060) 2006; 64 Liao, Liu, Guo, Moon, Nakata, Wu, Kannan (bb0125) 2012; 46 Van der Ven, Van de Kuil, Verhoef, Verwer, Lilienthal, Leonards (bb0215) 2008; 245 Lee, Liao, Song, Ra, Kannan, Moon (bb0110) 2015; 119 Besis, Samara (bb0015) 2012; 169 Covaci, Voorspoels, Abdallah, Geens, Harrad, Law (bb0020) 2009; 1216 Pullen, Boecker, Tiegs (bb0165) 2003; 184 The European Commission (bb0195) 2011 Dodson, Perovich, Covaci, Van den Eede, Ionas, Dirtu, Brody, Rudel (bb0025) 2012; 46 Loganathan, Kannan (bb0140) 2011; 61 US EPA (bb0210) 2011 ECB (bb0035) 2006 Government of Canada (bb0070) 2010; Vol. 144, No. 7 Ni, Zeng (bb0160) 2013; 458–460 Wang, Huang, Chan, Cheung, Wong (bb0220) 2013; 73 Grasselli, Cortese, Fabbri, Smerilli, Vergani, Voci, Gallo, Canesi (bb0075) 2014; 112 Liao, Kannan (bb0115) 2013; 61 Whitehead, Metayer, Buffler, Rappaport (bb0240) 2011; 21 European Union (bb0040) 2006 Song, Song, Zeng, Wang, Liu, Ruan, Jiang (bb0175) 2014; 186 Liao, Kannan (bb0120) 2014; 31 Dunnick, Sanders, Kissling, Johnson, Boyle, Elmore (bb0030) 2015; 43 Geens, Roosens, Neels, Covaci (bb0055) 2009; 76 Ma, Subedi, Kannan (bb0150) 2014; 18 Shi, Wu, Li, Zhao, Feng (bb0170) 2009; 43 Abdallah, Harrad, Covaci (bb0005) 2008; 42 US EPA (bb0200) 2002 FDA (bb0045) 2012 Kang, Wang, Cheung, Wong (bb0090) 2011; 45 Liao (10.1016/j.envint.2015.06.015_bb0115) 2013; 61 Liao (10.1016/j.envint.2015.06.015_bb0125) 2012; 46 Shi (10.1016/j.envint.2015.06.015_bb0170) 2009; 43 Wang (10.1016/j.envint.2015.06.015_bb0230) 2013; 463–464 Gevao (10.1016/j.envint.2015.06.015_bb0060) 2006; 64 Kang (10.1016/j.envint.2015.06.015_bb0090) 2011; 45 Lakind (10.1016/j.envint.2015.06.015_bb0105) 2011; 21 Guo (10.1016/j.envint.2015.06.015_bb0080) 2011; 45 Dodson (10.1016/j.envint.2015.06.015_bb0025) 2012; 46 US EPA (10.1016/j.envint.2015.06.015_bb0210) 2011 Strack (10.1016/j.envint.2015.06.015_bb0180) 2007; 67 ECB (10.1016/j.envint.2015.06.015_bb0035) 2006 Batterman (10.1016/j.envint.2015.06.015_bb0010) 2009; 43 Government of Canada (10.1016/j.envint.2015.06.015_bb0070) 2010; Vol. 144, No. 7 Lorber (10.1016/j.envint.2015.06.015_bb0145) 2015; 77 Loganathan (10.1016/j.envint.2015.06.015_bb0140) 2011; 61 Grasselli (10.1016/j.envint.2015.06.015_bb0075) 2014; 112 Wang (10.1016/j.envint.2015.06.015_bb0220) 2013; 73 Geens (10.1016/j.envint.2015.06.015_bb0050) 2012; 50 US EPA (10.1016/j.envint.2015.06.015_bb0205) 2008 Van der Ven (10.1016/j.envint.2015.06.015_bb0215) 2008; 245 European Union (10.1016/j.envint.2015.06.015_bb0040) 2006 Geens (10.1016/j.envint.2015.06.015_bb0055) 2009; 76 Wang (10.1016/j.envint.2015.06.015_bb0235) 2013; 261 Abdallah (10.1016/j.envint.2015.06.015_bb0005) 2008; 42 FDA (10.1016/j.envint.2015.06.015_bb0045) 2012 Zhou (10.1016/j.envint.2015.06.015_bb0245) 2014; 944 Kitamura (10.1016/j.envint.2015.06.015_bb0095) 2002; 293 Liao (10.1016/j.envint.2015.06.015_bb0135) 2012; 46 Whitehead (10.1016/j.envint.2015.06.015_bb0240) 2011; 21 Pullen (10.1016/j.envint.2015.06.015_bb0165) 2003; 184 Suzuki (10.1016/j.envint.2015.06.015_bb0185) 2006; 68 Besis (10.1016/j.envint.2015.06.015_bb0015) 2012; 169 Ghisari (10.1016/j.envint.2015.06.015_bb0065) 2005; 244 Takigami (10.1016/j.envint.2015.06.015_bb0190) 2009; 76 Johnson-Restrepo (10.1016/j.envint.2015.06.015_bb0085) 2009; 76 US EPA (10.1016/j.envint.2015.06.015_bb0200) 2002 Liao (10.1016/j.envint.2015.06.015_bb0130) 2012; 46 Mariussen (10.1016/j.envint.2015.06.015_bb0155) 2003; 43 Covaci (10.1016/j.envint.2015.06.015_bb0020) 2009; 1216 Ni (10.1016/j.envint.2015.06.015_bb0160) 2013; 458–460 Klepeis (10.1016/j.envint.2015.06.015_bb0100) 2001; 11 Wang (10.1016/j.envint.2015.06.015_bb0225) 2013; 77 Dunnick (10.1016/j.envint.2015.06.015_bb0030) 2015; 43 Ma (10.1016/j.envint.2015.06.015_bb0150) 2014; 18 Song (10.1016/j.envint.2015.06.015_bb0175) 2014; 186 Lee (10.1016/j.envint.2015.06.015_bb0110) 2015; 119 Liao (10.1016/j.envint.2015.06.015_bb0120) 2014; 31 The European Commission (10.1016/j.envint.2015.06.015_bb0195) 2011 |
