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  • 1
    In: Environmental Science and Pollution Research, Springer Science and Business Media LLC, Vol. 25, No. 8 ( 2018-3), p. 7170-7179
    Type of Medium: Online Resource
    ISSN: 0944-1344 , 1614-7499
    RVK:
    Language: English
    Publisher: Springer Science and Business Media LLC
    Publication Date: 2018
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  • 2
    In: VNU Journal of Science: Natural Sciences and Technology, Vietnam National University Journal of Science, Vol. 36, No. 1 ( 2020-03-30)
    Abstract: In this study, the gas–particle distribution characteristics and emission sources of phthalate esters (PAEs) and volatile methyl siloxanes (VMSs) were evaluated for indoor air samples collected from different micro-environments such as homes, offices, kindergartens, hair salons, laboratories, and cars in 4 cities and provinces of Hanoi, Bac Ninh, Thai Binh, and Tuyen Quang, northern Vietnam. In general, total concentrations of PAEs and VMSs were higher in gas phase as compared to particle phase; however, phase distribution profiles of individual compounds were strongly related to their structures and physicochemical properties. For examples, low-molecular-weight compounds such as dimethyl phthalate, diethyl phthalate, D3, D4, L4, and L5 were more abundant in gas phase, while heavier compounds like di(2-ethylhexyl) phthalate and L8 were preferentially associated with particle phase. Assessment of PAE emission sources is relatively difficult because they have been applied in different consumer products and materials. Significant correlation between cyclic VMSs (e.g., D4, D5, and D6) was observed, suggesting their applications in cosmetics and personal care products. Keywords: Phthalate esters, volatile methyl siloxanes, indoor air, phase distribution, source apportionment.  
    Type of Medium: Online Resource
    ISSN: 2588-1140 , 2615-9317
    Language: Unknown
    Publisher: Vietnam National University Journal of Science
    Publication Date: 2020
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  • 3
    In: Environmental Geochemistry and Health, Springer Science and Business Media LLC, Vol. 39, No. 4 ( 2017-8), p. 935-954
    Type of Medium: Online Resource
    ISSN: 0269-4042 , 1573-2983
    Language: English
    Publisher: Springer Science and Business Media LLC
    Publication Date: 2017
    detail.hit.zdb_id: 1494595-2
    SSG: 13
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  • 4
    In: Chemosphere, Elsevier BV, Vol. 197 ( 2018-04), p. 389-398
    Type of Medium: Online Resource
    ISSN: 0045-6535
    RVK:
    Language: English
    Publisher: Elsevier BV
    Publication Date: 2018
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  • 5
    Online Resource
    Online Resource
    Vietnam National University Journal of Science ; 2022
    In:  VNU Journal of Science: Natural Sciences and Technology ( 2022-10-12)
    In: VNU Journal of Science: Natural Sciences and Technology, Vietnam National University Journal of Science, ( 2022-10-12)
    Abstract: In this study, a rapid analytical method was developed and validated for the determination of polybrominated diphenyl ethers PBDEs in house dust samples. The dust sample was solvent extracted by using a focused ultrasonic processor with reduced extraction time (total 30 min/sample) and solvent volume (about 30 mL/sample). The crude extract was purified by passing through a self-packed multilayer column containing 44% sulfuric acid impregnated silica gel, Florisil, and anhydrous sodium sulfate. PBDEs were eluted from the clean-up column by a mixture of dichloromethane in hexane (1:3,…). PBDEs (41 mono- to deca-BDE congeners) were analyzed by using gas chromatography/mass spectrometry (GC/MS) with negative chemical ionization (NCI) and selected ion monitoring (SIM) mode. The analytical method was validated by using procedural blank, matrix-spike, and standard reference material (SRM) samples. Recoveries of PBDEs in spiked samples ranged from 65% to 120%. Analytical results of the SRM 2585 (Organic Contaminants in House Dust, National Institute of Standards and Technology, USA) indicate method accuracy with ratios of measured to certified values of almost compounds ranging from 76% to 110%. All the experiments were conducted in duplicate, showing acceptable repeatability (RSD 〈 15%). This method can be applied for simultaneous determination of mono- to deca-BDE congeners in dust samples at ppb to ppm levels with several advantages such as simple, rapid, accurate, cost-effective, and reducing amounts of chemicals and solvents.
