Effects of single or repeated dermal exposure to methyl parathion on behavior and blood cholinesterase activity in rats

The effects of a single or repeated dermal administration of methyl parathion on motor function, learning and memory were investigated in adult female rats and correlated with blood cholinesterase activity. Exposure to a single dose of 50 mg/kg methyl parathion (75% of the dermal LD(50)) resulted in an 88% inhibition of blood cholinesterase activity and was associated with severe acute toxicity. Spontaneous locomotor activity and neuromuscular coordination were also depressed. Rats treated with a lower dose of methyl parathion, i.e. 6.25 or 12.5 mg/kg, displayed minimal signs of acute toxicity. Blood cholinesterase activity and motor function, however, were depressed initially but recovered fully within 1-3 weeks. There were no delayed effects of a single dose of methyl parathion on learning acquisition or memory as assessed by a step-down inhibitory avoidance learning task. Repeated treatment with 1 mg/kg/day methyl parathion resulted in a 50% inhibition of blood cholinesterase activity. A decrease in locomotor activity and impairment of memory were also observed after 28 days of repeated treatment. Thus, a single dermal exposure of rats to doses of methyl parathion which are lower than those that elicit acute toxicity can cause decrements in both cholinesterase activity and motor function which are reversible. In contrast, repeated low-dose dermal treatment results in a sustained inhibition of cholinesterase activity and impairment of both motor function and memory.     

Pharmacokinetics of methyl parathion: a comparison following single intravenous,oral or dermal administration

Assessment of the risks posed by the residential use of methyl parathion requires an understanding of its pharmacokinetics after different routes of exposure. Thus, studies were performed using adult female rats to define the pharmacokinetic parameters for methyl parathion after intravenous injection and to apply the described model to an examination of its pharmacokinetics after single oral or dermal exposure. The pharmacokinetics of methyl parathion after intravenous administration (1.5 mg/kg) were best described by a three-compartment model; the apparent volume of the central compartment was 1.45 liters/kg, clearance was 1.85 liters/h/kg and the terminal half-life was 6.6 h with an elimination constant of 0.50 h(-1). The apparent oral absorption coefficient for methyl parathion (1.5 mg/kg) was 1.24 h(-1), and its oral bioavailability was approximately 20%. The latter likely includes a significant first pass effect. Concentrations of methyl parathion increased during the initial 10-60 min and then declined during the next 15-36 h. After dermal administration (6.25-25 mg/kg), methyl parathion concentrations peaked within 12-26 h and then declined dose dependently. The apparent dermal absorption coefficient was approximately 0.41 h(-1), and only two pharmacokinetic compartments could be distinguished. In conclusion, the pharmacokinetics of methyl parathion are complex and route dependent. Also, dermal exposure, because of sustained methyl parathion concentrations, may pose the greatest risk.     

Parathion and methyl parathion toxicity and metabolism in piperonyl butoxide and diethyl maleate pretreated mice

Pretreatment of male mice with piperonyl butoxide, 400 mg/kg 1 h before challenge with insecticides, resulted in a 40-fold antagonism of the acute i.p. toxicity of methyl parathion but potentiated the toxicity of parathion two-fold. Piperonyl butoxide had no effect on the toxicity of the oxygen analogs of these insecticides, methyl paraoxon and paraoxon. Diethyl maleate (1 ml/kg) depleted liver glutathione by 80% after one hour, potentiated the toxicity of both methyl parathion and methyl paraoxon, and partially counteracted the protective effect of piperonyl butoxide on methyl parathion toxicity. Piperonyl butoxide delayed the onset of brain cholinesterase inhibition by parathion. Studies of the metabolism of the insecticides by liver homogenates in vitro demonstrated that piperonyl butoxide inhibited both the oxidative formation of the oxygen analogs (activation) and oxidative cleavage to p-nitrophenol and dialkylphosphorothioic acid (detoxification). While parathion metabolism was mostly oxidative, methyl parathion metabolism appeared to be predominantly via glutathione-dependent enzymes. Studies of in vitro distribution of the insecticides demonstrated that piperonyl butoxide pretreatment resulted in elevated tissue concentrations of parathion and methyl parathion; however, the rate constant for elimination from plasma for both insecticides was unaffected by piperonyl butoxide. The overall rate of metabolism of methyl parathion in vivo was approximately twice that of parathion. These results suggest that during piperonyl butoxide inhibition of oxidative activation and cleavage, methyl parathion detoxification continues through uninhibited glutathione-dependent pathways of metabolism. The net result is a reduction in the acute toxicity of methyl parathion. Lack of an effective alternate pathway of detoxification may explain the delayed but greater toxicity of parathion in piperonyl butoxide pretreated mice.     