| References_xml | – year: 2012 ident: bb0045 article-title: Bisphenol A (BPA): Use in Food Contact Application – volume: 68 start-page: 1843 year: 2006 end-page: 1846 ident: bb0185 article-title: PBDEs and PBDD/Fs in house and office dust from Japan publication-title: Organohalogen Compd. – volume: 76 start-page: 755 year: 2009 end-page: 760 ident: bb0055 article-title: Assessment of human exposure to bisphenol-A, triclosan and tetrabromobisphenol-A through indoor dust intake in Belgium publication-title: Chemosphere – volume: 169 start-page: 217 year: 2012 end-page: 229 ident: bb0015 article-title: Polybrominated diphenyl ethers (PBDEs) in the indoor and outdoor environments—a review on occurrence and human exposure publication-title: Environ. Pollut. – year: 2006 ident: bb0035 article-title: European union risk assessment report. 2,20,6,60-Tetrabromo-4,40-isopropylidenediphenol (tetrabromobisphenol-A or TBBP-A). Part II — human health publication-title: European Union Risk Assessment Report – volume: 45 start-page: 2386 year: 2011 end-page: 2393 ident: bb0090 article-title: Polybrominated diphenyl ethers (PBDEs) in indoor dust and human hair publication-title: Atmos. Environ. – volume: 46 start-page: 6860 year: 2012 end-page: 6866 ident: bb0130 article-title: Bisphenol S in urine from the United States and seven Asian countries: occurrence and human exposures publication-title: Environ. Sci. Technol. – volume: Vol. 144, No. 7 year: 2010 ident: bb0070 publication-title: Order Amending Schedule I to the Hazardous Products Act (bisphenol A), Part II – volume: 46 start-page: 9138 year: 2012 end-page: 9145 ident: bb0125 article-title: Occurrence of eight bisphenol analogues in indoor dust from the United States and several Asian countries: implications for human exposure publication-title: Environ. Sci. Technol. – volume: 11 start-page: 231 year: 2001 end-page: 252 ident: bb0100 article-title: The National Human Activity Pattern Survey (NHAPS): a resource for assessing exposure to environmental pollutants publication-title: J. Expo. Sci. Environ. Epidemiol. – volume: 119 start-page: 1000 year: 2015 end-page: 1006 ident: bb0110 article-title: Emission of bisphenol analogues including bisphenol A and bisphenol F from wastewater treatment plants in Korea publication-title: Chemosphere – volume: 77 start-page: 55 year: 2015 end-page: 62 ident: bb0145 article-title: Exposure assessment of adult intake of bisphenol A (BPA) with emphasis on canned food dietary exposures publication-title: Environ. Int. – volume: 73 start-page: 204 year: 2013 end-page: 213 ident: bb0220 article-title: Risk assessment of non-dietary exposure to polycyclic aromatic hydrocarbons (PAHs) via PM2.5, TSP and dust in home and the implications from human hair publication-title: Atmos. Environ. – volume: 31 start-page: 319 year: 2014 end-page: 329 ident: bb0120 article-title: A survey of bisphenol A and other bisphenol analogues in foodstuffs from nine cities in China publication-title: Food Addit. Contam., Part A – volume: 43 start-page: 533 year: 2003 end-page: 542 ident: bb0155 article-title: The effect of brominated flame retardants on neurotransmitter uptake into rat brain synaptosomes and vesicles publication-title: Neurochem. Int. – volume: 18 start-page: 2182 year: 2014 end-page: 2199 ident: bb0150 article-title: The occurrence of bisphenol A, phthalates, parabens and other environmental phenolic compounds in house dust: a review publication-title: Curr. Org. Chem. – volume: 186 start-page: 14 year: 2014 end-page: 19 ident: bb0175 article-title: Occurrence and profiles of bisphenol analogues in municipal sewage sludge in China publication-title: Environ. Pollut. – volume: 76 start-page: 542 year: 2009 end-page: 548 ident: bb0085 article-title: An assessment of sources and pathways