    Type of Medium: Online Resource
    ISSN: 2588-1140 , 2615-9317
    Language: Unknown
    Publisher: Vietnam National University Journal of Science
    Publication Date: 2022
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  • 6
    In: Marine Pollution Bulletin, Elsevier BV, Vol. 106, No. 1-2 ( 2016-05), p. 341-346
    Type of Medium: Online Resource
    ISSN: 0025-326X
    Language: English
    Publisher: Elsevier BV
    Publication Date: 2016
    detail.hit.zdb_id: 414337-1
    detail.hit.zdb_id: 2001296-2
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  • 7
    Online Resource
    Online Resource
    Vietnam National University Journal of Science ; 2020
    In:  VNU Journal of Science: Natural Sciences and Technology Vol. 36, No. 3 ( 2020-09-24)
    In: VNU Journal of Science: Natural Sciences and Technology, Vietnam National University Journal of Science, Vol. 36, No. 3 ( 2020-09-24)
    Abstract: Concentrations of polychlorinated biphenyls (PCBs) including 43 congeners of 10 homologs were determined in settled dust samples collected from urban houses and end-of-life vehicle (ELV) processing workshops in northern Vietnam. Concentrations of total 43 PCBs (ΣPCBs), 7 indicator PCBs (IN-PCBs), and 12 dioxin-like PCBs (DL-PCBs) in the ELV workshop dusts were significantly higher than those measured in the urban house dusts, suggesting ELV processing activities as potential sources of PCBs. However, concentrations of PCB-11 (3,3’-dichlorobiphenyl) in the urban house dusts (mean 4.5; range 1.2–8.7 ng/g) were markedly higher than levels found in the ELV workshop dusts (1.6; 0.46–5.4 ng/g). PCB-11 is a novel congener because it is only a trace component of technical PCB mixtures but identified as a major impurity of many organic pigments, especially diarylide yellow pigments. PCB patterns of the ELV workshop dusts were dominated by penta- and hexa-PCBs with major congeners as PCB-118, -138, -153, -110, and -101, which were also principal components of technical formulations such as Aroclor 1254, Kanechlor 500, and Sovol. Meanwhile, PCB-11 served as the most predominant congener detected in the urban house dusts, implying current emissions from paints and pigmented products; however, this point should be confirmed by further studies on the occurrence of PCBs in Vietnamese commercial products. Apart from PCB-11, the urban house dusts also contained elevated proportions of penta- and hexa-PCBs, suggesting residues from electrical equipment application in the past. Our results indicate that even though PCBs are legacy and banned chemicals, their presence has been observed in indoor environments due to their persistent nature and novel emission sources. Further studies on the occurrence and emission behavior of these pollutants should be conducted, including not only congeners in technical mixtures but also unintentionally produced compounds.
    Type of Medium: Online Resource
    ISSN: 2588-1140 , 2615-9317
    Language: Unknown
    Publisher: Vietnam National University Journal of Science
    Publication Date: 2020
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  • 8
    In: VNU Journal of Science: Natural Sciences and Technology, Vietnam National University Journal of Science, Vol. 35, No. 4 ( 2019-12-23)
    Abstract: Concentrations of 16 polycyclic aromatic hydrocarbons (PAHs) were determined in settled house dust and road dust samples collected from a core urban area of Hanoi. Levels of PAHs ranged from 830 to 3500 (median 2000) ng/g in house dust, and from 1400 to 4700 (median 1700) ng/g in road dust. Concentrations of PAHs in dust samples of this study were within the moderate range as compared with those from other countries in the world. Toxic equivalents to benzo[a]pyrene (BaP-EQs) in our samples ranged from 81 to 850 (median 330) ng BaP-EQ/g with principal contributors as BaP and dibenz[a,h] anthracene, which accounted for 69% to 93% of BaP-EQs. In almost all the samples, proportions