Methyl parathion increases neuronal activities in the rat locus coeruleus

Exposure to organophosphate insecticides induces undesirable behavioral changes in humans, including anxiety and irritability, depression, cognitive disturbances and sleep disorders. Little information currently exists concerning the neural mechanisms underlying such behavioral changes. The brain stem locus coeruleus (LC) could be a mediator of organophosphate insecticide-induced behavioral toxicities since it contains high levels of acetylcholinesterase and is involved in the regulation of the sleep-wake cycle, attention, arousal, memory, and pathological processes, including anxiety and depression. In the present study, using a multi-wire recording technique, we examined the effects of methyl parathion, a commonly used organophosphate insecticide, on the firing patterns of LC neurons in rats. Systemic administration of a single dose of methyl parathion (1 mg/kg, i.v.) increased the spontaneous firing rates of LC neurons by 240% but did not change the temporal relationships among the activities of multiple LC neurons. This dose of methyl parathion induced a 50% decrease in blood acetylcholinesterase activity and a 48% decrease in LC acetylcholinesterase activity. The methyl parathion-induced excitation of LC neurons was reversed by administration of atropine sulfate, a muscarinic receptor antagonist, indicating an involvement of muscarinic receptors. The methyl parathion-induced increase in LC neuronal activity returned to normal within 30 min while the blood acetylcholinesterase activity remained inhibited for over 1 h. These data indicate that methyl parathion treatment can elicit excitation of LC neurons. Such excitation could contribute to the neuronal basis of organophosphate insecticide-induced behavioral changes in human.     

Cytotoxicity of organophosphate anticholinesterases

Summary Organophosphate (OP) anticholinesterases were found to modulate metabolic activities of human neuroblastoma cells and hepatocytes, which was detectable by the Cytosensor? microphysiometer. The nerve gas ethyl-S-2-diisopropylaminoethyl methylphosphorothiolate (VX), at 10 μM, produced significant reduction in cell metabolism within 2 min, as measured by changes in the acidification rate of the medium. The reduction was dose-and time-dependent and irreversible after 4 h of exposure. Two alkaline degradation products of VX produced no cytotoxicity. Exposure for 24 h to 3 μM VX caused 36% and 94% irreversible loss of metabolism in hepatocytes and neuroblastoma cells, respectively. The insecticides parathion and chlorpyrifos stimulated hepatocyte metabolism but inhibited neuroblastoma cells. Their oxons were more active. Exposure of neuroblastoma cells for 4 h to VX, parathion, paraoxon, diisopropylfluorophosphate or chlorpyrifos gave an LC₅₀ of 65, 775, 640, 340, or 672 μM, respectively, whereas 24 h gave an LC₅₀ of 0.7, 3.7, 2.5, 29, and 31 μM, respectively. Preincubation of hepatocytes with phenobarbital enhanced their response to parathion and VX due to metabolic bioactivation. Atropine partially blocked the effects of VX and paraoxon on both cell types, which suggests the involvement of a muscarinic receptor as the target for cytotoxicity. There was no correlation between OP in vivo neurotoxicity and in vitro cytotoxicity. It is suggested that the former results from their cholinesterase inhibition, while the latter results from action on different targets and requires much higher concentrations.     

