Analyses of selected organic contaminants and metals in drinking bottles

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1 Analyses of selected organic contaminants and metals in drinking s Technical report Pawel Rostkowski, Hilde T. Uggerud, Mikael Harju, Vladimir Nikiforov, Anders Borgen, Alfhild Kringstad, Morten Bjørklund, Silje Thomassen, Marit Vadset, Mebrat Ghebremeskel, Heidi Eikenes, Malcolm Reid

2 ISBN: CLASSIFICATION: A DATE SIGNATURE OF RESPONSIBLE PERSON NUMBER OF PAGES Kari Nygaard (sign.) 24 TITLE Analyses of selected organic contaminants and metals in drinking s Technical report AUTHOR(S) Pawel Rostkowski, Hilde T. Uggerud, Mikael Harju, Vladimir Nikiforov, Anders Borgen, Alfhild Kringstad, Morten Bjørklund, Silje Thomassen, Marit Vadset, Mebrat Ghebremeskel, Heidi Eikenes, Malcolm Reid NILU: Pawel Rostkowski, Hilde T. Uggerud, Mikael Harju, Vladimir Nikiforov, Anders Borgen, Morten Bjørklund, Silje Thomassen, Marit Vadset, Mebrat Ghebremeskel, Heidi Eikenes NIVA: Alfhild Krigstad, Malcolm Reid PROJECT LEADER Pawel Rostkowski NILU PROJECT NO. O QUALITY CONTROLLER Martin Schlabach REPORT PREPARED FOR CONTRACT REF. Norwegian Consumer Council (Forbrukerrådet) ABSTRACT On behalf of Norwegian Consumer Council NILU has conducted analyses of organic contaminants and metals in the leachate from selected drinking s. The simulation of the leakage is conducted based on a compilation of the methods described within NS- EN and NS-EN The instrumental analytical methods used were already established at NILU and NIVA. A number of different organic contaminants and metals have been found in trace amounts in the different products. NORWEGIAN TITLE Analyse av utvalgte miljøgifter og metaller i drikkeflasker og kaffekopper KEYWORDS Environmental contaminants Heavy metals Elements ABSTRACT (in Norwegian) NILU har på vegne av Forbrukerrådet bestemt innholdet av organiske forurensninger og tungmetaller i utlekkingsvæske fra utvalgte drikkeflasker. Simuleringen av lekkasjen er basert på en sammenstilling av metodene beskrevet i NS-EN og NS-EN De instrumentelle analysemetodene som ble benyttet var allerede etablert hos NILU og NIVA. En rekke forskjellige organiske forurensninger og metaller har blitt funnet i spormengder i de ulike produktene. PUBLICATION TYPE: Digital document (pdf) COVER PICTURE: Source: NILU NILU Norwegian Institute for Air Research The publication may be freely cited where the source is acknowledged NILU s ISO Certifications: NS-EN ISO 9001 and NS-EN ISO NILU s Accreditation: NS-EN ISO/IEC

3 Preface Norwegian Consumer Council was interested in checking for possible leakage of potential harmful substances from drinking s that could be drunk by Norwegian consumers. The aim of the project was to test out for leakage of selected organic contaminants and metals in s provided for analyses. The simulation of the leakage is conducted based on a compilation of the methods described within NS-EN and NS-EN Analyses of different compounds were conducted with methods established in NILU and NIVA laboratories. 2

4 Contents Preface... 2 Summary Introduction Materials and Methods Samples Compounds tested Organic contaminants Metals Methods Organic contaminants Metals Results Analytical uncertainty Concentrations of phenolic compounds Concentrations of selected phthalates Concentrations of selected organophosphorus flame retardants Concentrations of selected UV-filters Chlorinated paraffins New brominated flame retardants and hexachlorocyclohexane Metals Summary

