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首页> 外文期刊>Applied Geochemistry: Journal of the International Association of Geochemistry and Cosmochemistry >Bottled drinking water: Water contamination from bottle materials (glass, hard PET, soft PET), the influence of colour and acidification
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Bottled drinking water: Water contamination from bottle materials (glass, hard PET, soft PET), the influence of colour and acidification

机译:瓶装饮用水:瓶装材料(玻璃,硬PET,软PET)产生的水污染,颜色和酸化的影响

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摘要

A test comparing concentrations of 57 chemical elements (Ag, Al, As, B, Ba, Be, Bi, Ca, Cd, Ce, Co, Cr, Cs, Cu, Dy, Er, Eu, Fe, Ga, Gd, Ge, Hf, Ho, I, K, La, Li, Lu, Mg, Mn, Mo, Na, Nb, Nd, Ni, Pb, Pr, Rb, Sb, Se, Sm, Sn, Sr, Ta, Tb, Te, Th, Ti, Tl, Tm, U, V, W, Y, Yb, Zn and Zr) determined by inductively coupled plasma quadrupole mass spectrometry (ICP-QMS) in 294 samples of the same bottled water (predominantly mineral water) sold in the European Union in glass and PET bottles demonstrates significant (Wilcoxon rank sum test, α= 0.05) differences in median concentrations for Sb, Ce, Pb, Al, Zr, Ti, Th, La, Pr, Fe, Zn, Nd, Sn, Cr, Tb, Er, Gd, Bi, Sm, Y, Lu, Dy, Yb, Tm, Nb and Cu. Antimony has a 21× higher median value in bottled water when sold in PET bottles (0.33 vs. 0.016μg/L). Glass contaminates the water with Ce (19× higher than in PET bottles), Pb (14×), Al (7×), Zr (7×), Ti, Th (5×), La (5×), Pr, Fe, Zn, Nd, Sn, Cr, Tb (2×), Er, Gd, Bi, Sm, Y, Lu, Yb, Tm, Nb and Cu (1.4×). Testing an additional 136 bottles of the same water sold in green and clear glass bottles demonstrates an important influence of colour, the water sold in green glass shows significantly higher concentrations in Cr (7.3×, 1.0 vs. 0.14μg/L), Th (1.9×), La, Zr, Nd, Ce (1.6×), Pr, Nb, Ti, Fe (1.3×), Co (1.3×) and Er (1.1×).One hundred and twenty-six bottles of three different materials (glass, hard PET and soft PET) in 5 principal colours (clear, light and dark green and blue, brown) were subsequently washed and then filled with high purity water (18.2MΩcm). A portion of the bottles where left at the original average pH of the water (pH 6.5) while the remaining bottles were acidified to pH 3.5 with HNO_3. Concentrations of the same 57 elements as above were determined after 1, 2, 3, 4, 5, 15, 30, 56, 80 and 150days of leaching. Results substantiate the observations from the direct comparison of the same water sold in different bottle types (colour). For most elements leaching is enhanced at pH 3.5, and dark coloured bottles leach more than clear bottles, independent of bottle material. Values are still on the increase at the end of the test at 150days. At that date the leachates showed a maximum concentration of 0.45μg/L Sb, 0.3μg/L Ce, 0.61μg/L Pb, 68μg/L Al and 0.06μg/L Cr (all in glass at pH 3.5). None of the leachates approaches the maximum concentrations for drinking water as defined in European jurisdiction.
机译:比较57种化学元素(Ag,Al,As,B,Ba,Be,Bi,Ca,Cd,Ce,Co,Cr,Cs,Cu,Dy,Er,Eu,Fe,Ga,Gd,Ge ,Hf,Ho,I,K,La,Li,Lu,Mg,Mn,Mo,Na,Nb,Nd,Ni,Pb,Pr,Rb,Sb,Se,Sm,Sn,Sr,Ta,Tb,Te电感耦合等离子体四极杆质谱(ICP-QMS)测定的294个瓶装水(主要是矿泉水)样品中的Tb,Th,Ti,Tl,Tm,U,V,W,Y,Yb,Zn和Zr)欧盟的玻璃瓶和PET瓶显示Sb,Ce,Pb,Al,Zr,Ti,Th,La,Pr,Fe,Zn,Nd,Sb,Ce,Pb,Al,Zr的中位数浓度存在显着差异(Wilcoxon秩和检验,α= 0.05)。 Sn,Cr,Tb,Er,Gd,Bi,Sm,Y,Lu,Dy,Yb,Tm,Nb和Cu。装在PET瓶中的锑在瓶装水中的中位值高21倍(0.33对0.016μg/ L)。玻璃污染了水中的Ce(比PET瓶高19倍),Pb(14倍),Al(7倍),Zr(7倍),Ti,Th(5倍),La(5倍),Pr, Fe,Zn,Nd,Sn,Cr,Tb(2x),Er,Gd,Bi,Sm,Y,Lu,Yb,Tm,Nb和Cu(1.4x)。对另外136瓶以绿色和透明玻璃瓶出售的相同水进行测试,证明了颜色的重要影响,以绿色玻璃出售的水中Cr(7.3x,1.0 vs.0.14μg/ L),Th( 1.9倍),La,Zr,Nd,Ce(1.6倍),Pr,Nb,Ti,Fe(1.3倍),Co(1.3倍)和Er(1.1倍)。一百三十六瓶三种不同随后清洗5种主要颜色(透明,浅色和深绿色以及蓝色,棕色)的材料(玻璃,硬PET和软PET),然后填充高纯度水(18.2MΩcm)。将一部分瓶子留在水的原始平均pH值(pH 6.5)下,将其余瓶子用HNO_3酸化至pH 3.5。在浸出1、2、3、4、5、15、30、56、80和150天后确定与上述相同的57种元素的浓度。通过直接比较以不同瓶型(颜色)出售的相同水,结果证实了观察结果。对于大多数元素而言,在pH 3.5时浸出会增强,深色瓶子比透明瓶子的浸出更多,而与瓶子的材料无关。在测试结束时(150天),值仍在增加。当时渗滤液的最大浓度为0.45μg/ L Sb,0.3μg/ L Ce,0.61μg/ L Pb,68μg/ L Al和0.06μg/ L Cr(全部在pH 3.5的玻璃中)。没有渗滤液达到欧洲管辖区所定义的饮用水最高浓度。

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