Neuromuscular dysfunction induced by acetylcholinesterase inhibition.

The organophosphate cholinesterase inhibitor paraoxon produces a dose-dependent necrosis in rat skeletal muscle fibers after a single administration. The pathology, which is initiated at the motor end-plate region, is evident as early as 30 minutes after paraoxon administration and is characterized by dilated mitochondria, expanded sarcoplasmic reticulum, fused and widened subsynaptic folds, and coated cleft vesicles. By 24 hours, a generalized breakdown of muscle fiber architecture is evident with an accompanying infiltration of phagocytes. Electrophysiological studies have shown that paraoxon increases neurotransmitter release and causes spontaneous and impulse-related antidromic nerve activity, both of which can be reduced significantly by reactivation of inhibited acetylcholinesterase (AChE) with pyridine-2-aldoxime methiodide. The severity of the myopathy has been found to be positively correlated to the degree and duration of AChE inhibition. It appears that 2 hours of inhibition, with a critical loss in activity, viz., 85%, is necessary to initiate severe muscle fiber necrosis. Prior nerve transection prevents myopathic development and current data support the hypothesis that the induction of skeletal muscle fiber necrosis is triggered by inhibition of a neurally regulated fraction of AChE.     

Differential modulation of organophosphate-sensitive muscarinic receptors in rat brain by parathion and chlorpyrifos

We previously reported similar levels of brain cholinesterase inhibition but marked differences in toxicity following acute maximum tolerated doses of the organophosphate pesticides parathion and chlorpyrifos. Because extensive acetylcholinesterase inhibition often induces compensatory changes in cholinergic receptor populations, we compared the effects of parathion and chlorpyrifos on brain muscarinic receptors. Adult male rats were treated with vehicle or the maximum tolerated dose of parathion (18 mg/kg, sc) or chlorpyrifos (279 mg/kg, sc) and observed for signs of acute toxicity. Similarly treated animals were sacrificed at 2, 7, or 14 days after treatment for measurement of cholinesterase activity and binding to the nonselective muscarinic antagonist [³H]quinuclidinyl benzilate, the M2-preferential antagonist [³H]AFDX-384, and the high-affinity agonist [³H]cis-methyldioxolane. More acute toxicity was noted after parathion treatment. Both insecticides caused similar levels (> 85%) of maximal cholinesterase inhibition and reductions (up to 55%) in atropine-sensitive quinuclidinyl benzilate binding (i.e., total muscarinic receptors) and [³H]AFDX-384 binding in cortex and striatum. Parathion also reduced, whereas chlorpyrifos increased, total muscarinic receptor binding and [³H]AFDX-384 binding in the cerebellum. When tissues were preincubated with paraoxon (10 μM), radiolabeling of a subset of quinuclidinyl benzilate binding sites was blocked and the apparent densities of these organophosphate-sensitive receptors in all three tissues were decreased (16% maximal) by parathion but increased (up to 37%) by chlorpyrifos. Similarly, parathion decreased whereas chlorpyrifos increased [³H]cis-methyldioxolane binding sites in all three brain regions. We propose that differential modulation of these organophosphate-sensitive muscarinic receptors contributes to differences in acute toxicity following exposure to these pesticides.     

Some aspects of neurophysiological basis of insecticide action.