of human exposure to polybrominated diphenyl ethers in the United States publication-title: Chemosphere – volume: 184 start-page: 11 year: 2003 end-page: 22 ident: bb0165 article-title: The flame retardants tetrabromobisphenol A and tetrabromobisphenol A-bisallylether suppress the induction of interleukin-2 receptor alpha chain (CD25) in murine splenocytes publication-title: Toxicology – volume: 67 start-page: 405 year: 2007 end-page: 411 ident: bb0180 article-title: Cytotoxicity of TBBPA and effects on proliferation, cell cycle and MAPK pathways in mammalian cells publication-title: Chemosphere – year: 2011 ident: bb0210 publication-title: Exposure Factors Handbook – volume: 112 start-page: 511 year: 2014 end-page: 518 ident: bb0075 article-title: Thyromimetic actions of tetrabromobisphenol A (TBBPA) in steatotic FaO rat hepatoma cells publication-title: Chemosphere – volume: 244 start-page: 31 year: 2005 end-page: 41 ident: bb0065 article-title: Impact of environmental chemicals on the thyroid hormone function in pituitary rat GH3 cells publication-title: Mol. Cell. Endocrinol. – volume: 61 start-page: 4655 year: 2013 end-page: 4662 ident: bb0115 article-title: Concentrations and profiles of bisphenol A and other bisphenol analogues in foodstuffs from the United States and their implications for human exposure publication-title: J. Agric. Food Chem. – volume: 245 start-page: 76 year: 2008 end-page: 89 ident: bb0215 article-title: Endocrine effects of tetrabromobisphenol-A (TBBPA) in Wistar rats as tested in a one-generation reproduction study and a subacute toxicity study publication-title: Toxicology – volume: 21 start-page: 272 year: 2011 end-page: 279 ident: bb0105 article-title: Daily intake of bisphenol A and potential sources of exposure: 2005–2006 National Health and Nutrition Examination Survey publication-title: J. Expo. Sci. Environ. Epidemiol. – volume: 293 start-page: 554 year: 2002 end-page: 559 ident: bb0095 article-title: Thyroid hormonal activity of the flame retardants tetrabromobisphenol A and tetrachlorobisphenol A publication-title: Biochem. Biophys. Res. Commun. – volume: 458–460 start-page: 15 year: 2013 end-page: 19 ident: bb0160 article-title: HBCD and TBBPA in particulate phase of indoor air in Shenzhen, China publication-title: Sci. Total Environ. – volume: 46 start-page: 6515 year: 2012 end-page: 6522 ident: bb0135 article-title: Bisphenol S, a new bisphenol analogue, in paper products and currency bills and its association with bisphenol A residues publication-title: Environ. Sci. Technol. – volume: 76 start-page: 270 year: 2009 end-page: 277 ident: bb0190 article-title: Brominated flame retardants and other polyhalogenated compounds in indoor air and dust from two houses in Japan publication-title: Chemosphere – volume: 45 start-page: 3788 year: 2011 end-page: 3794 ident: bb0080 article-title: Comparative assessment of human exposure to phthalate esters from house dust in China and the United States publication-title: Environ. Sci. Technol. – volume: 261 start-page: 753 year: 2013 end-page: 762 ident: bb0235 article-title: Size fraction effect on phthalate esters accumulation, bioaccessibility and in vitro cytotoxicity of indoor/outdoor dust, and risk assessment of human exposure publication-title: J. Hazard. Mater. – volume: 43 start-page: 2693 year: 2009 end-page: 2700 ident: bb0010 article-title: Concentrations and emissions of polybrominated diphenyl ethers from U.S. Houses and Garages publication-title: Environ. Sci. Technol. – volume: 46 start-page: 13056 year: 2012 end-page: 13066 ident: bb0025 article-title: After the PBDE phase-out: a broad suite of flame retardants in repeat house dust samples from California publication-title: Environ. Sci. Technol. – year: 2011 ident: bb0195 article-title: Commission Directive 2011/8/EU of 28 January 2011 Amending Directive 2002/72/EC as Regards the