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2. ENVIRONMENTAL ChEMISTRy & TEChNOLOGy 2.1. Lectures

2. ENVIRONMENTAL ChEMISTRy & TEChNOLOGy 2.1. Lectures

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Chem. Listy, 102, s265–s1311 (2008) Environmental Chemistry & Technology<br />

L04 COMPLEx ESSESSMENT OF<br />

ORGANOPhOSPhATES LOw DOSE<br />

ChRONIC ExPOSuRE ON ENDOThELIuM,<br />

MACROPhAGES, PLATELETS AND<br />

ESTERASES<br />

e. ERMOLAEVA, n. GOnCHAROV, A. RADILOV,<br />

L. GLASHKInA, I. MInDUKSHEVa , P. AVDOnInb ,<br />

I. DOBRYLKO and V. REMBOVSKIY<br />

Research Institute of Hygiene, Occupational Pathology and<br />

Human Ecology, Saint-Petersburg, Russia,<br />

aI. M.Sechenov Institute of Evolutionary Physiology and Biochemistry,<br />

Saint-Petersburg, Russia,<br />

bN. K. Koltzov Institute of Developmental Biology, Moscow,<br />

Russia,<br />

nvgoncharov@mail.ru<br />

Introduction<br />

Morphofunctional disturbances of circulation in rat<br />

embryos intoxicated by derivatives of organophosphates<br />

(OP), a role of endothelium directly affected by OP under<br />

acute intoxications 1,2 , and various data on the role of endothelium<br />

in development of peripheral neuropathies of various<br />

genesis 3,4,5 were the basis for consideration of endothelium<br />

as one of the main targets under chronic intoxication with OP.<br />

In this research work, an attempt has been undertaken to clarify<br />

an impact of circulatory disturbances, the cellular component<br />

of haemostasis, and neuropathy target esterase (nTE)<br />

activity upon reaction of rat organism under intoxication with<br />

low doses of OP.<br />

Materials and Methods<br />

In these experiments diisopropylfluorophosphate (DFP),<br />

which can induce the delayed polyneuropathy, and paraoxon<br />

s297<br />

which has no such effect, were applied with drinking water<br />

at doses 10 –2 mg kg –1 (1/100 LD 50 ) and 10 –4 mg kg –1 (1/10,000<br />

LD 50 ). The intoxication was conducted daily 5 times in a week<br />

for 3 months. Esterases of choline and non-choline substrate specificity<br />

6,7,8,9 were studied; for rat brain, the enzyme activity was<br />

calculated per mg of protein 10 . To investigate the OP effects upon<br />

nADPH-oxidase system, we used the functional state of peritoneal<br />

macrophages with fluorescent microscope and fluorescent<br />

probe dichlorfluorescein diacetate (DCF) 11 . Kinetic parameters<br />

of platelet aggregation were studied by low angle light scattering<br />

technique 12 . The functional activity of endothelium under OP<br />

intoxication was studied with rat aorta by method of endotheliumdependent<br />

relaxation 13,14 . The results obtained were processed by<br />

variation statistics and MS Exсel software.<br />

Results and Discussion<br />

Comparing the level of inhibition of esterases in blood<br />

plasma after 3 months’ intoxication with the OP, we have<br />

found that the residual activity of nTE was much lower than<br />

that of red blood cells’ acetylcholine esterase (AChE). Inhibition<br />

of nTE activity in rat brain 2 months after stopping<br />

intoxication with DFP gives an indirect evidence for development<br />

of neurotoxic effects. Activity of esterases after chronic<br />

intoxication demonstrates a switch of inhibition from one<br />

enzyme to another, embracing both choline specific and nonspecific<br />

esterases. It is noticeable that the most prolonged<br />

neurotoxic effect (20–30 % reduction of nTE activity after<br />

6 months’ period of the post-intoxication recovery) remained<br />

in the platelet-rich plasma (PRP).<br />

The next method demonstrating its efficacy for diagnostics<br />

of the low dose intoxication with OP was estimation<br />

of the level of generation of reactive oxygen species<br />

(ROS) during “respiratory burst” by professional phagocytes<br />

(macrophages). It is a widely known fact that macrophages<br />

Fig. 1. Generation of ROS by mice macrophages after 3 months’ chronic intoxication and 2 and 4 months after cessation of the intoxication<br />

with paraoxon and DFP at doses 10 –4 mg kg –1 (min) and 10 –2 mg kg –1 (max)

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