When the insecticide parathion was administered to awake, unrestrained rats with chronically implanted brain electrodes, it was observed that the latency of the averaged flash-evoked potential in the visual cortex and superior colliculus was increased and the amplitude was decreased 2 to 4 hours later with responses returning to pretreatment levels about 8 hours after administration. Similarly, after administration of several dose levels of parathion in the rat, durations of phases of the maximal electroshock seizure (MES) pattern were altered to the greatest extent 4 hours later, but effects disappeared at 24 hours. These effects of parathion on the MES and evoked potentials coincided with a fall in blood and brain acetylcholinesterase (AChe) activities but disappeared after AChe inhibition had reached its peak and stabilized. Brain AChe activities required 2 to 4 weeks for recovery whereas blood AChe activity recovered in 1 week following inhibition by parathion (at least 2 mg/kg body weight). Studies in the monkey demonstrated similar results. Because these measurements of central nervous system function returned to normal despite continued inhibition of AChe activity, the results are interpreted to mean either that adaptation of evoked potentials or MES responses to prolonged AChe inhibition can occur in the rat and monkey after parathion administration or that some of the effects of parathion do not depend on AChe inhibition. Administration of DDT (100 mg/kg by mouth) to awake, unrestrained rats markedly increased the amplitude of spontaneous electrical activity in the cerebellum, whereas there was much less effect on electrical activity recorded simultaneously in the occipital cortex, reticular formation, and medial geniculate body. Similarly, DDT administration had marked effects on the averaged, sound evoked potential recorded in the cerebellum; DDT caused the appearance and increased the amplitude of an early component of this response not usually present during control recordings. Sound-evoked potentials recorded simultaneously from the frontal and occipital cortex and reticular formation were affected less or were decreased in amplitude by administration of DDT.     

Detoxication of paraoxon by rat liver homogenate and serum carboxylesterases and A-esterases.

Paraoxon, the active metabolite of parathion, can be detoxified through a noncatalytic pathway by carboxylesterases and a catalytic pathway by calcium-dependent A-esterases, producing p-nitrophenol as a common metabolite. The detoxication patterns of carboxylesterases and A-esterases were investigated in vitro in the present study with a high tissue concentration (75 mg/mL rat liver homogenate or 50% rat serum solution) to more closely reflect enzyme concentrations in intact tissues. A final paraoxon concentration of 3.75 microM was used to incubate with liver homogenates or serum solutions for 5 seconds or 3, 5, 15, or 25 minutes; also 0.625, 1.25, 2.5, 3.125, 3.75, or 5.0 microM paraoxon (final concentration) was incubated with liver homogenates or serum solutions for 15 minutes. Phenyl saligenin cyclic phosphate and EDTA were used to inhibit carboxylesterases and A-esterases, respectively. Significant amounts of p-nitrophenol were generated with or without either inhibitor during a 15 minute incubation with paraoxon from low (0.625 microM) to high (5.0 microM) concentrations. The amount of p-nitrophenol generated via carboxylesterase phosphorylation was greater than via A-esterase-mediated hydrolysis in the initial period of incubation or when incubating with a low concentration of paraoxon. Plateau shape curves of p-nitrophenol concentration versus time or paraoxon concentration indicated that carboxylesterase phosphorylation was saturable. When incubated for long time intervals or with high concentrations of paraoxon, more p-nitrophenol was generated via A-esterase-mediated hydrolysis than from carboxylesterase phosphorylation. The ratio of paraoxon concentration to tissue amount used in in vitro assays of this study was equivalent to dosing a rat with toxicologically relevant dosages. These in vitro data suggest that both carboxylesterases and A-esterases detoxify paraoxon in vivo; carboxylesterases may be an important mode of paraoxon detoxication in initial exposures to paraoxon or parathion before they become saturated, whereas A-esterases may contribute to paraoxon detoxication in repeated exposures to paraoxon or parathion because they will not become inhibited and will remain catalytically active unlike the carboxylesterases. The importance of carboxylesterases in detoxication of paraoxon was verified by an in vivo study. In rats pretreated with tri-o-tolyl phosphate, an in vivo carboxylesterase inhibitor, brain acetylcholinesterase was significantly inhibited after intravenous exposure to parathion. No significant inhibition of brain acetylcholinesterase was observed in rats pretreated with corn oil.     