Restriction of Use of Bisphenol A in Plastic Infant Feeding Bottles – volume: 944 start-page: 152 year: 2014 end-page: 156 ident: bb0245 article-title: Automated on-line column-switching high performance liquid chromatography isotope dilution tandem mass spectrometry method for the quantification of bisphenol A, bisphenol F, bisphenol S, and 11 other phenols in urine publication-title: J. Chromatogr. B – year: 2008 ident: bb0205 publication-title: Child-specific Exposure Factors Handbook, EPA/600/R-06/096 – volume: 77 start-page: 525 year: 2013 end-page: 533 ident: bb0225 article-title: Risk assessment of bioaccessible organochlorine pesticides exposure via indoor and outdoor dust publication-title: Atmos. Environ. – volume: 43 start-page: 464 year: 2015 end-page: 473 ident: bb0030 article-title: Environmental chemical exposure may contribute to uterine cancer development: studies with tetrabromobisphenol A publication-title: Toxicol. Pathol. – volume: 21 start-page: 549 year: 2011 end-page: 564 ident: bb0240 article-title: Estimating exposures to indoor contaminants using residential dust publication-title: J. Expo. Sci. Environ. Epidemiol. – volume: 50 start-page: 3725 year: 2012 end-page: 3740 ident: bb0050 article-title: A review of dietary and non-dietary exposure to bisphenol-A publication-title: Food Chem. Toxicol. – year: 2002 ident: bb0200 article-title: Child-Specific Exposure Factors Handbook, EPA-600-P-00-002B – volume: 61 start-page: 68 year: 2011 end-page: 73 ident: bb0140 article-title: Occurrence of bisphenol A in indoor dust from two locations in the eastern United States and implications for human exposures publication-title: Arch. Environ. Contam. Toxicol. – volume: 1216 start-page: 346 year: 2009 end-page: 363 ident: bb0020 article-title: Analytical and environmental aspects of the flame retardant tetrabromobisphenol-A and its derivatives publication-title: J. Chromatogr. A – year: 2006 ident: bb0040 article-title: Risk Assessment Report TBBP-A, Part II-Human Health – volume: 43 start-page: 4314 year: 2009 end-page: 4319 ident: bb0170 article-title: Dietary exposure assessment of Chinese adults and nursing infants to tetrabromobisphenol-a and hexabromocyclododecanes: occurrence measurements in foods and human milk publication-title: Environ. Sci. Technol. – volume: 463–464 start-page: 1201 year: 2013 end-page: 1209 ident: bb0230 article-title: Exposure assessment and distribution of polychlorinated biphenyls (PCBs) contained in indoor and outdoor dusts and the impacts of particle size and bioaccessibility publication-title: Sci. Total Environ. – volume: 64 start-page: 603 year: 2006 end-page: 608 ident: bb0060 article-title: House dust as a source of human exposure to polybrominated diphenyl ethers in Kuwait publication-title: Chemosphere – volume: 42 start-page: 6855 year: 2008 end-page: 6861 ident: bb0005 article-title: Hexabromocyclododecanes and tetrabromobisphenol-A in indoor air and dust in Birmingham, UK: implications for human exposure publication-title: Environ. Sci. Technol. – year: 2011 ident: 10.1016/j.envint.2015.06.015_bb0210 – volume: 463–464 start-page: 1201 year: 2013 ident: 10.1016/j.envint.2015.06.015_bb0230 article-title: Exposure assessment and distribution of polychlorinated biphenyls (PCBs) contained in indoor and outdoor dusts and the impacts of particle size and bioaccessibility publication-title: Sci. Total Environ. doi: 10.1016/j.scitotenv.2013.04.059 – year: 2006 ident: 10.1016/j.envint.2015.06.015_bb0040 – volume: 77 start-page: 55 year: 2015 ident: 10.1016/j.envint.2015.06.015_bb0145 article-title: Exposure assessment of adult intake of bisphenol A (BPA) with emphasis on canned food dietary exposures publication-title: Environ. Int. doi: 10.1016/j.envint.2015.01.008 – volume: 43 start-page: 464 year: 2015 ident: 10.1016/j.envint.2015.06.015_bb0030 article-title: Environmental chemical