Journals / Atmospheric Pollution Research / 2016 / Cilt: 7 - Sayı: 4

Occurrence of chlorpyrifos in the atmosphere of the Araucanía Region in Chile using polyurethane foam-based passive air samplers

Pages
706–710
DOI
—
🏛️Bibliographic metadata and full text access for this article are provided via DergiPark.
DergiPark Record ↗
✨

AI Summary & Key Takeaways

AI Insight
⚡ TL;DR(Too Long; Didn't Read)

These results provide initialdata for CPF in the Chilean atmosphere and contribute new information to understanding distribution ofCPF in Chilean environments.

📌 3 Key Takeaways

🎯
Objective & Hypothesis:Little is known regarding the use and ambient levels of pesticides in Chilean agricultural regions.Chlorpyrifos (CPF) is one of the most used active ingredients in Chile and in the world.
📊
Key Findings & Data:In this study,PUF disk passive air samples were deployed during ~one year in two areas, Angol (5 sites) and Villarrica(2 sites), in the Araucanía Region.
💡
Conclusion & Impact:These results provide initialdata for CPF in the Chilean atmosphere and contribute new information to understanding distribution ofCPF in Chilean environments.
🔬Design:Research Article
📍Scope:2008 Verileri
⚙️Variables:Domain Parameters

Özet

Little is known regarding the use and ambient levels of pesticides in Chilean agricultural regions.Chlorpyrifos (CPF) is one of the most used active ingredients in Chile and in the world. However, fewinvestigations have been conducted to understand its environmental distribution and fate. In this study,PUF disk passive air samples were deployed during ~one year in two areas, Angol (5 sites) and Villarrica(2 sites), in the Araucanía Region. The concentration in air of CPF ranged from ten to thousands of pg m3(20e14 600). The highest CPF concentrations were detected at the Angol sites (~14 600 pg m3) duringperiod 2 (AugusteDecember 2008). These results were higher by a factor of ~10e15 than those detectedin Villarica sites (~2000 pg m3) in period 1 (AprileJuly 2008). Seasonal CPF variations were observed, atboth sites, within the sampling periods. Air back trajectory analyses showed that air masses from nearbyagricultural zones contributed most of the CPF detected in Angol sites when the wind speed was low andat Villarrica when those sources were likely located north of the VMA site. These results provide initialdata for CPF in the Chilean atmosphere and contribute new information to understanding distribution ofCPF in Chilean environments.

🔖

Cite This Article

POZO, K., LLANOS, Y., ESTELLANO, V. H., CORTES, S., JORQUERA, H., GERLİ, L., POZO, K., ENCİNA, F., PALMA, R., FOCARDİ, S. (2016). Occurrence of chlorpyrifos in the atmosphere of the Araucanía Region in Chile using polyurethane foam-based passive air samplers. Atmospheric Pollution Research, Cilt: 7 - Sayı: 4, 706–710. https://ajindex.com/articles/351535

References (2)

  1. Barra, R., Carmi, J., 1995. A simple method for extraction and GC-ECD analysis of chlorpyrifos from water and environmental samples. J. High Resolut. Chromatogr. 18, 194e195. Bogdal, C., Abad, E., Abalos, M., van Bavel, B., Hagberg, J., Scheringer, M., Fiedler, H., 2013. Worldwide distribution of Persistent Organic Pollutants in air - results of air monitoring by passive air sampling in five continents. Trends Anal. Chem. 46, 2012. BCN, 2015. Biblioteca del Congreso Nacional de Chile. www.bcn.cl/ (access May 2015).
  2. Briceno, G., Fuentes, M.S., Palma, G., Jorquera, M.A., Amoroso, M.J., Diez, M.C., 2012. ~ Chlorpyrifos biodegradation and 3,5,6-trichloro-2-pyridinol production by actinobacteria isolated from soil International. Biodeterior. Biodegrad. 73, 1e7. Copaja, S., Vergara, R., Bravo, H., 2014. Bioavailability of chlorpyrifos in wheat plants (Triticum aestivun). Agric. Sci. 5, 660e667. Draxler, R., Hess, G.D., 1998. An overview of the HYSPLIT_4 modelling system for trajectories, dispersion, and deposition. Aust. Meteorol. Mag. 47, 295e308. Duramad, P., Tage, r I.B., Leikauf, J., Eskenazi, B., Holland, N.T., 2006. Expression of Th1/Th2 cytokines in human blood after in vitro treatment with chlorpyrifos, and its metabolites, in combination with endotoxin LPS and allergen Der p1. J. Appl. Toxicol. 26, 458e465. European Food Safety Authority, 2013. International framework dealing with human risk assessment of combined exposure to multiple chemicals. EFSA J. 11 (7), 3313 [69 pp.] doi: 10.2903/j.efsa.2013.3313. SCIENTIFIC REPORT OF EFSA International Frameworks Dealing with Human Risk Assessment of Combined Exposure to Multiple Chemicals1, European Food Safety Authority2,3. Parma, Italy. EFSA Journal 2013;11(7):3313. Estellano, V.H., Pozo, K., Efstathiou, C., Pozo, K., Corsolini, S., Focardi, S., 2015. Assessing levels and seasonal variations of current-use pesticides (CUPs) in the Tuscan atmosphere, Italy, using polyurethane foam disks (PUF) passive air samplers. Environ. Pollut. 205, 52e59. Fan, A., Hopke, P.K., Raunemaa, T.M., Oblad, M., Pacyna, J.M., 1995. A study on the € potential sources of air pollutants observed at Tjorn, Sweden. Environ. Sci. € Pollut. Res. 2, 107e115. Gao, N., Cheng, M.D., Hopke, P.K., 1993. Potential source contribution function analysis and source apportionment of sulfur species measured at Rubidoux, CA during the Southern California Air Quality Study, 1987. Anal. Chim. Acta 277, 369e380. Gouin, T., Shoeib, M., Harner, T., 2008a.