Russell L. Carr

Inhibition Patterns of Brain Acetylcholinesterase and Hepatic and Plasma Aliesterases Following Exposures to Three Phosphorothionate Insecticides and Their Oxons in Rats

Rats were administered high sublethal intraperitoneal dosages of the phosphorothionate insecticides parathion, methyl parathion, and chlorpyrifos, and their oxons. Acetylcholinesterase activities in cerebral cortex and medulla oblongata and aliesterase activities in liver and plasma were monitored at 2 hr and 1, 2, and 4 days after exposure. The maximal inhibition of brain acetylcholinesterase activity was not immediate with parathion and chlorpyrifos, reflecting the time required for bioactivation of the phosphorothionates as well as the effectiveness of the aliesterases to inactivate much of the hepatically generated oxons. In contrast, brain acetylcholinesterase activities were more quickly inhibited following administration of paraoxon and chlorpyrifos-oxon, which do not require bioactivation. Brain acetylcholinesterase was also rapidly inhibited following administration of methyl parathion and methyl paraoxon, reflecting the low sensitivity of the aliesterases to methyl paraoxon. Aliesterases were inhibited to a greater extent than acetylcholinesterase at each sampling time with parathion and chlorpyrifos and their oxons, whereas the reverse was true with methyl parathion and methyl paraoxon. All of the above patterns correlate with the in vitro sensitivities of acetylcholinesterase and aliesterases to the oxons. The very prolonged inhibition of esterase activities following chlorpyrifos treatment probably results from its substantially greater lipophilicity compared to the other compounds, which would allow it to be stored and released for gradual bioactivation. The data reported indicate that the disposition and effects of different phosphorothionate insecticides will be influenced by the sensitivities of target and nontarget esterases for their oxons and by their lipophilicity, and that predictions of in vivo responses can be made from in vitro data.

Biochemical mechanisms contributing to species differences in insecticidal toxicity

Comparison of published LD50 or LC50 levels for a variety of insecticides in several vertebrate species indicate that a wide range of toxicity levels exist, and these cannot be easily predicted within either a chemical group or within a species. There is a relatively limited data base documenting interactions between insecticides and other chemicals, either agricultural or non-agricultural; however, the fact that all major insecticide groups perturb nervous system function as their primary mechanism of acute toxicity suggests the potential for interactions. Studies in our laboratories on a select group of phosphorothionate insecticides in rats indicated that brain acetylcholinesterase sensitivity to inhibition by the oxons, the active metabolites of the phosphorothionates, does not correlate with acute toxicity levels. The activities and properties of hepatic cytochrome P450-mediated activation (desulfuration) and detoxication (dearylation) of the phosphorothionates as well as of A-esterase-mediated hydrolysis of oxons contribute substantially to understanding the acute toxicity levels in rats, as does the sensitivity of the protective aliesterases to phosphorylation. However, in the channel catfish, the acetylcholinesterase sensitivity to oxon inhibition reflects the acute toxicity level of these same insecticides, and may be largely responsible for determining the acute toxicity level in this species. Thus, metabolism of insecticides appears to be far more influential in some species than others in determining the toxicity elicited.

Effect of neonatal rat bisphenol a exposure on performance in the Morris water maze.

Bisphenol A (BPA), an environmental estrogen, is a component of many food and beverage containers and can leach into the container contents over time. Due to its estrogenic properties, exposure to BPA during development could alter the appropriate maturation of pathways essential for normal cognitive function at later ages. To investigate this, the effects of repeated postnatal exposure of male and female rats to BPA on spatial learning and memory were investigated using a Morris water maze. Breeders and offspring were maintained on a standard phytoestrogen-free diet. Oral administration of 72 microg/kg 17 beta-estradiol (E(2)), 100 microg/kg BPA (low BPA), 250 microg/kg BPA (high BPA), or the safflower oil vehicle was performed daily from postnatal d 1 (PND1) through PND14. There were no treatment-related effects on swimming ability or motivation (PND33) or on acquisition of maze solution (PND34-37). However, acquisition of maze performance was significantly better in control males than in control females. Treatment with E(2) and low BPA disrupted this normal gender-dependent pattern of acquisition, while treatment with high BPA did not. In a probe trial (PND40), females treated with high BPA spent significantly less time in the escape quadrant. These data indicate that E(2) and low dosages of BPA can alter the normal gender-dependent pattern of acquisition, while higher dosages of BPA alter the retention of spatial information without significantly affecting acquisition.

