Weihmann Jenny, Mansfeldt Tim, Schulte Ulrike
Arbeitsgruppe Bodengeographie/Bodenkunde, Geographisches Institut, Universität zu Köln, D-50923 Köln, Germany.
Anal Chim Acta. 2007 Jan 23;582(2):375-81. doi: 10.1016/j.aca.2006.09.013. Epub 2006 Sep 16.
The occurrence of iron-cyanide complexes in the environment is of concern, since they are potentially hazardous. In order to determine the source of iron-cyanide complexes in contaminated soils and wastes, we developed a method based on the stable isotope ratios (13)C/(12)C and (15)N/(14)N of the complexed cyanide-ion (CN(-)). The method was tested on three pure chemicals and two industrials wastes: blast-furnace sludge (BFS) and gas-purifier waste (GPW). The iron-cyanide complexes were converted into the solid cupric ferrocyanide, Cu(2)[Fe(CN)(6)].7H(2)O, followed by combustion and determination of the isotope-ratios by continuous flow isotope ratio mass spectrometry. Cupric ferrocyanide was obtained from the materials by (i) an alkaline extraction with 1M NaOH and (ii) a distillate digestion. The Fe(CN)(6) of the alkaline extraction was precipitated after adding Cu(2+). The CN(-) of the distillate digestion was at first complexed with Fe(2+) under inert conditions and then precipitated after adding Cu(2+). The delta(13)C-values obtained by the two methods differed slightly up to 1-3 per thousand for standards and BFS. The difference was larger for alkaline-extracted GPW (4-7 per thousand), since non-cyanide C was co-extracted and co-precipitated. Therefore the distillate digestion technique is recommended when determining the C isotope ratios in samples rich in organic carbon. Since the delta(13)C-values of BFS are in the range of -30 to -24 per thousand and of -17 to -5 per thousand for GPW, carbon seems to be a suitable tracer for identifying the source of cyanide in both wastes. However, the delta(15)N-values overlapped for BFS and GPW, making nitrogen unsuitable as a tracer.
环境中氰化铁络合物的出现令人担忧,因为它们具有潜在危险性。为了确定受污染土壤和废物中氰化铁络合物的来源,我们基于络合氰离子(CN⁻)的稳定同位素比率(¹³C/¹²C和¹⁵N/¹⁴N)开发了一种方法。该方法在三种纯化学品和两种工业废物上进行了测试:高炉污泥(BFS)和气体净化废物(GPW)。将氰化铁络合物转化为固体亚铁氰化铜Cu₂[Fe(CN)₆]·7H₂O,然后燃烧并通过连续流同位素比率质谱法测定同位素比率。通过以下步骤从材料中获得亚铁氰化铜:(i)用1M NaOH进行碱性萃取,以及(ii)馏出物消解。碱性萃取的[Fe(CN)₆]⁴⁻在加入Cu²⁺后沉淀。馏出物消解的CN⁻首先在惰性条件下与Fe²⁺络合,然后在加入Cu²⁺后沉淀。对于标准品和BFS,两种方法获得的δ¹³C值略有差异,高达千分之一至千分之三。碱性萃取的GPW差异更大(千分之四至千分之七),因为非氰化物C被共萃取和共沉淀。因此,在测定富含有机碳的样品中的C同位素比率时,建议使用馏出物消解技术。由于BFS的δ¹³C值在千分之 - 30至 - 24范围内,GPW的δ¹³C值在千分之 - 17至 - 5范围内,碳似乎是识别两种废物中氰化物来源的合适示踪剂。然而,BFS和GPW的δ¹⁵N值重叠,使得氮不适合作为示踪剂。