Oxidation of cholinesterase-inhibiting pesticides: A simple experiment to illustrate the role of bioactivation in the toxicity of chemicals

A simple undergraduate laboratory experiment that can be used in Biochemistry and Toxicology courses to illustrate the importance of metabolic reactions in the toxicity of chemical substances is reported. It involves the experimental confirmation that oxidized phosphorothionate esters, commonly used as insecticides, are stronger cholinesterase inhibitors and therefore exhibit higher toxicity than do their sulphur analogs starting from which the first are formed by in vivo oxidative desulphuration. Two separated aliquots of a bovine blood sample are incubated with parathion and paraoxon, its oxygen analog, and compared for cholinesterase activity with "normal" blood. Previously, a standard sample of paraoxon was obtained by oxidation of the thiono group of parathion with bromine vapour by reaction TLC. The comparison of the inhibitory capacity of both compounds is made by a colorimetric procedure using acetylthiocholine as substrate of the enzyme and 5,5'-dithiobis-(2-nitrobenzoic acid) as chromogen.     

钩虾胆碱酯酶（ChE）和谷胱甘肽转硫酶（GST）的敏感性和特异性比较研究

研究了有机磷农药甲地基嘧啶流磷,有机氯农药林丹,菊酯类农药氯菊酯,表面活性剂直链苯磺酸钠和重金属Zn对钩虾（Gammarus pulex L.)胆碱酯酶（ChE）和谷胱甘肽转硫酶（GST）活性变化以及毒性影响,结果表明,在暴露24h和48h后,仅有机磷农药甲基嘧硫磷显著抑制胆碱酯的酶的活性,在暴露48h后,有机氯农药林丹和菊酯类农药氯菊酯能显著提高谷胱甘肽转硫酶活性,在暴露24h后,仅梵在导致谷胱甘肽转硫酶明显升高,作为生物标志物,胆碱酯酶比谷胱甘肽转硫酶具有更高的特异性,这两种生物标志物较毒性试验方法具有更高的敏感性。     

Development of a urinary biomarker for exposure to the organophosphate propetamphos: data from an oral and dermal human volunteer study.

Propetamphos is a member of the vinyl phosphate group of insecticides and is mainly used for sheep dipping. There have been no published metabolic studies on the effect of propetamphos in man to date, although the present authors have published the identification of a metabolite. The present paper presents data from a human volunteer study investigating the toxicokinetics of the organophosphorus pesticide propetamphos following oral and dermal exposure. Five volunteers ingested a propetamphos dose of 10 micrograms kg-1 (35 nmol kg-1) body weight. Following a washout of 4 weeks, a 100 mg (356 mumol) dermal dose of propetamphos was applied, occluded to 80 cm2 of the inner forearm, for 8 h to the same five volunteers. In a pilot study (several weeks before the main study), one volunteer also received an occluded dermal dose of 50 mg (178 mumol) propetamphos. Unabsorbed propetamphos on the skin was washed off after 8 h and collected. Blood and urine samples were collected over 30 and 54 h for the oral and dermal exposures respectively. Blood samples were analysed for plasma and erythrocyte cholinesterase. Urine samples were analysed for a urinary metabolite of propetamphos: methylethylphosphoramidothioate (MEPT). Following oral and dermal exposure, peak urinary MEPT levels occurred at 1 and 10-12 h respectively. The apparent urinary elimination half-lives of MEPT had means of 1.7 h (oral exposure) and 3.8 h (dermal exposure). Approximately 40% of the oral dose and 1% of the dermal dose were recovered as urinary MEPT or metabolites, which could be hydrolysed to MEPT. Approximately 90% of the dermal dose was recovered from the skin washings. Data from a volunteer showed that a doubling of the dermal dose resulted in approximately double the concentration of total MEPT. Alkaline hydrolysis of urine samples increased the level of MEPT detected after both oral and dermal doses. The increase was greater and statistically significant (p < 0.001, paired t-test) for the dermal dose. This increase in MEPT suggests the presence of other MEPT-containing metabolites or conjugates. The difference in the increase between oral and dermal doses raises the question of a difference in metabolism between the two routes. No individual showed a significant depression compared with their pre-exposure levels of erythrocyte acetyl cholinesterase or plasma cholinesterase activity for either dosing route. However, on a group basis, there was a statistically significant mean depression in plasma cholinesterase activity at 8 and 24 h for oral exposure, with a maximum mean depression of 7% from pre-exposure levels at 8 h. Hydrolysis of urine samples had the effect of reducing the interindividual coefficient of variation (CV) for total excretion of MEPT following both oral (CV reduced from 36 to 8%) and dermal (CV reduced from 40 to 17%) exposure. The ability to detect and follow the elimination of low doses of propetamphos by measurement of 'total' (after hydrolysis) urinary MEPT suggests it is a suitable biomarker of propetamphos exposure. The comparatively short elimination half-lives suggest a strategy for biological monitoring of occupational exposure based on samples collected at the end of the shift.     