Acute effects of the organophosphate paraoxon on schedule-controlled behavior and esterase activity in rats: Dose-response relationships ☆

The effects of acute intraperitoneal administration of paraoxon on behavioral and biochemical parameters were studied in male rats. Rats were trained to press a lever under an FR10 schedule of reinforcement. Rats were injected with 3 sublethal doses of paraoxon (0.5, 0.75, and 1.0 mg/kg) and performance was monitored for four days after exposure. Response rates were depressed significantly for days 1 and 2 with 0.75 and 1.0 mg/kg, but not 0.5 mg/kg, even though there was inhibition of brain and plasma cholinesterases at all doses. Performance recovered prior to brain AChE recovery. There was no clear-cut threshold of brain AChE inhibition required to yield performance deficits, nor was there a direct correlation between significant inhibition in peripheral enzymes which could serve as markers (plasma aliesterases, butyrylcholinesterase, non-iso-OMPA-sensitive cholinesterase, and hepatic aliesterases) and performance deficits, suggesting that other noncholinergic targets may play a role in OP-induced behavioral deficits.

Biomarkers as Predictors in Health and Ecological Risk Assessment

Biomarkers are measurable biological parameters that change in response to xenobiotic exposure and other environmental or physiological stressors, and can be indices of toxicant exposure or effects. If the biomarkers are sufficiently specific and well characterized, they can have great utility in the risk assessment process by providing an indication of the degree of exposure of humans or animals in natural populations to a specific xenobiotic or class of xenobiotics. Most biomarkers are effective as indices of exposure, but adequate information is rarely available on the appropriate dose-response curves to have well-described biomarkers of effect that can be widely applicable to additional populations. Specific examples of acetylcholinest-erase inhibition following exposure to organophosphorus insecticides are cited from experiments in both mammals (rats) and fish. These experiments have indicated that the degree of inhibition can be readily influenced by endogenous (e.g., age) and exogenous (e.g., chemical exposures) factors, and that the degree of inhibition is not readily correlated with toxicological effects. Caution is urged, therefore, in an attempt to utilize biomarkers in the risk assessment process until more complete documentation is available on the specificity, sensitivity, and time course of changes, and on the impact of multiple exposures or the time of exposures.

Developmental Chlorpyrifos and Methyl Parathion Exposure Alters Radial-Arm Maze Performance in Juvenile and Adult Rats

Although the use of organophosphate (OP) insecticides has been restricted, sufficient exposure can occur to induce detrimental neurobehavioral effects. In this study, we measured physical and reflex development and spatial learning and memory in rats repeatedly exposed to incremental doses of chlorpyrifos (CPS) and methyl parathion (MPS) from postnatal day (PND) 1 to PND21. Other than decreased body weight in the higher dosage groups, no effects on physical or reflex development were observed. Significant hippocampal cholinesterase inhibition was induced in all treatment groups for up to 19 days following exposure. Beginning on PND36, working and reference memory was tested using a 12-arm radial maze, with subject animals trained and tested 4 days a week for 4 weeks. In males, working memory was decreased with the medium and high dosage of MPS but only the high dosage of CPS; while in females, no deficits were observed. For reference memory, errors were significantly increased in males exposed to the high dosage of CPS and all dosages of MPS. In females, enhanced performance was observed within the medium and high dosages of CPS but not with MPS. These data show that repeated developmental exposure to OP insecticides can induce sex-selective alterations and long-lasting changes in spatial learning and memory formation when measured using a radial arm maze and that MPS and CPS induce different neurobehavioral outcomes.

IMMUNOTOXICOLOGICAL ASSESSMENT OF METHYL PARATHION IN FEMALE B6C3F1 MICE

Methyl parathion is a widely used agricultural insecticide, and the recent unlicensed use of this compound in homes has led to the evacuation of approximately 1100 persons in Mississippi. Although the primary concern in such cases of acute exposure is neurotoxicity, a few organophosphorus compounds apparently have immunotoxic effects at dosages that do not produce neurotoxic symptoms. The purpose of the present study was to determine if this is the case for methyl parathion. Female B6C3F1 mice were exposed to methyl parathion by gavage, daily for 7, 14, 2 1, or 28 d (at 6 mg/kg/d). Exposure for 14-28 d produced significant, dose-responsive inhibition of acetylcholin-esterase (the target molecule for methyl parathion-induced neurotoxicity) in brain or plasma, indicating that the compound was active. The following immunological parameters were evaluated: white blood cell counts and differentials, spleen and thymus weight and cellularity, splenic natural killer cell activity, nitrite production by peritoneal macrophages following activation in vitro, antibody response to sheep erythrocytes in vitro and in vivo, the cytotoxic T lymphocyte response to allogeneic tumor cells, and resistance to Streptococcus agalactiae and B16F10 melanoma cells. Methylparathion at 1 or 3 mg/kg/d significantly increased splenic natural killer cell activity. Nitrite production by macrophages was increased in mice treated with 1, 3, or 6 mg/kg/d. The antibody response to sheep erythrocytes in vitro was significantly suppressed, but the humoral response to sheep erythrocytes in vivo was not affected. The cytotoxic T-lymphocyte response to allogeneic tumor cells was not significantly affected. Host resistance was not significantly decreased. Although it remains possible that immunological parameters not tested here may be affected by methyl parathion, the present results do not suggest substantial immunotoxic potential for this compound.

