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"The future will depend on our wisdom not to replace one poison with another."
National Pediculosis Association®, Inc.


MONITORING WITH AN ELECTRONIC NOSE OF LINDANE AND NITROBEZENE CONTAMINATED WATER

R. E. Baby, A. Bucari, M. Cabezas and N. E. Walsöe de Reca

PRINSO (PRograma de INvestigaciones en SOlidos)
CITEFA-CONICET

Zufriategui 4380. Villa Martelli (1603) Buenos Aires

Abstract

The advances in the technology of multisensors arrays and neural computation allow the development of the "electronic noses" which can discriminate compounds by their odours playing a fundamental role in the quality control of food, packaging, perfumes, pharmaceuticals, cosmetics, chemicals, textil fibres, etc as well as in the field of the environmental monitoring.

In this work, the MOSES II (MOdular SEnsor System) "electronic nose" was employed. Each module of sensors is a self-contained unit which can be exchanged by the user since there is not an unique or ideal sensor system. Contrary to the classical analysis tools as gas chromatography or mass spectrography, the MOSES II does not attempt to separate a gas mixture into its individual components, rather, a "fingerprint" of an odour is taken. The equipment is particularly suitable for objective and reproducible odour comparison.

The aim of this paper was to discriminate low concentrations (ppm) of lindane and nitrobenzene in water by the odour since contaminating residues of insecticides and the leather manufacture industry (phenols, nitrobenzene, anilines) are often thrown into streams or rivers in spite of generating a real danger for the population health and for the survivence of fishes and plants. Combining the odour detection with chemical analysis, it was possible to "calibrate" the equipment response and to obtain also a quantitative "discrimination" of contaminants.

www.systems.org/HTML/Environmental_Studies/es-v01/baby/Abstract.htm


Biorestoration of PCB and Lindane Contaminated Soil.

T. PHILLIPS1*, L.A. BEAUDETTE2, K. SHAW1, A. SEECH1, H. LEE2 AND J.T. TREVORS.2  1Grace Bioremediation Technologies, Mississauga, Ontario and 2University of Guelph, Guelph, Ontario. Email: tphillip@uogeulph.ca

Polychlorinated biphenyl- (PCB) and hexachlorocyclohexane (alpha, beta, delta-HCH; gamma-HCH or Lindane) were tested for their biodegradability in contaminated soils using Grace Bioremediation Technologies patented soil amendment technology. Soil microcosms were prepare in mason jars with the soil being cycled through oxic/anoxic cycles.

--HCH-contaminated soil amended with Daramend® technology and Fe resulted in a total HCH loss of 92%. Forty percent greater then the control.
--Lindane (gamma-HCH), a known persistent pesticide, was reduced by 95% in the total HCH loss.
--No significant loss of PCBs was observed using Grace Bioremediation Technologies patented amendment technology as compared to the controls.
 
EMp7

http://www.umanitoba.ca/outreach/csm/posters_and_talks.htm#LINDANE


FATAL ACUTE POISONING WITH LINDANE INSECTICIDE - A CASE REPORT

Pinho Marques E.G., Oliveira M.M.F., Monsanto P.V., Proenca P., Castanheira F., Castanheira A.M., Avila M.T.

Servicos de Toxicologia Forense Instituto de Medicina Legal de Coimbra, Largo da Sé Nova, 3000 Coimbra, Portugal

Lindane (g-hexachlorocyclohexane) is a organochlorine insecticide. Acute intoxications by this pesticide are not frequent in Portugal.
This paper describes analytical methods for lindane determination in biological samples by gas chromatography with electron capture detection (GC/ECD) and mass spectrometry detection (GC/MSD). A liquid-liquid extraction was performed. The purification was performed using different solvents and by chromatography column. The limit of detection was approximately 0.001 µg/mL or 0.01 µg/g by GC/ECD and 0.01 µg/mL or 0.1 µg/g by GC/MSD. The recoveries ranged from 70.1 to 89.2%, and the coefficients of variation were generally below 5% by GC/ECD and 10% by GC/MSD. This method was used in toxicological analyses performed in the fatal poisoning of a woman. Lindane concentrations were 16.4 µg/g, 1.61 µg/mL, 1.90 µg/g and 1.92 µg/g for stomach, blood, liver and kidney, respectively.
In cases of acute poisoning it is not necessary to use the GC/ECD technique, that required cleanest extracts in spite of this method has shown more precision.

http://www.tiaft.org/tiaft97/proceedings/abstract/posters/135.html


Clinical Laboratory Methods:

GAMMA-HCH &/OR METABOLITES WERE DETERMINED IN MICROBIAL CULTURES, URINE, TISSUES & HUMAN BLOOD BY GAS CHROMATOGRAPHY. NITROGEN WAS CARRIER GAS, FLAME IONIZATION & ELECTRON CAPTURE DETECTORS WERE USED.
[MACHOLZ R ET AL; Z GESAMTE HYG IHRE GRENZGEB 29 (6): 336-9 (1983)]**PEER REVIEWED**

EGGS BY GC/THERMIONIC DETECTION: FINSTERWALDER CE; J ASSOC OFF ANAL CHEM 59: 169 (1976). RAT SERUM BY PC, GC/ECD, DETECTION LIMIT 15 NG/L: FRANKEN JJ, LUYTEN BJM; J ASSOC OFF ANAL CHEM 59: 1279 (1976).
[IARC. Monographs on the Evaluation of the Carcinogenic Risk of Chemicals to Man. Geneva: World Health Organization, International Agency for Research on Cancer,1972-PRESENT. (Multivolume work).,p. V20 209 (1979)]**PEER REVIEWED**
TOXNET


Recently, our laboratory identified the important role the ovary performs in regulating drug transfer into developing egg yolks (Donoghue et al., 1996). Yolks develop in the ovary over a period of months and, even when contaminant transfer was limited to just a 24-hour period, yolks that are weeks to months from ovulation incorporated and stored residues. Interestingly, the patterns of residue transfer into yolks were similar for different types of contaminants. In separate, replicated studies, we determined that two dissimilar classes of antibiotics (ampicillin or oxytetracycline) or the pesticide, lindane, all had similar patterns of residue uptake into developing egg yolks. This potentially universal physiological regulation of residue transfer into egg yolks has been used to develop the following mathematical prediction model for residue transfer for all types of chemical compounds. Our model is as follows:

I+j-1

Pk

k=I

It is beyond the scope of this article to define and give examples of our model, but for interested readers, this information can be obtained from our paper in Journal of Food Protection (Donoghue, et. al., 1997; in press) or by contacting the author. FDA MEDWATCH

http://www.fda.gov/cvm/fda/infores/fdavet/1998/0198fdavet.html


Doctor's Data, Inc. is an independent reference laboratory providing data on levels of toxic and essential elements in hair, and elements, amino acids, and metabolites in blood and urine.

http://www.doctorsdata.com/DEFAULT.HTM


Accu-Chem Laboratories, Richardson, TX: (972) 234-5412 or (800) 451-0116

National Medical Services, Willow Grove, PA: (215) 657-4900 or (800) 522-6671

Antibody Assay Laboratories, Santa Ana, CA: (714) 972-9979 or (800) 522-2611

 

 

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