11.10.2013 Views

2. ENVIRONMENTAL ChEMISTRy & TEChNOLOGy 2.1. Lectures

2. ENVIRONMENTAL ChEMISTRy & TEChNOLOGy 2.1. Lectures

2. ENVIRONMENTAL ChEMISTRy & TEChNOLOGy 2.1. Lectures

SHOW MORE
SHOW LESS

You also want an ePaper? Increase the reach of your titles

YUMPU automatically turns print PDFs into web optimized ePapers that Google loves.

Chem. Listy, 102, s265–s1311 (2008) Environmental Chemistry & Technology<br />

P59 DETECTION OF FOREIGN ORGANIC<br />

SubSTANCES IN wATER AND bIOLOGICAL<br />

SAMPLES<br />

e. SAVELIEVA, n. KORYAGInA, n. KHLEBnIKOVA,<br />

n. GOnCHAROV and A. RADILOV<br />

Research Institute of Hygiene, Occupational Pathology and<br />

Human Ecology, Saint-Petersburg, Russia,<br />

esavelieva59@mail.ru<br />

Introduction<br />

The chemical analysis of biomedical samples (bodily<br />

fluids, tissues) aimed at revealing exposure to toxic chemicals<br />

(TCs) can be directed to the following targets:<br />

(i) TCs themselves, when their metabolism is slow<br />

enough,<br />

(ii) Low-molecular metabolites of TCs,<br />

(iii) High-molecular adducts of TCs with proteins.<br />

Right choice of target (marker) with account for the life<br />

cycle of a TC (adsorption–distribution – metabolism – excretion)<br />

predetermines success of analysis. The targets (i) and<br />

(ii) are more convenient to determine by conventional GC-<br />

MS methods but are unsuitable for retrospective analysis in<br />

view of their short life time in the organism. We developed<br />

procedures for the determination in biomedical samples of all<br />

the three groups of biomarkers of TCs.<br />

Results and Discussion<br />

Direct analysis of a TC in biomedical samples was considered<br />

to be a rational approach in toxicokinetic research<br />

on fluoroacetic acid, one of the most potent metabolic poinsons<br />

(FAA). Salts of FAA are still used in some countries for<br />

rodent population control; deadly poisoning of humans and<br />

farm animals was also described. At our laboratory, procedures<br />

for the determination of O-alkyl esters of methylphosphonic<br />

acid (low-molecular metabolites of organophosphorus<br />

warfare agents, OPWAs) and thiodiglycol (metabolite of<br />

sulfur mustard) were also developed. These metabolites are<br />

products of both biogenic and abiogenic hydrolysis of the<br />

parent agents, and, therefore, their determination in environmental<br />

samples is actual for retrospective analysis aimed at<br />

establishing the fact and degree of environmental pollution<br />

with the corresponding agents. Of particular importance for<br />

forensic analysis are universal procedures suitable both for<br />

water and for biological fluids. We developed universal procedures<br />

for the determination of FAA, methylphosphonic acid<br />

(MPA), ethyl MPA (marker of VX), isopropyl MPA (marker<br />

of sarin), isobutyl MPA (marker of Russian VX), pinacolyl<br />

MPA (soman marker), and thiodiglycol in water, urine, and<br />

blood plasma.<br />

For retrospective establishment of exposure to TCs,<br />

procedures for the determination of reactivation products<br />

of blood plasma butyryl cholinesterase (BChE) inhibited by<br />

OPWAs and of thiodiglycol isolated by alkaline hydrolysis<br />

from albumin adducts. These procedures all are based on GC/<br />

MS combined with solid-phase microextraction (SPME).<br />

s450<br />

Solid-phase microextraction is a unique method that<br />

allows one to combine on a single stage extraction from a<br />

matrix, concentration, and injection of a sample. SPME offers<br />

a great advantage of analyzing the whole sample rather<br />

than its aliquot, and, therefore, is more than about an order<br />

of magnitude more sensitive compared with traditional separation<br />

and concentration methods. SPME poses no threat of<br />

contamination of a GCMS system by matrix components. Of<br />

key importance for successful SPME analysis is right choice<br />

of microfiber, conditions for sorption (temperature, time,<br />

sample mixing mode, ionic strength of analyzed solution)<br />

and desorption (temperature, delay time).<br />

Therefore, in developing an SPME procedure, one<br />

should optimize the following parameters:<br />

•<br />

•<br />

•<br />

•<br />

Type of microfiber<br />

Sorption and thermodesorption temperatures of target<br />

analytes<br />

Sorption and thermodesorption times<br />

Ionic strength of the solution.<br />

Before GC/MS analysis nonvolatile target compounds<br />

were derivatized either in situ with subsequent concentration<br />

of the volatile derivative on microfiber (analysis for FAA)<br />

or directly on microfiber with vapors of derivatizing agents<br />

(analysis for MPA and its O-alkyl esters).<br />

In what follows we schematically represent certain of<br />

the mentioned procedures. Fig. 1. shows the block scheme of<br />

the determination of sodium fluoroacetate in various media.<br />

In view of the fact that the volatile derivative, ethyl fluoroacetate,<br />

is sampled from equilibrium vapor, the sample matrix<br />

scarcely affects the results of analysis. The developed procedure<br />

is universal and can be applied both for control of drinking<br />

water and for toxicokinetic and forensic investigations.<br />

Fig. 1. Block scheme of the unified procedure for the determination<br />

of sodium fluoroacetate in water and biomedical samples<br />

by SPME-GCMS<br />

The detection limits are 0.001 mg ml –1 for drinking<br />

and natural waters, 0.01 mg ml –1 for blood plasma, and<br />

0.01 mg ml –1 for organ homogenates (without recounting for<br />

dry weigh). The procedure is described in detail in ref. 1 .<br />

For the determination of the low-molecular metabolites<br />

of organophosphorus warfare agents, MPA and its alkyl

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!