exposure may contribute to uterine cancer development: studies with tetrabromobisphenol A publication-title: Toxicol. Pathol. doi: 10.1177/0192623314557335 – volume: 184 start-page: 11 year: 2003 ident: 10.1016/j.envint.2015.06.015_bb0165 article-title: The flame retardants tetrabromobisphenol A and tetrabromobisphenol A-bisallylether suppress the induction of interleukin-2 receptor alpha chain (CD25) in murine splenocytes publication-title: Toxicology doi: 10.1016/S0300-483X(02)00442-0 – volume: 73 start-page: 204 year: 2013 ident: 10.1016/j.envint.2015.06.015_bb0220 article-title: Risk assessment of non-dietary exposure to polycyclic aromatic hydrocarbons (PAHs) via PM2.5, TSP and dust in home and the implications from human hair publication-title: Atmos. Environ. doi: 10.1016/j.atmosenv.2013.03.007 – volume: 45 start-page: 3788 year: 2011 ident: 10.1016/j.envint.2015.06.015_bb0080 article-title: Comparative assessment of human exposure to phthalate esters from house dust in China and the United States publication-title: Environ. Sci. Technol. doi: 10.1021/es2002106 – year: 2002 ident: 10.1016/j.envint.2015.06.015_bb0200 – year: 2008 ident: 10.1016/j.envint.2015.06.015_bb0205 – volume: 31 start-page: 319 year: 2014 ident: 10.1016/j.envint.2015.06.015_bb0120 article-title: A survey of bisphenol A and other bisphenol analogues in foodstuffs from nine cities in China publication-title: Food Addit. Contam., Part A doi: 10.1080/19440049.2013.868611 – volume: 43 start-page: 4314 year: 2009 ident: 10.1016/j.envint.2015.06.015_bb0170 article-title: Dietary exposure assessment of Chinese adults and nursing infants to tetrabromobisphenol-a and hexabromocyclododecanes: occurrence measurements in foods and human milk publication-title: Environ. Sci. Technol. doi: 10.1021/es8035626 – volume: Vol. 144, No. 7 year: 2010 ident: 10.1016/j.envint.2015.06.015_bb0070 – volume: 458–460 start-page: 15 year: 2013 ident: 10.1016/j.envint.2015.06.015_bb0160 article-title: HBCD and TBBPA in particulate phase of indoor air in Shenzhen, China publication-title: Sci. Total Environ. doi: 10.1016/j.scitotenv.2013.04.003 – volume: 169 start-page: 217 year: 2012 ident: 10.1016/j.envint.2015.06.015_bb0015 article-title: Polybrominated diphenyl ethers (PBDEs) in the indoor and outdoor environments—a review on occurrence and human exposure publication-title: Environ. Pollut. doi: 10.1016/j.envpol.2012.04.009 – volume: 61 start-page: 68 year: 2011 ident: 10.1016/j.envint.2015.06.015_bb0140 article-title: Occurrence of bisphenol A in indoor dust from two locations in the eastern United States and implications for human exposures publication-title: Arch. Environ. Contam. Toxicol. doi: 10.1007/s00244-010-9634-y – volume: 46 start-page: 13056 year: 2012 ident: 10.1016/j.envint.2015.06.015_bb0025 article-title: After the PBDE phase-out: a broad suite of flame retardants in repeat house dust samples from California publication-title: Environ. Sci. Technol. doi: 10.1021/es303879n – volume: 64 start-page: 603 year: 2006 ident: 10.1016/j.envint.2015.06.015_bb0060 article-title: House dust as a source of human exposure to polybrominated diphenyl ethers in Kuwait publication-title: Chemosphere doi: 10.1016/j.chemosphere.2005.11.055 – volume: 261 start-page: 753 year: 2013 ident: 10.1016/j.envint.2015.06.015_bb0235 article-title: Size fraction effect on phthalate esters accumulation, bioaccessibility and in vitro cytotoxicity of indoor/outdoor dust, and risk assessment of human exposure publication-title: J. Hazard. Mater. doi: 10.1016/j.jhazmat.2013.04.039 – volume: 112 start-page: 511 year: 2014 ident: 10.1016/j.envint.2015.06.015_bb0075 article-title: Thyromimetic actions of tetrabromobisphenol A (TBBPA) in steatotic FaO rat hepatoma cells publication-title: Chemosphere doi: 10.1016/j.chemosphere.2014.03.114 – volume: 46 start-page: 9138 year: 2012 ident: 10.1016/j.envint.2015.06.015_bb0125 