© Benaki Phytopathological Institute
1
Laboratory of Pesticide Science, Agricultural Universi-
ty of Athens, Iera Odos 75, GR-118 55 Athens, Greece.
2
Faculty of Applied Biology and Biotechnology, De-
partment of Biology, University of Crete, GR-714 09
Heraklion, Greece
.
3
Pesticides Residues Laboratory, Department of Pes-
ticides Control and Phytopharmacy, Benaki Phyto-
pathological Institute, 8 St. Delta str., GR-145 61 Kifis-
sia (Athens) Greece.
Corresponding author:
Hellenic Plant Protection Journal
6:
69-82, 2013
Biodegradation of diazinon by the epiphytic yeasts
Rhodotorula glutinis
and
Rhodotorula rubra
E.D. Bempelou
1,3
, J.G. Vontas
2
, K.S. Liapis
3
and V.N. Ziogas
1
Summary
The capability of the epiphytic yeasts
Rhodotorula glutinis
and
Rhodotorula rubra
to biode-
grade diazinon in pure cultures and tomato fruits was investigated. Higher biodegradation rates were
observed as the concentration of diazinon and the inoculum of the microorganisms were increased,
and the yeasts proved to be more active at 25
o
C and 15
o
C. The presence of glucose in the mineral nu-
trient medium, as an extra source of carbon, delayed the biodegradation by
Rh. glutinis
, while
Rh. ru-
bra
biodegrade diazinon faster in the presence of glucose. The detection and quantification of diazi-
non and its degradation product 2-isopropyo-6-methyl-4-pyrimidinol (IMP) were achieved successful-
ly in the LC-MS/MS chromatographic system. The in vitro enzymatic assays applied suggested that glu-
tathione-S-transferases may be involved in the biodegradation of diazinon, a fact that was further en-
hanced after the addition of the synergists triphenyl phosphate, diethyl maleate and piperonyl butox-
ide in the biodegradation trials. The decrease of diazinon residues on tomato fruits confirmed the cor-
responding on pure cultures, resulting in the suggestion that the yeasts
Rh. glutinis
and
Rh. rubra
can
possibly be used successfully for the removal or detoxification of diazinon residues ontomatoes.
Additional keywords:
biodegradation, diazinon, epiphytic yeasts, glutathione-S-transferases, synergists
Introduction
The excessive and frequent application of
pesticides in agricultural practice has result-
ed in high levels of pesticide residues accu-
mulated on vegetables. This matter poses a
potential health risk to consumers (Bologne-
si and Morasso, 2000), particularly in coun-
tries where highly toxic insecticides are still
in use. An increased interest in the develop-
ment of means for removing pesticide resi-
dues from vegetables, using environmental
friendly approaches, such as microorgan-
isms or recombinant enzyme systems has
been observed.
Diazinon,
[Ο, O-diethyl O-[6-methyl-2-(1-
methylethyl)-4-pyrimidinyl] ester,
has mainly
been used extensively as an insecticide or
nematicide for the control of a broad range
of insects and pests, playing a distinguished
role in agriculture and veterinary. It is a non
systemic pesticide with action through
stomach or suffocation. The main paths of
its degradation in the environment are ox-
idation in air (Schomburg
et al.
, 1991; Seiber
et al.
, 1993) and hydrolysis, photolysis and
biodegradation in water and soil (Domagal-
ski and Kuivila, 1993; Frank
et al.
, 1991; How-
ard, 1991). The half-life of diazinon in plants
has been measured from 1 to 14 days while
in tissues with high fat concentration has
been found to be more persistent (Bartch,
1974). The corresponding time in animals is
too short with a maximum of 12 hours half-
life. The pesticide is rapidly excreted though
urine and feces, with the 70% of the total ex-
cretion to be consisted of metabolites (US
Public Health Service, 1995). Moreover, di-
azinon has an intermediate toxicity to mam-
mals and may affect the central nervous
system, the cardiovascular system and the