Centre for Environmental Risk Assessment and Remediation (CERAR), University of South Australia, Mawson Lakes, SA, Australia.
Environ Int. 2011 Jan;37(1):184-9. doi: 10.1016/j.envint.2010.08.017. Epub 2010 Sep 26.
Contaminants in general do not occur as single chemicals but as mixtures at any contaminated site. Gasworks sites are the typical mixed contaminated sites. These sites are not only subjected to PAH contamination but also varying degrees of heavy metal contamination. Bioremediation in these sites is often hindered by the presence of heavy metals. The co-occurrence of PAHs with heavy metals has not been systematically investigated. Metals are reported to inhibit the general soil microbiological processes. The total concentration of soluble metal in the system includes both free metal ion and complexed forms. Within bioavailable fraction, the most toxic form is the free metal species, which was not addressed well so far in gas works site characterisation. This study underpins the science and importance of metal bioavailability and speciation based site characterisation in mixed contaminated sites. In this study a detailed elemental chemistry of the gas works site soils are discussed using different methods. The PAH contamination was contributed by both low and high molecular weight PAHs. The total PAHs concentration ranged from 335 to 8645 mg/kg. Among most toxic metals Pb was found in high concentration ranging from 88 to 671 mg/kg, Cd 8 to 112 mg/kg and Zn varied from 64 to 488 mg/kg. Thermodynamic chemical equilibrium model VMINTEQ (Ver 2.52) was used to calculate the free metal species in gas works site soils. The percentage free metal species showed a different trend compared to total metal concentrations, free Zn species ranged 18-86%, free Cd was 26-87% and Pb showed lowest free metal percentage (0-17%). The bioavailable metal species and its implications to bioremediation have also been discussed.
一般来说,污染物不是以单一化学物质的形式存在,而是在任何污染地点以混合物的形式存在。煤气厂遗址就是典型的混合污染地点。这些地点不仅受到多环芳烃的污染,还受到不同程度的重金属污染。生物修复在这些地点经常受到重金属的阻碍。多环芳烃与重金属的共同存在尚未得到系统的研究。据报道,金属会抑制土壤的一般微生物过程。系统中可溶性金属的总浓度包括游离金属离子和络合形式。在可利用的部分中,最有毒的形式是游离金属物种,到目前为止,在煤气厂遗址的特征描述中还没有很好地解决这个问题。本研究支持了基于金属生物可利用性和形态的混合污染场地特征描述的科学和重要性。在这项研究中,使用不同的方法讨论了煤气厂遗址土壤的详细元素化学。多环芳烃污染是由低分子量和高分子量多环芳烃共同造成的。总多环芳烃浓度范围为 335 至 8645 毫克/千克。在最有毒的金属中,Pb 的浓度很高,范围为 88 至 671 毫克/千克,Cd 为 8 至 112 毫克/千克,Zn 的浓度范围为 64 至 488 毫克/千克。热力学化学平衡模型 VMINTEQ(版本 2.52)用于计算煤气厂遗址土壤中的游离金属物种。游离金属物种的百分比显示出与总金属浓度不同的趋势,游离 Zn 物种的范围为 18-86%,游离 Cd 为 26-87%,Pb 显示出最低的游离金属百分比(0-17%)。还讨论了生物可利用的金属物种及其对生物修复的影响。