Antimony leaching from polyethylene terephthalate (PET) plastic used for bottled drinking water

被引:230
|
作者
Westerhoff, Paul [1 ]
Prapaipong, Panjai [2 ]
Shock, Everett [2 ,3 ]
Hillaireau, Alice [4 ]
机构
[1] Arizona State Univ, Dept Civil & Environm Engn, Tempe, AZ 85287 USA
[2] Arizona State Univ, Sch Earth & Space Explorat, Tempe, AZ 85287 USA
[3] Arizona State Univ, Dept Chem & Biochem, Tempe, AZ 85287 USA
[4] Univ Poitiers, Poitiers, France
关键词
antimony; drinking water; polyethylene terephthalate;
D O I
10.1016/j.watres.2007.07.048
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Antimony is a regulated contaminant that poses both acute and chronic health effects in drinking water. Previous reports suggest that polyethylene terephthalate (PET) plastics used for water bottles in Europe and Canada leach antimony, but no studies on bottled water in the United States have previously been conducted. Nine commercially available bottled waters in the southwestern US (Arizona) were purchased and tested for antimony concentrations as well as for potential antimony release by the plastics that compose the bottles. The southwestern US was chosen for the study because of its high consumption of bottled water and elevated temperatures, which could increase antimony leaching from PET plastics. Antimony concentrations in the bottled waters ranged from 0.095 to 0.521 ppb, well below the US Environmental Protection Agency (USEPA) maximum contaminant level (MCL) of 6 ppb. The average concentration was 0.195 +/- 0.116 ppb at the beginning of the study and 0.226 +/- 0.160 ppb 3 months later, with no statistical differences; samples were stored at 22 degrees C. However, storage at higher temperatures had a significant effect on the time-dependent release of antimony. The rate of antimony (Sb) release could be fit by a power function model (Sb(t) = Sb-o x [Time, h](k); k = 8.7 x 10(-6) x [Temperature (C)]2 55; Sbo is the initial antimony concentration). For exposure temperatures of 60, 65, 70, 75, 80, and 85 degrees C, the exposure durations necessary to exceed the 6 ppb MCL are 176, 38, 12, 4.7, 2.3, and 1.3 days, respectively. Summertime temperatures inside of cars, garages, and enclosed storage areas can exceed 65 degrees C in Arizona, and thus could promote antimony leaching from PET bottled waters. Microwave digestion revealed that the PET plastic used by one brand contained 213 35 mgSb/kg plastic; leaching of all the antimony from this plastic into 0.5 L of water in a bottle could result in an antimony concentration of 376 ppb. Clearly, only a small fraction of the antimony in PET plastic bottles is released into the water. Still, the use of alternative types of plastics that do not leach antimony should be considered, especially for climates where exposure to extreme conditions can promote antimony release from PET plastics. (c) 2007 Elsevier Ltd. All rights reserved.
引用
收藏
页码:551 / 556
页数:6
相关论文
共 50 条
  • [41] Characterization of poly(ethylene terephthalate) used in commercial bottled water
    Bach, Cristina
    Dauchy, Xavier
    Etienne, Serge
    5TH INTERNATIONAL EEIGM/AMASE/FORGEMAT CONFERENCE ON ADVANCED MATERIALS RESEARCH, 2009, 5
  • [42] Elucidating the Parameters Involved with Antimony and Phthalates Co-leaching in Bottled Water
    Andra, Syam S.
    Makris, Konstantinos C.
    METALS AND RELATED SUBSTANCES IN DRINKING WATER, 2012, : 281 - 281
  • [43] Migration of Plasticizers from Polyethylene Terephthalate and Low-Density Polyethylene Casing into Bottled Water: A Case Study From India
    Moitraiyee Mukhopadhyay
    Mohammed Jalal
    G. Vignesh
    Muhammed Ziauddin
    Srimurali Sampath
    Girija K. Bharat
    Luca Nizzetto
    Paromita Chakraborty
    Bulletin of Environmental Contamination and Toxicology, 2022, 109 : 949 - 955
  • [44] Migration of Plasticizers from Polyethylene Terephthalate and Low-Density Polyethylene Casing into Bottled Water: A Case Study From India
    Mukhopadhyay, Moitraiyee
    Jalal, Mohammed
    Vignesh, G.
    Ziauddin, Muhammed
    Sampath, Srimurali
    Bharat, Girija K.
    Nizzetto, Luca
    Chakraborty, Paromita
    BULLETIN OF ENVIRONMENTAL CONTAMINATION AND TOXICOLOGY, 2022, 109 (06) : 949 - 955
  • [45] Novel putative polyethylene terephthalate (PET) plastic degrading enzymes from the environmental metagenome
    Karunatillaka, Isuru
    Jaroszewski, Lukasz
    Godzik, Adam
    PROTEINS-STRUCTURE FUNCTION AND BIOINFORMATICS, 2022, 90 (02) : 504 - 511
  • [46] Fabrication and properties of polyethylene terephthalate (PET) aerogel composites from plastic bottle waste
    Goh, Xue Yang
    Guo, Kaiting
    Nguyen, Luon Tan
    Ong, Ren Hong
    Duong, Hai M.
    MATERIALS TODAY COMMUNICATIONS, 2023, 37
  • [47] Impact of sunlight/dark storage on natural spring water bottled in polyethylene terephthalate
    Abboudi, Maher
    Odeh, Adnan
    JOURNAL OF WATER SUPPLY RESEARCH AND TECHNOLOGY-AQUA, 2015, 64 (02): : 149 - 156
  • [48] Determination of Antimony from Polyethylene Terephthalate in Drinking Water by Solid Floating Organic Drop Microextraction and Electrothermal Atomization Atomic Absorption Spectrometry
    Atakan, Deniz
    Durukan, Ilknur
    Bektas, Sema
    ANALYTICAL LETTERS, 2016, 49 (07) : 1066 - 1078
  • [49] Effect of Contact Time on the Level of Phthalates in Polyethylene Terephthalate-bottled Water from the Point of Sale
    Hazira, Abdul Rasid
    Fatimah, Ungku Zainal Abidin Ungku
    Jinap, Selamat
    Omar, Syaliza
    Sanny, Maimunah
    PERTANIKA JOURNAL OF TROPICAL AGRICULTURAL SCIENCE, 2021, 44 (02): : 389 - 400
  • [50] Bottled drinking water: Water contamination from bottle materials (glass, hard PET, soft PET), the influence of colour and acidification
    Reimann, Clemens
    Birke, Manfred
    Filzmoser, Peter
    APPLIED GEOCHEMISTRY, 2010, 25 (07) : 1030 - 1046