Dioxin & PCB Analysis

Dioxins have been considered highly toxic and cause reproductive and developmental problems. Since the amount of dioxin in the environment is extremely small, it is imperative to secure accurate and sensitive detection methods for qualitative and quantitative measurements. With this in mind, FUJIIFILM Wako has a large selection of reference standards, standard solutions, and mixed standard solutions used for the analysis of dioxins and PCBs (polychlorinated biphenyls).

FUJIFILM Wako Pure Chemical Corporation provides a wide variety of mixed standards.

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An Overview on Methods for Analysis of Dioxins in China

Methods for the analysis of dioxins have been developed to be equivalent to international standards, so each nation has laid down these methods. However, as the demand for dioxins monitoring has increased, simple methods have been developed that can be performed quickly and at low cost. In some nations, such as the EU, the U.S. and Japan, have laid down simple methods for the analysis of dioxins. This article will explain methods for the analysis of dioxins, focusing on China’s trends.

Definition of dioxins

Dioxins are defined as the following three groups of organochlorine compounds;

  • Polychlorinated dibenzo-para-dioxin (PCDDs)
  • Polychlorinated dibenzofurans (PCDFs)
  • Dioxin-like PCBs (Dl-PCBs)

Dl-PCBs possess similar toxicity to those of PCDDs and PCDFs. Each group includes their homologue and isomer with chlorine substituents in eight positions.

*Dl-PCBs could be called coplanar polychlorinated biphenyl (Co-PCBs).

dioxin_pcb_img01.png
Figure 1 Dioxins

The United Nations Environment Programme(UNEP) provides the catalogue of all kinds of dioxins in the “Toolkit for Identification and Quantification of Releases of Dioxins, Furans and Other Unintentional POPs”, based on the ”Article of the Stockholm Convention”. In the Article 7 of the convention, each party are required to develop and submit to the conference of the parties a national implementation plan to fulfill their conditional obligations and to revise it as new substances are added. In addition, Article 5 stipulates that an action plan for reducing or eliminating unintentionally generated POPs such as PCDD and PCDF should be developed and implemented as a part of the domestic implementation plan.

Dioxins are not substances manufactured as industrial products, but substances generated by natural phenomena such as waste incinerators and forest fires. Dioxins are generated from exhaust gas and wastewater emitted from incinerators, herbicides and pesticides used on farms, and polychlorinated biphenyls (PCBs) used as insulating oil for electrical equipment.

Since the dioxins generation mechanism by combustion is complicated, the generation process has not been completely elucidated. It is said that dioxins are generated when precursors produced by burning organic compounds at low temperatures undergo a complex chemical reaction.

dioxin_pcb_img02.png
Figure 2 The mechanism of dioxins generation

 

Countermeasures against dioxins and official law in China

As of March 2020, 181 parties, the EU, and the Palestinian Interim Self-Government Authority (PA) have signed the POPs Convention, and POPs countermeasures are progressing worldwide. On the other hand, there are not many countries in East Asia where chemical substance management is advanced, and they are promoting interregional cooperation.

China joined the World Trade Organization (WTO) in 2001 and has been accelerating the development of environment-related legislation since then. This is because each party of WTO is obliged to make legislation as to international trades, and keep the administrative transparency. The agreement on Technical Barriers to Trade (TBT) was issued in 1995, and on its basis each party is obliged to make or revise local standards there (in China, GB standard) equivalent to international standards, such as ISO and IEC.

The method of environmental measurement and analysis for determining whether dioxins do not exceed the standard value set by the government is stipulated as the official analytical method by laws and regulations. There is a need to have a legally sufficient scientific basis, so it is required to be a method comparable to the ISO standard.

