ORIGINAL ARTICLE
Preliminary study on the use of ozonation for the degradation of dithiocarbamate residues in the fruit drying process: mancozeb residue in blackcurrant is the example used
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1
University of Rzeszów
Faculty of Biology and Agriculture, Ćwiklińskiej 2, 3-601 Rzeszów, Poland
2
University of Rzeszów
Institute of Plant Protection – National Research Institute, Laboratory for Research on Pesticide Residues Gen. M. Langiewicza, 35-101 Rzeszów, Poland
3
University of Rzeszów
Campus branch, Faculty of Biotechnology, Werynia 502, 36-100 Kolbuszowa, Poland
Submission date: 2012-10-07
Acceptance date: 2012-12-12
Corresponding author
Maciej Balawejder
University of Rzeszów
Faculty of Biology and Agriculture, Ćwiklińskiej 2, 3-601 Rzeszów, Poland
Journal of Plant Protection Research 2013;53(1):48-52
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TOPICS
ABSTRACT
In order to reduce the level of dithiocarbamate fungicide mancozeb residues in blackcurrants, two different ozone treatment procedures were evaluated. The first one entailed washing the plant material with an aqueous solution of ozone. This ozone enriched
water solution allowed for a 59% reduction of mancozeb residues, compared with the initial concentration. The latter method was based on the utilization of ozone in a gaseous phase combined with a drying process. In that procedure, samples of blackcurrant fruit were exposed to a 19 ppm ozone concentration, and then the blackcurrants were dried. The utilization of ozone in a gaseous phase permitted a 38% reduction of mancozeb residues, in comparison with the initial concentration. As a result of the combination of both
processes; ozonation and drying, a 58% reduction of mancozeb residues was achieved.
CONFLICT OF INTEREST
The authors have declared that no conflict of interests exist.
REFERENCES (10)
1.
Chiron S., Fernandez-Alba A., Rodriguez A., Garcia-Calvo E. 2000. Pesticide chemical oxidation: State of the art. Water Res. 34 (2): 366–377.
2.
Chmiel Z. 1979. Spektrofotometryczne oznaczanie śladowych pozostałości dwutiokarbaminianów w materiale roślinnym. Chem. Anal. 24: 505–511.
3.
Gana S., Lau E.V., Ng H.K. 2009. Remediation of soils contaminated with polycyclic aromatic hydrocarbons (PAHs). J. Hazard. Mater. 172 (2/3): 532–549.
4.
Hwang E.S., Cash J.N., Zabik M.J. 2002. Degradation of mancozeb and ethylenethiourea in apples due to postharvest treatments and processing. J. Food Sci. 67 (9): 3295–3300.
5.
Masten S.J., Davies S.H.R. 1997. Efficiency of in situ ozonation for remediation of PAH contaminated soils. J. Contam. Hydrol. 28 (4): 327–335.
6.
Podymniak M. 2006. Kryzys w produkcji owoców miękkich. Hasło Ogrodnicze 05.2006: 100–101.
7.
Sadło S., Szpyrka E., Rogozińska K., Rupar J. 2003. Oznaczanie pozostałości ditiokarbaminianów w owocach i warzywach na poziomie 0,01 mg/kg. [Determination of dithiocarbamate residues in fruit and vegetables at the level of 0.01 mg/ kg]. Prog. Plant Protect./Post. Ochr. Roślin 43 (2): 895–897.
8.
Tzortzakis N., Singleton I., Barnes J. 2008. Impact of low-level atmospheric ozone-enrichment on black spot and anthracnose rot of tomato fruit. Postharvest Biol. Tech. 47 (1): 1–9.
9.
Zhang L., Lu Z., Yu Z., Gao X. 2005. Preservation of fresh-cut celery by treatment of ozonated water. Food Control 16 (3): 279–283.
10.
Rozporządzenie Ministra Zdrowia z dnia 16 września 2010 r., w sprawie środków spożywczych specjalnego przeznaczenia żywieniowego Na podstawie art. 26 ust. 1 i ust. 2 pkt 3 ustawy z dnia 25 sierpnia 2006 r. o bezpieczeństwie żywności żywienia (Dz. U. z 2010 r. Nr 136, poz. 914).