5 Summary On behalf of Norwegian Consumer Council NILU has conducted analyses of organic contaminants and metals in the leachate from selected drinking s. The simulation of the leakage was conducted based on a compilation of the methods described within NS-EN and NS-EN The instrumental analytical methods used were already established at NILU and NIVA. A number of different organic contaminants and metals have been found in trace amounts in the different products. 4

6 Analyses of selected organic contaminants and metals in drinking s 1 Introduction Technical report The project was conducted as described in the offer that was sent to Norwegian Consumer Council on , Nets nr and that was accepted a day after. 11 different drinking s from various suppliers were purchased in different stores by the staff of Norwegian Consumer Council and delivered to NILU in January The aim of the project was to test out for leakage of selected organic contaminants and from the s provided for analyses. The simulation of the leakage was conducted based on the compilation of the methods described within NS-EN and NS-EN All analyses of the different compounds were conducted with methods established at NILU, except for UV-filters that were analysed by NIVA. 2 Materials and Methods 2.1 Samples In order to effectively conduct different analyses in laboratories in different locations, 11 drinking s were purchased in December 2017 and delivered in triplicate. A total of 33 s were delivered to NILU. Details are described in Table 1. One of the triplicated samples delivered was used for analyses of metals in NILU laboratory in Kjeller, while another two for organic analyses in NILUs laboratories in Kjeller and Tromsø, respectively. Table 1: Information about s subjected to analyses No Shop Location of purchase 1 XXL Alna center 2 G- Sport Alna center 3 Ikea Furuset 4 Nille Jernbanetorget 6 Jernia Strøget 7 Biltema Alna center 8 Rusta Alna 9 Europris Lindeberg 10 Coop Obs Alna 12 ToysRus Alna center 13 Clas Ohlson Alna center 2.2 Compounds tested Organic contaminants Details about the contaminants tested are included in tables

7 Table 2: Selected flame retardants and chlorinated paraffins Name Chemical name CAS number Organophosphorus flame retardants Structure TCEP Tris(2-chloroethyl) phosphate TCPP Tris(1-chloro-2-propyl) phosphate TDCPP Tris(1,3-dichloro-2- propyl)phosphate TBEP tris-(2-butoxyethyl)-phosphate EHDPP 2-ethylhexyl diphenyl phosphate TCP Tricresyl phosphate

8 Name Chemical name CAS number Structure TnBP Tri-n-butyl phosphate TiBP Tri-iso-butyl phosphate TPP Triphenyl phosphate TEHP tris(2-ethylhexyl)phosphate TEP Triethyl phosphate TXP Trixylenyl Phosphate

9 Name CAS Chemical name number New brominated flame retardants Structure BEHTBP Bis(2- ethylhexyl)tetrabromophthalate EHTBB 2-Ethylhexyl-2,3,4,5- tetrabromobenzoate HBB Hexabromobenzene PBT Pentabromotoluene PBBZ Pentabromobenzene DBDPE Decabromodiphenylethane BTBPE 1,2-Bis(2,4,6- tribromophenoxy)ethane α-tbech Β-TBECH α-tetrabromoethylcyclohexane Β-Tetrabromocyclohexane

10 Name Chemical name CAS number Structure g/d-tbech Γ/δ- Tretrabromocyclohexane Not available ATE (TBP- AE) 2,4,6-tribromophenyl allyl ether PBEB Pentabromoethylbenzene Dechloran e Plus (syn/anti) SCCP MCCP 1,4:7,10- Dimethanodibenzo[a,e]cycloocte ne / Cl Cl Cl Cl Cl Cl Cl Cl Cl Cl Cl Cl Chlorinated paraffins Short chain chlorinated paraffins Group of compounds, not a single structure 84-8 Medium chain chlorinated Group of compounds, not a single structure paraffins

11 Table 3: Selected phthalates Name Chemical name CAS number DMP Dimethylphthalate Structure DEP Diethylphthalate DiBP diisobutyl phthalate DBP BMPP di-n-butylphthalate Bis(4-metyl-2- pentyl) phthalate BMEP Bis(2-metoxyethyl) phthalate BEEP Bis(2-etoxyethyl) phthalate