Modulation of the mutagenicity of heterocyclic amines by organophosphate insecticides and their metabolites

People are commonly exposed to organophosphorus ester (OP) insecticides through the treatment of pets, homes, lawns, gardens, workplaces and in commercial agriculture. Aromatic amines are another chemical class with wide human exposure particularly dietary heterocyclic aromatic amines (HAAs). Previously, we reported that specific aromatic amines and ethyl paraoxon (the metabolite of the insecticide ethyl parathion) induced enhanced mutagenic responses in Salmonella typhimurium. In the present study, we demonstrated that the mutagenicity of 2-acetoxyacetylaminofluorene (2AAAF) and the heterocyclic dietary carcinogen 2-amino-1-methyl-6-phenylimidazo(4,5-b)pyridine (PhIP) was enhanced in the presence of the OP insecticides, ethyl parathion or methyl parathion or a metabolite (methyl paraoxon). The mutagenicity of 2-amino-3-methylimidazo-(4,5-f)quinoline (IQ) was increased by methyl parathion and methyl paraoxon but not by ethyl parathion. This mutagenic synergy was expressed in S. typhimurium strain YG1024. Mammalian microsomal activation was required for PhIP and IQ to express mutagenic synergy. Synergistic responses are rarely incorporated in risk assessment models, yet such responses are important in establishing accurate toxicological characteristics of agents. Under real world conditions where people are exposed to a multitude of agents, the results of this study raise a concern about the environmental and public health impacts of OP insecticides.     

Development of a urinary biomarker for exposure to the organophosphate propetamphos: data from an oral and dermal human volunteer study

Propetamphos is a member of the vinyl phosphate group of insecticides and is mainly used for sheep dipping. There have been no published metabolic studies on the effect of propetamphos in man to date, although the present authors have published the identification of a metabolite. The present paper presents data from a human volunteer study investigating the toxicokinetics of the organophosphorus pesticide propetamphos following oral and dermal exposure. Five volunteers ingested a propetamphos dose of 10 μg kg^-1 (35nmol kg^-1) body weight. Following a washout of 4 weeks, a 100mg (356 μmol) dermal dose of propetamphos was applied, occluded to 80cm² of the inner forearm, for 8 h to the same five volunteers. In a pilot study (several weeks before the main study), one volunteer also received an occluded dermal dose of 50 mg (178 μmol) propetamphos. Unabsorbed propetamphos on the skin was washed off after 8 h and collected. Blood and urine samples were collected over 30 and 54 h for the oral and dermal exposures respectively. Blood samples were analysed for plasma and erythrocyte cholinesterase. Urine samples were analysed for a urinary metabolite of propetamphos: methylethylphosphoramidothioate (MEPT). Following oral and dermal exposure, peak urinary MEPT levels occurred at 1 and 10-12 h respectively. The apparent urinary elimination half-lives of MEPT had means of 1.7h (oral exposure) and 3.8 h (dermal exposure). Approximately 40% of the oral dose and 1% of the dermal dose were recovered as urinary MEPT or metabolites, which could be hydrolysed to MEPT. Approximately 90% of the dermal dose was recovered from the skin washings. Data from a volunteer showed that a doubling of the dermal dose resulted in approximately double the concentration of total MEPT. Alkaline hydrolysis of urine samples increased the level of MEPT detected after both oral and dermal doses. The increase was greater and statistically significant (p < 0.001, paired t-test) for the dermal dose. This increase in MEPT suggests the presence of other MEPT-containing metabolites or conjugates. The difference in the increase between oral and dermal doses raises the question of a difference in metabolism between the two routes. No individual showed a significant depression compared with their pre-exposure levels of erythrocyte acetyl cholinesterase or plasma cholinesterase activity for either dosing route. However, on a group basis, there was a statistically significant mean depression in plasma cholinesterase activity at 8 and 24 h for oral exposure, with a maximum mean depression of 7% from pre-exposure levels at 8 h. Hydrolysis of urine samples had the effect of reducing the interindividual coefficient of variation (CV) for total excretion of MEPT following both oral (CV reduced from 36 to 8%) and dermal (CV reduced from 40 to 17%) exposure. The ability to detect and follow the elimination of low doses of propetamphos by measurement of 'total' (after hydrolysis) urinary MEPT suggests it is a suitable biomarker of propetamphos exposure. The comparatively short elimination half-lives suggest a strategy for biological monitoring of occupational exposure based on samples collected at the end of the shift.     