of high-molecular-weight PAHs (HMW-PAHs with 4–6 rings) were higher than those of low-molecular-weight PAHs (LMW-PAHs with 2–3 rings), suggesting emission sources from combustion processes rather than direct contamination by petrogenic sources. Traffic activities were estimated as important sources of PAHs in the studied areas, for example, vehicular exhaust and tire debris. Keywords: PAHs, house dust, road dust, traffic emission, urbanization. References [1] K. Srogi, Monitoring of environmental exposure to polycyclic aromatic hydrocarbons: a review, Environ. Chem. Let. 5 (2007) 169-195. https://doi. org/10.1007/s10311-007-0095-0.[2] K.H. Kim, S.A. Jahan, E. Kabir, R.J.C. Brown, A review of airborne polycyclic aromatic hydrocarbons (PAHs) and their human health effects. Environ. Int. 60 (2013) 71–80. https://doi. org/10.1016/j.envint.2013.07.019.[3] E. Stogiannidis, R. Laane, Source characterization of polycyclic aromatic hydrocarbons by using their molecular indices: an overview of possibilities. Rev. Environ. Contam. Toxicol. 234 (2015) 49–133. https://doi.org/10.1007/978-3-319-10638-0_2.[4] H.I. Abdel-Shafy, M.S.M. Mansour, A review on polycyclic aromatic hydrocarbons: source, environmental impacts, effect on human health and remediation. Egypt. J. Pet. 25 (2016) 107–123. https://doi.org/10.1016/j.ejpe.2015.03.011.[5] ATSDR, 1995. Toxicological profile for polycyclic aromatic hydrocarbons. https://www.atsdr.cdc. gov/toxprofiles/tp69.pdf.[6] M.T. Anh, L.M. Triet, J.J. Sauvain, J. Tarradellas, PAH contamination levels in air particles and sediments of Ho Chi Minh City, Vietnam. Bull. Environ. Contam. Toxicol. 63 (1999) 728–735. https://doi.org/10.1007/s00128 9901040.[7] T.T. Hien, L.T. Thanh, T. Kameda, N. Takenaka, H. Bandow, Distribution characteristics of polycyclic aromatic hydrocarbons with particle size in urban aerosols at the roadside in Ho Chi Minh City, Vietnam. Atmos. Environ. 41 (2007) 1575–1586. https://doi.org/10.1016/j.atmosenv. 2006.10.045.[8] M. Kishida, K. Imamura, N. Takenaka, Y. Maeda, P.H. Viet, H. Bandow, Concentrations of atmospheric polycyclic aromatic hydrocarbons in particulate matter and the gaseous phase at roadside sites in Hanoi, Vietnam. Bull. Environ. Contam. Toxicol. 81 (2008) 174–179. https://doi. org/10.1007/s00128-008-9450-5. [9] H.Q. Anh, K. Tomioka, N.M. Tue, L.H. Tuyen, N.K. Chi, T.B. Minh, P.H. Viet, S. Takahashi, A preliminary investigation of 942 organic micro-pollutants in the atmosphere in waste processing and urban areas, northern Vietnam: levels, potential sources, and risk assessment. Ecotoxicol. Environ. Saf. 167 (2019) 354–364. https://doi.org/10.1016/j.ecoenv.2018.10.026.[10] C.V. Hung, B.D. Cam, P.T.N Mai, B.Q. Dzung, Heavy metals and polycyclic aromatic hydrocarbons in municipal sewage sludge from a river in highly urbanized metropolitan area in Hanoi, Vietnam: levels, accumulation pattern and assessment of land application. Environ. Geochem. Health 37 (2015) 133–146. https:// doi.org/10.1007/s10653-014-9635-2.[11] C.T. Pham, N. Tang, A. Toriba, K. Hayakawa, Polycyclic aromatic hydrocarbons and nitropolycyclic aromatic hydrocarbons in atmospheric particles and soil at a traffic site in Hanoi, Vietnam. Polycycl. Aromat. Comp. 35 (2015) 355–371. https://doi.org/10.1080/10406 638.2014.903284.[12] H.Q. Anh, K. Tomioka, N.M. Tue, G. Suzuki, T.B. Minh, P.H. Viet, S. Takahashi, Comprehensive analysis of 942 organic micro-pollutants in settled dusts from northern Vietnam: pollution status and implications for human exposure. J. Mater. Cycles Waste Manag. 21 (2019) 57–66. https://doi.org/10.1007/s101 63-018-0745-2.[13] L.H. Tuyen, N.M. Tue, G. Suzuki, K. Misaki, P.H. Viet, S. Takahashi, S. Tanabe, Aryl hydrocarbon receptor mediated activities in road dust from a metropolitan area, Hanoi-Vietnam: contribution of polycyclic aromatic hydrocarbons (PAHs) and human risk assessment. Sci. Total Environ. 491-492 (2014) 246–254. https://doi.org/10.1016/j.scitotenv.2014. 