12 Name Chemical name CAS number DPP Dipentyl phthalate Structure DHXP di-n-hexyl phthalate BBP benzyl butyl phthalate BnBP Bis(2-nbutoxyethyl) phthalate DEHP Bis(2-ethylhexyl) phthalate DCHP dicyclohexyl phthalate DOP di-n-octyl phthalate DNP di-nonyl phthalate

13 Table 4: Selected phenolic compounds and alkylphenol ethoxylates Name CAS number Structure Bisphenol A ,4'-Bisphenol A Bisphenol B Bisphenol C Bisphenol E ,2'-Bisphenol F ,4'-Bisphenol F ,4-Bisphenol F Bisphenol G

14 Bisphenol M Bisphenol P Bisphenol S (4,4') ,4'-Bisphenol S Bisphenol Z Bisphenol AF Bisphenol AP Bisphenol BP Bisphenol FL

15 Bisphenol PH Bisphenol TMC Tetrabromobisphenol A Octylphenol monoethoxylate (OPEO- 1) Octylphenol diethoxylate (OPEO-2) Nonylphenol monoethoxylate (NPEO- 1) Nonylphenol diethoxylate (NPEO-2) Triclosan

16 Table 5: Selected benzotriazole based UV-filters Name CAS number Structure 2-ethylhexyl-4- Dimethylaminobenzoate (ODPABA) Benzophenone 3 (BP3) Ethylhexylmethoxycinnamate (EHMC) Octocrylene (OC) UV UV UV UV UV UV

17 2.2.2 Metals Following metals were quantified in extracts: Aluminum (Al) Antimony (Sb) Arsenic (As) Beryllium (Be) Lead (Pb) Gallium (Ga) Germanium (Ge) Cadmium (Cd) Cobalt (Co) Copper (Cu) Chromium (Cr) Mercury (Hg) Molybdenum (Mo) Nickel (Ni) Zinc (Zn) Silver (Ag) Thallium (Tl) Tellurium (Te) Tin (Sn) Vanadium (V) 16

18 2.3 Methods Organic contaminants To avoid contamination and possible false identifications, all the s were thoroughly rinsed with ultra-pure Milli-Q water prior to extraction. Drinking s were filled with MilliQ-water again and extracted in 40 C for 24-hours. After 24-hrs, the extracts containing possible leachate were spiked with mixtures of isotopically labelled standards and subjected for further cleanup and concentration suitable to different type of analyses (liquid-liquid and/or solid phase extraction). To avoid possible false positives in analytical results due to contamination in the laboratory, lab blank samples were prepared with each batch of processed samples. In brief, clean glass containers were treated exactly the same way as drinking s. The final extracts were subjected to analyses with either gas or liquid-chromatography high resolution mass spectrometry Metals To avoid contamination and possible false identifications, all the s were thoroughly rinsed with ultra-pure Milli-Q water prior to extraction. Drinking s were filled with acetic acid diluted in MilliQ-water to 3% and extracted in 40 C for 24-hours. The extracts were analyzed by use of inductively coupled plasma mass spectrometry (ICP-MS) (Agilent 7700x). The calibration standards were matrix matched with 3% acetic acid. 115 In was used as internal standard and added to all calibration standards, blank samples and extracts during analysis. 17

