全部 标题 作者
关键词 摘要

OALib Journal期刊
ISSN: 2333-9721
费用:99美元

查看量下载量

相关文章

更多...

A Qualitative Study of Residual Pesticides on Cotton Fibers

DOI: 10.1155/2013/253913

Full-Text   Cite this paper   Add to My Lib

Abstract:

Two different methods are utilized for this study. The first method covers the measurement of bioelectrical signals caused by enzymatic inhibition of acetyl cholinesterase (AChE) for the detection of pesticides. Biosensor toxicity analyzer (BTA) was used for the testing and the monitoring of changes in bioelectrical signals caused by the interaction of biological substances, and residues were evaluated. The second method is based on measurement of the oxygen level caused by photosynthetic inhibition of residual pesticides by the interaction with green algae, Scenedesmus (Chlorophyta). Algae growth analyzer (AGA) equipped with miniature sensitive oxygen electrode, a light source and cover to model light and dark phases was used enabling us to follow the lifecycle of algae producing oxygen. The test, conducted under the guideline of faster analogy of DIN 863 toxicity test, alga growth inhibition test (OECD TG 201) was and ISO standard (ISO: 8692). Two samples of cotton were analyzed. Cryogenic homogenization was carried out for sample pretreatment. Soxhlet extraction method (SOX) and ultrasound assisted extraction (USE) were used for extraction. Both methods show reasonable results and can successfully be utilized for the detection of residual pesticides on different types of cotton and especially to compare the classical conventional and organic cotton. 1. Introduction Cotton has always been a major part of the textile industry and today provides almost 38% of the world textile consumption, second only to polyester, which recently took the lead [1]. Cotton production is highly technical and difficult because of pest pressures and environment, for example, drought, temperature, and soil nutritional conditions. The total area dedicated to cotton production accounts for approximately 2.4% of arable land globally, and cotton accounts for an estimated 16% of the world’s pesticide consumption [2]. Around 2.5 million tons of pesticides are used annually, and the number of registered active substances is higher than 500. Humans can be exposed to pesticides by direct or indirect means. Direct or primary exposure normally occurs during the application of these compounds, and indirect or secondary exposure can take place through the environment or the ingestion of food [3]. This is why development of natural biological methods of insect control was initiated. Cotton grown without the use of any synthetically compounded chemicals (i.e, pesticides, fertilizers, defoliants, etc.) is considered as “organic” cotton. It is produced under a system of production and