article-title: Occurrence of eight bisphenol analogues in indoor dust from the United States and several Asian countries: implications for human exposure publication-title: Environ. Sci. Technol. doi: 10.1021/es302004w – volume: 76 start-page: 542 year: 2009 ident: 10.1016/j.envint.2015.06.015_bb0085 article-title: An assessment of sources and pathways of human exposure to polybrominated diphenyl ethers in the United States publication-title: Chemosphere doi: 10.1016/j.chemosphere.2009.02.068 – volume: 50 start-page: 3725 year: 2012 ident: 10.1016/j.envint.2015.06.015_bb0050 article-title: A review of dietary and non-dietary exposure to bisphenol-A publication-title: Food Chem. Toxicol. doi: 10.1016/j.fct.2012.07.059 – volume: 293 start-page: 554 year: 2002 ident: 10.1016/j.envint.2015.06.015_bb0095 article-title: Thyroid hormonal activity of the flame retardants tetrabromobisphenol A and tetrachlorobisphenol A publication-title: Biochem. Biophys. Res. Commun. doi: 10.1016/S0006-291X(02)00262-0 – volume: 1216 start-page: 346 year: 2009 ident: 10.1016/j.envint.2015.06.015_bb0020 article-title: Analytical and environmental aspects of the flame retardant tetrabromobisphenol-A and its derivatives publication-title: J. Chromatogr. A doi: 10.1016/j.chroma.2008.08.035 – volume: 119 start-page: 1000 year: 2015 ident: 10.1016/j.envint.2015.06.015_bb0110 article-title: Emission of bisphenol analogues including bisphenol A and bisphenol F from wastewater treatment plants in Korea publication-title: Chemosphere doi: 10.1016/j.chemosphere.2014.09.011 – year: 2011 ident: 10.1016/j.envint.2015.06.015_bb0195 – volume: 244 start-page: 31 year: 2005 ident: 10.1016/j.envint.2015.06.015_bb0065 article-title: Impact of environmental chemicals on the thyroid hormone function in pituitary rat GH3 cells publication-title: Mol. Cell. Endocrinol. doi: 10.1016/j.mce.2005.01.013 – volume: 76 start-page: 755 year: 2009 ident: 10.1016/j.envint.2015.06.015_bb0055 article-title: Assessment of human exposure to bisphenol-A, triclosan and tetrabromobisphenol-A through indoor dust intake in Belgium publication-title: Chemosphere doi: 10.1016/j.chemosphere.2009.05.024 – volume: 45 start-page: 2386 year: 2011 ident: 10.1016/j.envint.2015.06.015_bb0090 article-title: Polybrominated diphenyl ethers (PBDEs) in indoor dust and human hair publication-title: Atmos. Environ. doi: 10.1016/j.atmosenv.2011.02.019 – volume: 68 start-page: 1843 year: 2006 ident: 10.1016/j.envint.2015.06.015_bb0185 article-title: PBDEs and PBDD/Fs in house and office dust from Japan publication-title: Organohalogen Compd. – volume: 21 start-page: 549 year: 2011 ident: 10.1016/j.envint.2015.06.015_bb0240 article-title: Estimating exposures to indoor contaminants using residential dust publication-title: J. Expo. Sci. Environ. Epidemiol. doi: 10.1038/jes.2011.11 – volume: 43 start-page: 2693 year: 2009 ident: 10.1016/j.envint.2015.06.015_bb0010 article-title: Concentrations and emissions of polybrominated diphenyl ethers from U.S. Houses and Garages publication-title: Environ. Sci. Technol. doi: 10.1021/es8029957 – year: 2006 ident: 10.1016/j.envint.2015.06.015_bb0035 article-title: European union risk assessment report. 2,20,6,60-Tetrabromo-4,40-isopropylidenediphenol (tetrabromobisphenol-A or TBBP-A). Part II — human health – volume: 46 start-page: 6860 year: 2012 ident: 10.1016/j.envint.2015.06.015_bb0130 article-title: Bisphenol S in urine from the United States and seven Asian countries: occurrence and human exposures publication-title: Environ. Sci. Technol. doi: 10.1021/es301334j – volume: 77 start-page: 525 year: 2013 ident: 10.1016/j.envint.2015.06.015_bb0225 article-title: Risk assessment of bioaccessible organochlorine pesticides exposure via indoor and outdoor dust publication-title: Atmos. Environ. doi: 10.1016/j.atmosenv.2013.04.071 – volume: 67 start-page: 405 year: 2007 