19 3 Results 3.1 Analytical uncertainty Due to the lack of available certified reference materials, replicated samples were analysed. The methods used are validated, but not accredited and analytical uncertainty for organic contaminants measured in this study has been established at the level of 60%. Although it appears to be somewhat high, for comparison, typical uncertainty in established accredited analyses of persistent organic pollutants in environmental matrices is at the level of 30-40%. Uncertainty for metals in this study was established at the level of 35%. 3.2 Concentrations of phenolic compounds 51 ng/kg of Octylphenol monoethoxilate (OPEO-1) was detected in a drinking from Toys R Us. Concentration of nonylphenol monoethoxylate (NPEO-1) was lower (37 ng/kg). Octylphenol diethoxylate was found only in a drinking from Toys R Us. In all other samples the levels of alkylphenol ethoxylates were below 10ng/kg. Several other phenolic contaminants have been detected and are presented in Table 6. Table 6: Selected phenolic contaminants found in leachate from drinking s (ng/kg). Note: to facilitate presentation only compounds detected in at least one of the samples are presented. Limits of detection (LOD) for all bisphenols from table 4 were established at 1ng/kg and for triclosan at 0.6 ng/kg. Type of the container Details bisphenol A (4,4')- bisphenol F (2,4')- bisphenol F (2,2')- bisphenol F bisphenol AF bisphenol S triclosan XXL <1 <1 4 <1 <1 <1 <0.6 G-Sport 52 <1 <1 <1 <1 <1 <0.6 Ikea <1 <1 <1 <1 <1 <1 <0.6 Nille 44 <1 <1 <1 <1 <1 <0.6 Jernia <1 <1 <0.6 Biltema <1 2 <0.6 Rusta < <1 <0.6 Europris 9 <1 <1 <1 <1 0 <0.6 Coop Obs <1 4 4 <1 <1 <1 <0.6 Toys R Us <1 0.8 Clas Ohlson <1 8 4 <1 <1 <1 < Concentrations of selected phthalates Limits of detection for selected phthalates that were not detected in the samples are presented in Table 7, while the concentrations of phthalates (ng/kg) found in the samples are presented in Table 8. Table 7: Limits of detection for analysed phthalates (ng/kg). Name Type BMEP BMPP BEEP DPP DHXP DCHP/DEHP DOP DNP LOD

20 Table 8: Concentrations of phthalates in a leachate from drinking s (ng/kg). Note: To facilitate presentation only compounds detected in at least one of the samples are presented. Type of Details DMP DEP DiBP DBP BBP DCHP/DEHP the container XXL < < <136 <45.8 G-Sport < < <136 <45.8 Ikea <24.8 <35.8 <5.5 <24.1 <136 <45.8 Nille <24.8 <35.8 < <136 <45.8 Jernia <24.8 < <136 <45.8 Biltema 206 < <136 <45.8 Rusta <24.8 < <136 <45.8 Europris < < <136 <45.8 Coop Obs Toys R Us Clas Ohlson <24.8 <35.8 <5.5 <24.1 <136 <45.8 < <45.8 < <136 < Concentrations of selected organophosphorus flame retardants Several organophosphorus flame retardants have been detected in the samples (Table 10). Limits of detection for those not being detected are presented in Table 9. Table 9: Limits of detection for selected organophosphorus flame retardants TPrP BdPhP DBPhP TDCPP TCP EHDP TXP TIPPP TTBPP TEHP

21 Table 10: Concentrations of organophosphorus flame retardants in a leachate from drinking s (ng/kg). Note: to facilitate presentation only compounds detected in at least one of the samples are presented. Type of the Details TEP TCEP TCPP TiBP TnBP TPP TBEP container XXL <9.23 <13.1 <15.3 <72.6 <2.22 <0.4 <58.8 G-Sport < <72.6 <2.22 <0.4 <58.8 Ikea <9.23 <13.1 <15.3 <72.6 <2.22 <0.4 <58.8 Nille <9.23 <13.1 <15.3 <72.6 <2.22 <0.4 <58.8 Jernia <9.23 <13.1 <15.3 <72.6 <2.22 <0.4 <58.8 Biltema 27.5 <13.1 <15.3 <72.6 < <58.8 Rusta <9.23 <13.1 <15.3 <72.6 < <58.8 Europris <9.23 <13.1 <15.3 <72.6 <2.22 <0.4 <58.8 Coop Obs <9.23 <13.1 <15.3 <72.6 <2.22 <0.4 <58.8 Toys R Us < < Clas Ohlson 25.1 <13.1 <15.3 <72.6 <2.22 <0.4 < Concentrations of selected UV-filters Analyses of benzotriazole based UV-filters revealed presence of BP3 only in leachate drinking from Toys R Us (31 ng/kg).. The levels of UV-filters were under limits of detection (see Table 11) for all other samples. Table 11: Limits of detection for selected UV-filters for all samples tested in this study (ng/kg). Type of container drinking s BP3 ODPABA UV-320 UV-326 UV-329 UV-328 UV-327 OC Sum EHMC