References

[1]  D. Myers, “Organic cotton,” in Organic Cotton, D. Myers, Ed., Intermediate Technology Publications Limited, London, UK, 1999.
[2]  R. S. Blackburn, “Life cycle and environmental impact,” in Sustainable Cotton Production, L. Grose, Ed., Wood Head Publishing Limited, Cambridge, UK, 2009.
[3]  E. Turiel, “Sample handling of pesticides in food and environmental samples,” in Analysis of Pesticides in Food and Environmental Samples, J. L. Tadeo, Ed., CRC Press, 2008.
[4]  S. Gordon and Y. L. Hsieh, Eds., Cotton: Science and Technology, Wood Head Publishing Ltd, Cambridge, UK, 2007.
[5]  L. Alder, K. Greulich, G. Kempe, and B. Vieth, “Residue analysis of 500 high priority pesticides: better by GC-MS or LC-MS/MS?” Mass Spectrometry Reviews, vol. 25, no. 6, pp. 838–865, 2006.
[6]  A. Naggar, “Clinical findings and cholineste rase levels in children of organ ophosphate s and carbamates poisoning,” European Journal of Pediatrics, vol. 168, pp. 951–956, 2009.
[7]  H. Hu, X. Liu, F. Jiang, X. Yao, and X. Cui, “A novel chemiluminescence assay of organophosphorous pesticide quinalphos residue in vegetable with luminol detection,” Chemistry Central Journal, vol. 4, no. 1, article 13, 2010.
[8]  A. Mulchandani, W. Chen, P. Mulchandani, J. Wang, and K. R. Rogers, “Biosensors for direct determination of organophosphate pesticides,” Biosensors and Bioelectronics, vol. 16, no. 4-5, pp. 225–230, 2001.
[9]  M. L. Hannam, J. A. Hagger, M. B. Jones, and T. S. Galloway, “Characterisation of esterases as potential biomarkers of pesticide exposure in the lugworm Arenicola marina (Annelida: Polychaeta),” Environmental Pollution, vol. 152, no. 2, pp. 342–350, 2008.
[10]  P. Mulchandani, A. Mulchandani, I. Kaneva, and W. Chen, “Biosensor for direct determination of organophosphate nerve agents—1. Potentiometric enzyme electrode,” Biosensors and Bioelectronics, vol. 14, no. 1, pp. 77–85, 1999.
[11]  R. P. Deo, J. Wang, I. Block et al., “Determination of organophosphate pesticides at a carbon nanotube/organophosphorus hydrolase electrochemical biosensor,” Analytica Chimica Acta, vol. 530, no. 2, pp. 185–189, 2005.
[12]  D. G. Buerk, Biosensors: Theory and Applications, Technomic Publishing Company, 1995.
[13]  A. Arvinte, “Development of a pesticides biosensor using carbon-based electrode systems,” in Chemicals as Intentional and Accidental Global Environmental Threats, L. Simeonov and E. Chirila, Eds., pp. 337–343, Springer, 2006.
[14]  J. Ma, “Differential sensitivity to 30 herbicides among populations of two green algae Scenedesmus obliquus and Chlorella pyrenoidosa,” Bulletin of Environmental Contamination and Toxicology, vol. 68, no. 2, pp. 275–281, 2002.
[15]  S. Sánchez-Fortún, F. Marvá, A. D'Ors, and E. Costas, “Inhibition of growth and photosynthesis of selected green microalgae as tools to evaluate toxicity of dodecylethyldimethyl-ammonium bromide,” Ecotoxicology, vol. 17, no. 4, pp. 229–234, 2008.
[16]  L. Barsanti and P. Gualtieri, Algae Anatomy, Biochemistry, and Biotechnology, CRC Press, Boca Raton, Fla, USA, 2006.
[17]  K. Rogers, Ed., Fungi, Algae AND Protists, Britannica Educational Publishing, New York, NY, USA, 1st edition, 2011.
[18]  Z. Perrine, S. Negi, and R. T. Sayre, “Optimization of photosynthetic light energy utilization by microalgae,” Algal Research, vol. 1, no. 2, pp. 134–142, 2012.
[19]  D. Chapman, Ed., Water Quality Assessments, E & Fn Spon, London, UK, 2nd edition, 1996.
[20]  M. Edwards, Green Algae Strategy End Oil Imports and Engineer Sustainable Food and Fuel, Mark R. Edwards, Tempe, Ariz, USA, 2008.
[21]  M. D. Ferrando, E. Sancho, and E. Andreu-Moliner, “Chronic toxicity of fenitrothion to an algae (Nannochloris oculata), a rotifer (Brachionus calyciflorus), and the cladoceran (Daphnia magna),” Ecotoxicology and Environmental Safety, vol. 35, no. 2, pp. 112–120, 1996.
[22]  J. Ma, R. Zheng, L. Xu, and S. Wang, “Differential sensitivity of two green algae, Scenedesmus obliqnus and Chlorella pyrenoidosa, to 12 pesticides,” Ecotoxicology and Environmental Safety, vol. 52, no. 1, pp. 57–61, 2002.
[23]  K. J. Buhl, S. J. Hamilton, and J. C. Schmulbach, “Chronic toxicity of the bromoxynil formulation Buctril to Daphnia magna exposed continuously and intermittently,” Archives of Environmental Contamination and Toxicology, vol. 25, no. 2, pp. 152–159, 1993.
[24]  J. L. Tadeo, “Pesticides: classification and properties,” in Analysis of Pesticides in Food and Environmental Samples, J. L. Tadeo, Ed., CRC Press, 2008.
[25]  A. Mulchandani and R. Rajesh, “Microbial biosensors for organophosphate pesticides,” Applied Biochemistry and Biotechnology, vol. 165, no. 2, pp. 687–699, 2011.

Full-Text

Contact Us

service@oalib.com

QQ:3279437679

WhatsApp +8615387084133