Dioxins research in China began in the late 1980s and early 1990s. Gas chromatography /high-resolution mass spectrometry (GC/HRMS) was often used in accordance with the in EPA in U.S. “EPA Method 8280A” as an analysis method for PCDDs and PCDFs in samples. In China, the official analytical method came into effect on April 1, 2009 due to growing interest in environmental pollution caused by dioxins and the need for legislation that complies with international standards such as ISO. However, it does not cover all dioxins, for example HJ 77.2-2008 does not specify the analysis of Dl-PCBs.

Table 1 Some national standards for dioxin analysis and regulation in China
dioxin_pcb_img03R.png

 

Dioxin analysis

Typical analytical methods for dioxins include conventional instrumental methods, GC/HRMS, and biological assay.

Table 2 Applicability of dioxin analysis method to sample objects
dioxin_pcb_img04.png
※1 applicable for soot and dust samples

 

dioxin_pcb_img05.png
Figure 3 Steps in a typical dioxin analysis

The procedure for measuring dioxins is shown in figure 3. A sample is collected for each target, PCDDs and PCDFs are extracted, cleanup of them using silica gel column chromatography and reagents, and the identification and quantification of them prescribed in each method.

Typical methods for the analysis of dioxins are described as follows.

 

1. Gas chromatography/high-resolution mass spectrometry (GC/HRMS)

GC/HRMS consists of gas chromatography (GC) that can separate the mixture into individual component and mass spectrometry (MS). GC separates component according to the difference in the moving speed of the vaporized sample through the column. In the official analytical method for dioxins, each isomer of dioxins is determined by the GC / HRMS method.

dioxin_pcb_img06.png
Figure 4 Dioxin analysis using GC/MS

 

Pretreatment reagents for dioxin analysis are listed as follows;

dioxin_pcb_img07.png

※Unless otherwise stated, reagents are required to have the quality of pesticide residue analysis. In the case of solvents, quality that guarantees that the content of dioxins is below the standard value is required by the test after concentration.

 

2. Quadrupole mass spectrometer (QMS)

GS is also used in simple methods for the analysis of dioxins as in the GC / HRMS method. However, low-resolution mass spectrometers such as quadrupole type and ion trap type are used. Quadrupole mass spectrometer (QMS) comprises four parallel cylindrical metal rods, which are charged by direct current. These rods scan sample ions based on their mass-to-charge ratio. This analysis method uses the same reagents as in GC/HRMS.

dioxin_pcb_img08.png
Figure 5 QMS

 

3. Bioassays

Bioassay is used to estimate the quantity, compounds, and efficacy of substances from the reaction of subjects, such as animals, plants, tissues, stimulated by them.

The pretreatment for bioassay is a method of extracting and cleaning up by multi-layer silica gel column treatment in the same way as the official method. There are two methods, using living tissues such as reporter gene assay and a toolkit composed by antigens reagents, such as enzyme immunoassay.

 

4. Enzyme Immunoassay (EIA) using anti-dioxins antibodies

Enzyme Immunoassay is used for an immunological measurement based on antigen-antibody reactions. This analysis method uses antibodies reacting specifically with dioxins.

 

References

  1. Liu, G., Zheng, M., Cai, Z., Wu, Y., Jiang, G.:Trends. Analyt. Chem., 46, 178 (2013).
    DOI: org/10.1016/j.trac.2012.05.012
  2. Liu, X., Fiedler, H., Gong, W., Wang, B., Yu, G.:Front. Environ. Sci. Eng., 12, 1 (2018).
    DOI: org/10.1016/j.trac.2012.05.012
  3. Samara, F., Gullett, B.K., Harrison, R. O., Chu, A,. Clark, G.C.:Environ. Int., 35, 588 (2009).
    DOI: org/10.1016/j.envint.2008.11.003
  4. Batey, J.H.:Vacuum, 101, 410 (2014).
    DOI: org/10.1016/j.vacuum.2013.05.005
  5. Fujimori, T., Kawamoto K.:J. Mater. Cycles Waste Manag., 30, 201 (2019).
    DOI: org/10.3985/mcwmr.30.201

 

Related Pages

Author: E. Leung

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