THE INSECTICIDAL MATERIAL IN LEAVES OF PLANTS GROWING IN SOIL TREATED WITH PARATHION

After parathion solutions had been watered on to soil around the roots of cabbage plants with leaves infested with Brevicoryne brassicae, Myzus persicae or Pieris brassicae larvae, these leaves showed a toxic effect on the feeding insects. In comparable experiments, Aphis fabae on leaves of broad bean was not affected at dosages that damaged the plants. The effect on the cabbage plants was observed when the parathion was of the highest degree of purity, as shown by chemical tests and its negligible anticholinesterase activity, although it was greater with commercial grade material. It occurred when all possibility of a fumigant action was excluded.
When the roots of wheat plants were treated with solutions of pure parathion the leaf guttation fluid was toxic to Aëdes aegypti larvae and contained an active anticholinesterase. This was shown to be paraoxon; no parathion could be detected in the fluid. The paraoxon was formed rather slowly from the parathion when the roots and leaves of wheat seedlings were immersed in the solution but not in the presence of compost alone.
In plants treated with pure parathion the translocation of the paraoxon formed under the influence of the roots was sufficient to account for the toxic effects produced. With commercial parathion, analogues or isomers present as impurities may also be translocated. Both these sources of systemic poisons should be borne in mind when considering parathion treatment of greenhouse soil in which food crops are to be grown.     

Effects of sinus gland extract on mandibular organ size and methyl farnesoate synthesis in the crawfish

Eyestalk inhibition of farnesoic acid O-methyl transferase, which mediates the final step of methyl farnesoate synthesis in the mandibular organ of the crawfish Procambarus clarkii, was evaluated. Eyestalk removal caused a 20-100-fold increase in methyl transferase activity 8-12 days following surgery. The surge in activity following eyestalk removal in males was approximately 4 days ahead of that of the females. This was accompanied by a three-fold increase in mandibular organ protein content. Methyl transferase inhibition was accomplished in vitro after only a 15-min exposure to sinus gland extract. The inhibition obtained by injecting animals in vivo was noticeably attenuated 6 h following injection. The contrast of the short-lived inhibition with the growth and prolonged increase following eyestalk removal suggests that the eyestalk exerts both chronic and acute effects on the mandibular organ.     