01.086.[14] L.H. Tuyen, N.M. Tue, S. Takahashi, G. Suzuki, P.H. Viet, A. Subramanian, K.A. Bulbule, P. Parthasarathy, A. Ramanathan, S. Tanabe, Methylated and unsubstituted polycyclic aromatic hydrocarbons in street dust from Vietnam and India: occurrence, distribution and in vitro toxicity evaluation. Environ. Pollut. 194 (2014) 272–280. https://doi.org/10.1016/j.envpol. 2014.07.029.[15] H.Q. Anh, T.M. Tran, N.T.T. Thuy, T.B. Minh, S. Takahashi, Screening analysis of organic micro-pollutants in road dusts from some areas in northern Vietnam: a preliminary investigation on contamination status, potential sources, human exposures, and ecological risk. Chemosphere 224 (2019) 428–436. https://doi.org/10.1016/j. chemosphere.2019.02.177.[16] H.T.T. Thuy, T.T.C. Loan, T.H. Phuong, The potential accumulation of polycyclic aromatic hydrocarbons in phytoplankton and bivalves in Can Gio coastal wetland, Vietnam. Environ. Sci. Pollut. Res. 25 (2018) 17240–17249. https://doi. org/10.1007/s11356-018-2249-y.[17] P.C. Van Metre, B.J. Mahler, J.T. Wilson, PAHs underfoot: contaminated dust from coal-tar sealcoated pavement is widespread in the United States. Environ. Sci. Technol. 43 (2009) 20–25. https://doi.org/10.1021/es802119h.[18] L. Liu, A. Liu, Y. Li, L. Zhang, G. Zhang, Y. Guan, Polycyclic aromatic hydrocarbons associated with road deposited solid and their ecological risk: Implications for road stormwater reuse. Sci. Total Environ. 563–564 (2016) 190–198. https://doi.org/10.1016/j.scitotenv.2016.04.114.[19] X. Zheng, Y. Yang, M. Liu, Y. Yu, J.L. Zhou, D. Li, PAH determination based on a rapid and novel gas purge-microsyringe extraction (GP-MSE) technique in road dust of Shanghai, China: Characterization, source apportionment, and health risk assessment. Sci. Total Environ. 557–558 (2016) 688–696. https://doi.org/10.1016/j. scitotenv.2016.03.124.[20] T.T. Dong, B.K. Lee, Characteristics, toxicity, and source apportionment of polycyclic aromatic hydrocarbons (PAHs) in road dust of Ulsan, Korea. Chemosphere 74 (2009) 1245–1253. https: //doi.org/10.1016/j.chemosphere.2008.11.035.[21] R. Khanal, H. Furumai, F. Nakajima, C. Yoshimura, Carcinogenic profile, toxicity and source apportionment of polycyclic aromatic hydrocarbons accumulated from urban road dust in Tokyo, Japan. Ecotoxicol. Environ. Saf. 165 (2018) 440–449. https://doi.org/10.1016/j. ecoenv.2018.08.095.[22] N. Soltani, B. Keshavarzi, F. Moore, T. Tavakol, A.R. Lahijanzadeh, N. Jaafarzadeh, M. Kermani, Ecological and human health hazards of heavy metals and polycyclic aromatic hydrocarbons (PAHs) in road dust of Isfahan metropolis, Iran. Sci. Total Environ. 505 (2015) 712–723. https://doi.org/10.1016/j.scitotenv.2014.09.097.[23] B.A.M. Bandowe, M.A. Nkansah, Occurrence, distribution and health risk from polycyclic aromatic compounds (PAHs, oxygenated-PAHs and azaarenes) in street dust from a major West African Metropolis. Sci. Total Environ. 553 (2016) 439-449. https://doi.org/10.1016/j. scitotenv.2016.02.142.[24] T.C. Nguyen, P. Loganathan, T.V. Nguyen, S. Vigneswaran, J. Kandasamy, D. Slee, G. Stevenson, R. Naidu, Polycyclic aromatic hydrocarbons in road-deposited sediments, water sediments, and soils in Sydney, Australia: Comparisons of concentration distribution, sources and potential toxicity. Ecotoxicol. Environ. Saf. 104 (2014) 339–348. https://doi.org/10.1016/j.ecoenv.2014.03.010. [25] C. Y. Kuo, H.C. Chen, F.C. Cheng, L.R. Huang, P.S. Chien, J.Y. Wang, Polycyclic aromatic hydrocarbons in household dust near diesel transport routes. Environ. Geochem. Health 34 (2012) 77–87. https://doi.org/10.1007/s10653-011-9392-4.[26] W. Wang, F.Y. Wu, J.S. Zheng, M.H. Wong, Risk assessments of PAHs and Hg exposure via settled house dust and street dust, linking with their correlations in human hair. J. Hazard. Mater. 263 (2013) 627–637. https://doi.org/10.1016/j.jhazmat. 2013.10.023.