ident: 10.1016/j.envint.2015.06.015_bb0180 article-title: Cytotoxicity of TBBPA and effects on proliferation, cell cycle and MAPK pathways in mammalian cells publication-title: Chemosphere doi: 10.1016/j.chemosphere.2006.05.136 – volume: 43 start-page: 533 year: 2003 ident: 10.1016/j.envint.2015.06.015_bb0155 article-title: The effect of brominated flame retardants on neurotransmitter uptake into rat brain synaptosomes and vesicles publication-title: Neurochem. Int. doi: 10.1016/S0197-0186(03)00044-5 – volume: 21 start-page: 272 year: 2011 ident: 10.1016/j.envint.2015.06.015_bb0105 article-title: Daily intake of bisphenol A and potential sources of exposure: 2005–2006 National Health and Nutrition Examination Survey publication-title: J. Expo. Sci. Environ. Epidemiol. doi: 10.1038/jes.2010.9 – volume: 61 start-page: 4655 year: 2013 ident: 10.1016/j.envint.2015.06.015_bb0115 article-title: Concentrations and profiles of bisphenol A and other bisphenol analogues in foodstuffs from the United States and their implications for human exposure publication-title: J. Agric. Food Chem. doi: 10.1021/jf400445n – volume: 186 start-page: 14 year: 2014 ident: 10.1016/j.envint.2015.06.015_bb0175 article-title: Occurrence and profiles of bisphenol analogues in municipal sewage sludge in China publication-title: Environ. Pollut. doi: 10.1016/j.envpol.2013.11.023 – volume: 46 start-page: 6515 year: 2012 ident: 10.1016/j.envint.2015.06.015_bb0135 article-title: Bisphenol S, a new bisphenol analogue, in paper products and currency bills and its association with bisphenol A residues publication-title: Environ. Sci. Technol. doi: 10.1021/es300876n – volume: 245 start-page: 76 year: 2008 ident: 10.1016/j.envint.2015.06.015_bb0215 article-title: Endocrine effects of tetrabromobisphenol-A (TBBPA) in Wistar rats as tested in a one-generation reproduction study and a subacute toxicity study publication-title: Toxicology doi: 10.1016/j.tox.2007.12.009 – volume: 18 start-page: 2182 year: 2014 ident: 10.1016/j.envint.2015.06.015_bb0150 article-title: The occurrence of bisphenol A, phthalates, parabens and other environmental phenolic compounds in house dust: a review publication-title: Curr. Org. Chem. doi: 10.2174/1385272819666140804230205 – year: 2012 ident: 10.1016/j.envint.2015.06.015_bb0045 – volume: 944 start-page: 152 year: 2014 ident: 10.1016/j.envint.2015.06.015_bb0245 article-title: Automated on-line column-switching high performance liquid chromatography isotope dilution tandem mass spectrometry method for the quantification of bisphenol A, bisphenol F, bisphenol S, and 11 other phenols in urine publication-title: J. Chromatogr. B doi: 10.1016/j.jchromb.2013.11.009 – volume: 11 start-page: 231 year: 2001 ident: 10.1016/j.envint.2015.06.015_bb0100 article-title: The National Human Activity Pattern Survey (NHAPS): a resource for assessing exposure to environmental pollutants publication-title: J. Expo. Sci. Environ. Epidemiol. doi: 10.1038/sj.jea.7500165 – volume: 42 start-page: 6855 year: 2008 ident: 10.1016/j.envint.2015.06.015_bb0005 article-title: Hexabromocyclododecanes and tetrabromobisphenol-A in indoor air and dust in Birmingham, UK: implications for human exposure publication-title: Environ. Sci. Technol. doi: 10.1021/es801110a – volume: 76 start-page: 270 year: 2009 ident: 10.1016/j.envint.2015.06.015_bb0190 article-title: Brominated flame retardants and other polyhalogenated compounds in indoor air and dust from two houses in Japan publication-title: Chemosphere doi: 10.1016/j.chemosphere.2009.03.006 |
| SSID | ssj0002485 |
| Score | 2.5744967 |
| Snippet | Tetrabromobisphenol A (TBBPA) and eight bisphenol analogues (BPs) including bisphenol A (BPA) were determined in 388 indoor (including homes and... |
| SourceID | proquest pubmed crossref elsevier |
| SourceType | Aggregation Database Index Database Enrichment Source Publisher |