The effect of high and low dosages of paraoxon in β-naphthoflavone-treated rats

Aliesterases (carboxylesterases) are serine esterases that can serve a protective role for the target acetylcholinesterase (AChE) during organophosphorus insecticide intoxication because the former esterases are alternate phosphorylation sites. The levels of aliesterase activity in liver and plasma and AChE activity in brain regions were investigated after the intravenous administration of paraoxon (P = O) into female rats. The rats were pretreated intraperitoneally with β-naphthoflavone (BNF), which decreases hepatic aliesterase activity following a 3 day in vivo treatment, and/or tri-o-totyl phosphate (TOTP) to inhibit aliesterases. The liver aliesterases were inhibited less by P = O in BNF-treated rats than in control rats, which suggests that either BNF exposure may have resulted in aliesterases that are less sensitive to P = O inhibition or BNF may have altered P = O's availability. The BNF treatment did not seem to alter the degree of inhibition of the brain AChE activity following the low dosage of paraoxon (0.04 mg/kg). However, the brain AChE activity in the P = O/TOTP/BNF-treated rats was lower than that in the P = O/TOTP-treated rats, suggesting that BNF also caused changes in systems affecting the disposition of P = O in addition to the changes in the hepatic aliesterases. At the high dosage of paraoxon (0.12 mg/kg), the AChE and aliesterase activities showed a pattern similar to that of the low dosage. This suggests that the aliesterases, as altered by BNF exposure, even when nearly completely inhibited, did not alter the response of the target enzyme, AChE, and, therefore, the magnitude of the toxic response. © 1997 John Wiley & Sons, Inc. J Biochem Toxicol 11: 263–268, 1997.     

The effects of sublethal concentrations of five organophosphorus insecticides on temperature tolerance, reflexes, and orientation in Gambusia affinis affinis (Pisces: Poeciliidae)

Gambusia affinis were exposed to the insecticides ABATE®, fenthion, chlorpyrifos, methyl parathion, and malathion for 24 h at concentrations of 1, 5, and 10 ppb and for 48 h at 5 ppb. The thermal tolerance was lowered significantly for male and female G. affinis by the toxicants methyl parathion and chlorpyrifos at 5 and 10 ppb with 24 h exposure. Activity was restricted with fish exposed to methyl parathion and chlorpyrifos at concentrations of 10 ppb for 24 h and at 5 ppb for 48 h.     

Motor functions but not learning and memory are impaired upon repeated exposure to sub-lethal doses of methyl parathion

Summary Our previous work showed that repeated exposure to methyl parathion (MP) caused a prolonged inhibition of acetylcholinesterase (AChE) activity (∼80%) and down-regulation of M₁ and M₂ muscarinic receptors (up to 38%) in rats at brain regions, including frontal cortex, striatum, hippocampus and thalamus. In the present neurobehavioral study, we found this repeated MP treatment had suppressant effects on rat’s locomotor activity. However, we observed no evidence of long-term effects of MP on associative learning and memory. Our data demonstrated that repeated exposure to MP caused some functional deficits in CNS, but motor activity and associative learning/memory process might differ in the sensitivity to its toxic effect. The motor dysfunctions in MP-treated rats may be mediated via reciprocal balance between cholinergic and dopaminergic systems at striatum following cholinergic over-stimulation. Our findings also suggest that the CNS deficits induced by repeated exposure to MP or other organophosphate (OP) pesticides cannot be attributed entirely to the inhibition of AChE. To accurately assess the neuro-toxic risk by occupational exposure to sub-lethal doses of MP, novel biomarkers besides in vivo anticholinesterase potency are needed.     

Sub-lethal effects of the organophosphate folidol 600 (methyl parathion) on Callichthys callichthys (pisces:teleostei)

1. The sublethal effects of Folidol 600, an organophosphate containing methyl parathion as its active principle, were analysed in the fish Callichthys callichthys.2. After an intracoelomatic application of 500 mg/kg of Folidol 600, the behavior and the levels of plasmatic cholinesterase were analysed along the time, in acute experiments.3. Plasma cholinesterase activity was inhibited by 90% after 4 hr from the initial time, keeping this level of inhibition for 4 days.4. It recovered slowly in the next 8 to 10 days, reaching about 80–90% of the normal levels around the 35th day after the beginning of the experiment.5. Many behavioral changes were observed in the first 96 hr, such as: lowering of motility with loss of equilibrium and frequent unnatural body positions; uncoordinated movements leading to incapacity of food intake; and increase in the levels of respiratory frequency.