[27] N. Ali, I.M.I. Ismail, M. Khoder, M. Shamy, M. Alghamdi, M. Costa, L.N. Ali, W. Wang, S.A.M.A.S. Eqani, Polycyclic aromatic hydrocarbons (PAHs) in indoor dust samples from cities of Jeddah and Kuwait: levels, sources and non-dietary human exposure. Sci. Total Environ. 573 (2016) 1607–1614. https://doi.org/10.1016/j. scitotenv.2016.09.134.[28] M.Y. Civan, U.M. Kara, Risk assessment of PBDEs and PAHs in house dust in Kocaeli, Turkey: levels and sources. Environ. Sci. Pollut. Res. 23 (2016) 23369–23384. https://doi.org/10. 1007/s11356-016-7512-5.[29] A. Maragkidou, S. Arar, A. Al-Hunaiti, Y. Ma, S. Harrad, O. Jaghbeir, D. Faouri, K. Hämeri, T. Hussein, Occupational health risk assessment and exposure to floor dust PAHs inside an educational building. Sci. Total Environ. 579 (2017) 1050–1056. https://doi.org/10.1016/j.scitotenv.2016. 11.055. [30] I.C. Yadav, N.L. Devi, J. Li, G. Zhang, Polycyclic aromatic hydrocarbons in house dust and surface soil in major urban regions of Nepal: implication on source apportionment and toxicological effect. Sci. Total Environ. 616–617 (2018) 223–235. https://doi.org/10.1016/j.scitotenv.2017.10.313.[31] R. Boonyatumanond, M. Murakami, G. Wattayakorn, A. Togo, H. Takada, Sources of polycyclic aromatic hydrocarbons (PAHs) in street dust in a tropical Asian mega-city, Bangkok, Thailand. Sci. Total Environ. 384 (2007) 420−432. https://doi.org/10.1016/j.scitotenv. 2007.06.046.[32] I. Sadiktsis, C. Bergvall, C. Johansson, R. Westerholm, Automobile tire–a potential source of highly carcinogenic dibenzopyrenes to the environment. Environ. Sci. Technol. 46 (2012) 3326−3334. https://doi.org/10.1021/es204257d.[33] M. Howsam, K.C. Jones, Sources of PAHs in the environment. In: Neilson, A.H. (Ed.), The Handbook of Environmental Chemistry Vol. 3 Part I PAHs and Related Compounds. Springer-Verlag, Berlin, Heidelberg (1998) 137–174. https://doi.org/10.1007/978-3-540-49697-7_4.[34] I.C.T. Nisbet, P.K. Lagoy, Toxic equivalency factors (TEFs) for polycyclic aromatic hydrocarbons (PAHs). Regul. Toxicol. Pharmacol. 16 (1992) 290–300. https://doi.org/10. 1016/0273-2300(92)90009-X.[35] B. Pieterse, E. Felzel, R. Winter, B. van der Burg, A. Brouwer, PAH-CALUX, an optimized bioassay for AhR-mediated hazard identification of polycyclic aromatic hydrocarbons (PAHs) as individual compounds and in complex mixtures. Environ. Sci. Technol 47 (2013) 11651–11659. https://doi.org/10.1021/es403810w.[36] M.B. Yunker, R.W. Macdonald, R. Vingarzan, R. H. Mitchell, D. Goyette, S. Sylvestre, PAHs in the Fraser River basin: a critical appraisal of PAH ratios as indicators of PAH source and composition. Org. Geochem. 33 (2002) 489–515. https://doi.org/10.1016/S0146-6380(02)00002-5.[37] M. Saha, A. Togo, K. Mizukawa, M. Murakami, H. Takada, M.P. Zakaria, N.H. Chiem, B.C. Tuyen, M. Prudente, R. Boonyatumanond, S.K. Sarkar, B. Bhattacharya, P. Mishra, T.S. Tana, Sources of sedimentary PAHs in tropical Asian waters: differentiation between pyrogenic and petrogenic sources by alkyl homolog abundance. Mar. Pollut. Bull. 58 (2009) 189–200. https://doi.org/10.1016/j.marpolbul.2008.04.049.
    Type of Medium: Online Resource
    ISSN: 2588-1140 , 2615-9317
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    Publisher: Vietnam National University Journal of Science
    Publication Date: 2019
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  • 9
    In: Marine Pollution Bulletin, Elsevier BV, Vol. 144 ( 2019-07), p. 28-35
    Type of Medium: Online Resource
    ISSN: 0025-326X
    Language: English
    Publisher: Elsevier BV
    Publication Date: 2019
    detail.hit.zdb_id: 414337-1
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  • 10
    In: Marine Pollution Bulletin, Elsevier BV, Vol. 156 ( 2020-07), p. 111222-
    Type of Medium: Online Resource
    ISSN: 0025-326X
    Language: English
    Publisher: Elsevier BV
    Publication Date: 2020
    detail.hit.zdb_id: 414337-1
    detail.hit.zdb_id: 2001296-2
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