22 3.6 Chlorinated paraffins Concentrations of chlorinated paraffins are presented in Table 12. Table 12: Concentrations of chlorinated paraffins Type of the Details SCCP (ng/kg) MCCP (ng/kg) container drinking XXL < drinking G-Sport < drinking Ikea < drinking Nille < drinking Jernia < drinking Biltema < drinking Rusta < drinking Europris < drinking COOP < Obs drinking Toys R Us < drinking Clas Olson < New brominated flame retardants and hexachlorocyclohexane Only DBDPE and isomers of hexachlorocyclohexane were detected in some of the samples ( Table 13). Other brominated flame retardants were not detected (with LOD< ng/kg). Table 13: Concentrations of new brominated flame retardants and hexachlorocyclohexane in a leachate from drinking s Type of details a-hch b-hch g-hch DBDPE container (ng/kg). Note: to facilitate XXL <2 presentation only compounds Type of details a-hch b-hch g-hch DBDPE detected in at least one of the container G-Sport <2 samples are presented. Ikea XXL <2 <2 Nille G-Sport <2 Jernia Ikea <2 Biltema Nille Rusta Jernia Europris Biltema Coop Rusta Obs <2 Toys Europris R Us Clas Coop Obs Ohlson Toys R Us < Clas Ohlson

23 3.8 Metals Germanium, silver (LODs = 10 ng/kg), arsenic (LOD = 50 ng/kg), tellurium, thallium and bismuth (LODs = 5 ng/kg) were not detected in any of the samples. Concentrations of other metals are presented in table Table

24 Table 14: Results of analyses of metals (ng/kg). Note: to facilitate presentation only compounds detected in at least one of the samples are presented. Type of the container Drinking Drinking Drinking Drinking Drinking Drinking Drinking Drinking Drinking Drinking details Be Al V Cr Co Ni Cu Zn Ga Mo Cd Sn Sb Te Pb XXL < <5 <50 <4 < <50 <10 <5 <50 <3 < G-Sport 7.74 <1000 <5 <50 <4 < <50 <10 <5 <50 <3 <5 <9 IKEA <5 <1000 <5 <50 <4 <20 < <50 <10 <5 <50 <3 <5 <9 Jernia < <5 < < Biltema < < <10 <5 < < Rusta <5 <1000 <5 <50 <4 <20 < <50 <10 <5 < <5 <9 Europris <5 <1000 <5 <50 <4 < <50 <10 < <3 < COOP obs <5 < <50 <4 <20 < <50 <10 <5 <50 <3 <5 <9 ToysRus <5 < < < <50 <10 <5 < < Clas Ohlson <5 <1000 <5 <50 <4 <20 <10 <100 <50 <10 <5 <50 <3 <5 <9 23

25 4 Summary A number of different environmental organic contaminants and metals have been found in trace amounts in selected commercial drinking s. As this is a data report only, the obtained results were neither compared with other reports nor discussed further. 24

26 NILU Norwegian Institute for Air Research NILU Norwegian Institute for Air Research is an independent, nonprofit institution established in Through its research NILU increases the understanding of climate change, of the composition of the atmosphere, of air quality and of hazardous substances. Based on its research, NILU markets integrated services and products within analyzing, monitoring and consulting. NILU is concerned with increasing public awareness about climate change and environmental pollution. NILU s values: NILU's vision: Integrity - Competence - Benefit to society Research for a clean atmosphere NILU Norwegian Institute for Air Research P.O. Box 100, NO-2027 KJELLER, Norway nilu@nilu.no ISBN:

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