| StartPage | 183 |
| SubjectTerms | Adolescent Adult Aged Aged, 80 and over Air Pollutants - analysis Air Pollution, Indoor - analysis average daily intake Benzhydryl Compounds - analysis Bisphenol A Bisphenols BPA Child Child, Preschool China Colombia diet Dust Dust - analysis Dust control Environmental Exposure Environmental Monitoring Environmental Pollutants - analysis Exposure exposure pathways Greece Houses Human exposure Humans India Indoor dust Infant Infant, Newborn infants Ingestion Japan Kuwait Microenvironment Middle Aged Pakistan Phenols - analysis Polybrominated Biphenyls - analysis Romania Saudi Arabia South Korea TBBPA toddlers United States Vietnam Young Adult |
| Title | A comparative assessment of human exposure to tetrabromobisphenol A and eight bisphenols including bisphenol A via indoor dust ingestion in twelve countries |
| URI | https://dx.doi.org/10.1016/j.envint.2015.06.015 https://www.ncbi.nlm.nih.gov/pubmed/26177148 https://www.proquest.com/docview/1705733893 https://www.proquest.com/docview/1712771279 https://www.proquest.com/docview/1730069401 https://www.proquest.com/docview/2000327599 |
| Volume | 83 |
| hasFullText | 1 |
| inHoldings | 1 |
| isFullTextHit | |
| isPrint | |
| link | http://utb.summon.serialssolutions.com/2.0.0/link/0/eLvHCXMwnV1Na9wwEBUhubSUkm6bfocp9Oquba2s-LiEhG1Lc2kDuQmNLYHLYi9rb9tTf0l_bGZkezeFJoEeDLY8MrI10ozkN2-EeC_JzFgyvJHPMI7YQkfoszLy0vtMJRiXgaz6y0W2uJx9ulJXe-J0jIVhWOUw9_dzepith5Lp8DWnq6qafmVutFlCBkzJEGLKEewzzVr-4fcO5sGUXT2_NzWFpMfwuYDx4mCymhGViQosnpwc99_m6Tb3M5ih80PxePAfYd438YnYc_VEPLzBKjgRR2e74DUSHUZvOxGP-j066EOPnoo_cyh25N9gtySd0HgIyfvA_Vo1vIcIXQOd69YWGb6HVcvQsIbaAbYuIWyvwra0haoulhu2inBT9Edl6U7ZNGvgfCHAO4otKwadQffTLakRIXcFL9-ficvzs2-ni2jI1hAVKtVdlKU5-YaIVmMusdRaK-XLxKW-TL1LXZ6gzJTUhUMb-1xab6VXhT9BFXvrUR6J_bqp3QsBWKKP0XnlsmymLSL5IUhLGWe1Ip1TL4UcO8kUA5U5Z9RYmhGz9t30XWu4aw1D9xKqFW1rrXoqj3vk9dj_5i-VNGRt7qn5blQXQ6OVf8HY2jWb1jB5kZbsJN4lk6Saj_wuGckc07Q4vl2Gg7BkqlVOz3ne6-z2vZmHX9NK-NV_v-Nr8YCvelzjG7HfrTfuLflnHR6HAXgsDuYfPy8urgFwTkA_ |
| linkProvider | Elsevier |
| linkToHtml | http://utb.summon.serialssolutions.com/2.0.0/link/0/eLvHCXMwnV1La9wwEBbp5tCWUtpt00f6UKFXs7a1surjEhI2TbKXJpCb0NgSOCz2svYm_TH5sZmRH0mgSaAHg7FmjOQZaUbyzDeM_RRoZgwa3sAlEAZkoQNwSR444VwiIwhzD1Z9skjmZ9Pf5_J8i-31uTAUVtmt_e2a7lfr7smk-5qTVVFM_hA22jRCAyaFTzF9xrYJnUqO2Pbs8Gi-GBZkQu1qIb6xN8jQZ9D5MC_KJyspqDKSHsiT6uP-20I95IF6S3Twhr3uXEg-a3v5lm3Zcsxe3gEWHLOd_dv8NSTtJnA9Zq_aYzreZh-9Y9cznt3if3Mz4HTyynFfv4_bv6uKjhF5U_HGNmsDFMEHRU3RYRX2g5sy5_6ElQ9Pa16U2XJDhpHfJb0sDLbkVbXmVDKE06FiTbqBd7y5skvshC9fQTv49-zsYP90bx50BRuCTMaqCZI4RfcQwChIBeRKKSldHtnY5bGzsU0jEIkUKrNgQpcK44xwMnO_QIbOOBA7bFRWpf3IOOTgQrBO2iSZKgOArgjgbsYaJVHt5CcmeiHprEMzp6IaS92HrV3oVrSaRKspei9CrmDgWrVoHk_Qq17--p5WajQ4T3D-6NVF44SlvzCmtNWm1oRfpAT5iY_RRLGiK32MRhDMNO6PH6ahPCwRK5niez60OjuMm6D4FW6GP__3GL-z5_PTk2N9fLg42mUvqKUNc_zCRs16Y7-iu9bAt2463gA31ULw |
| openUrl | ctx_ver=Z39.88-2004&ctx_enc=info%3Aofi%2Fenc%3AUTF-8&rfr_id=info%3Asid%2Fsummon.serialssolutions.com&rft_val_fmt=info%3Aofi%2Ffmt%3Akev%3Amtx%3Ajournal&rft.genre=article&rft.atitle=A+comparative+assessment+of+human+exposure+to+tetrabromobisphenol+A+and+eight+bisphenols+including+bisphenol+A+via+indoor+dust+ingestion+in+twelve+countries&rft.jtitle=Environment+international&rft.au=Wang%2C+Wei&rft.au=Abualnaja%2C+Khalid+O.&rft.au=Asimakopoulos%2C+Alexandros+G.&rft.au=Covaci%2C+Adrian&rft.date=2015-10-01&rft.pub=Elsevier+Ltd&rft.issn=0160-4120&rft.eissn=1873-6750&rft.volume=83&rft.spage=183&rft.epage=191&rft_id=info:doi/10.1016%2Fj.envint.2015.06.015&rft.externalDocID=S0160412015300039 |
| thumbnail_l | http://covers-cdn.summon.serialssolutions.com/index.aspx?isbn=/lc.gif&issn=0160-4120&client=summon |
| thumbnail_m | http://covers-cdn.summon.serialssolutions.com/index.aspx?isbn=/mc.gif&issn=0160-4120&client=summon |
| thumbnail_s | http://covers-cdn.summon.serialssolutions.com/index.aspx?isbn=/sc.gif&issn=0160-4120&client=summon |