Chemistry of Organophosphorus Insecticides

Publisher Summary This chapter introduces and summarizes the chemistry of organophosphorus insecticides. A classification scheme has been presented into which all commercially important OP insecticides fit, based on the central phosphorus atom and the four atoms immediately surrounding it. OP insecticides may be considered to be derivatives of phosphoric acid (H3PO4) or phosphonic acid (H3PO3) in which all H atoms are replaced by organic moieties. Thus, phosphates are compounds in which the P atom is surrounded by four O atoms. In many OPs, one or more of the oxygen atoms are replaced by sulfur and/or nitrogen. For phosphoric acid derivatives, the O, S, and N atoms can be arranged in 20 different configurations. Initially, elemental phosphorus is converted into P2S5 by reaction with sulfur or into PCl3 by direct chlorination. Trialklyl phosphites are particularly useful in the preparation of dialkyl vinyl phosphates from α-chloroaldehydes and ketones. For OPs with three different substituents on the P atom, it is necessary to begin with P(:O) Cl3 (from intermediate 3) or P(:S) Cl3 (from intermediate 4). Dialkyl phosphates with phenolic or heterocyclic leaving groups are easily prepared from the phenol or heterocyclic alcohol and the dialkyl phosphorochloridate. Unfortunately, the only phosphorochloridates readily available commercially are the dimethyl and the diethyl, the former being quite unstable. OP insecticides, when kept cool, dark, and anhydrous, are usually quite stable. Exposure to heat, light (especially ultraviolet), and/or water, however, may lead to chemical alterations. The three primary reactions involving the phosphorus atom and those immediately surrounding it are hydrolysis, oxidation, and rearrangement.

Low level chlorpyrifos exposure increases anandamide accumulation in juvenile rat brain in the absence of brain cholinesterase inhibition.

The prevailing dogma is that chlorpyrifos (CPF) mediates its toxicity through inhibition of cholinesterase (ChE). However, in recent years, the toxicological effects of developmental CPF exposure have been attributed to an unknown non-cholinergic mechanism of action. We hypothesize that the endocannabinoid system may be an important target because of its vital role in nervous system development. We have previously reported that repeated exposure to CPF results in greater inhibition of fatty acid amide hydrolase (FAAH), the enzyme that metabolizes the endocannabinoid anandamide (AEA), than inhibition of either forebrain ChE or monoacylglycerol lipase (MAGL), the enzyme that metabolizes the endocannabinoid 2-arachidonylglycerol (2-AG). This exposure resulted in the accumulation of 2-AG and AEA in the forebrain of juvenile rats; however, even at the lowest dosage level used (1.0mg/kg), forebrain ChE inhibition was still present. Thus, it is not clear if FAAH activity would be inhibited at dosage levels that do not inhibit ChE. To determine this, 10 day old rat pups were exposed daily for 7 days to either corn oil or 0.5mg/kg CPF by oral gavage. At 4 and 12h post-exposure on the last day of administration, the activities of serum ChE and carboxylesterase (CES) and forebrain ChE, MAGL, and FAAH were determined as well as the forebrain AEA and 2-AG levels. Significant inhibition of serum ChE and CES was present at both 4 and 12h. There was no significant inhibition of the activities of forebrain ChE or MAGL and no significant change in the amount of 2-AG at either time point. On the other hand, while no statistically significant effects were observed at 4h, FAAH activity was significantly inhibited at 12h resulting in a significant accumulation of AEA. Although it is not clear if this level of accumulation impacts brain maturation, this study demonstrates that developmental CPF exposure at a level that does not inhibit brain ChE can alter components of endocannabinoid signaling.

The Interaction of Chlorinated Alicyclic Insecticides with Brain GabaA Receptors in Channel Catfish (Ictalurus Punctatus)

Chlorinated alicyclic insecticides are believed to antagonize the action of the neurotransmitter gamma-aminobutyric acid (GABA) at its receptor in vertebrates. Binding of the specific GABA(A) receptor ligand [35S]-t-butylbicyclophosphorothionate (TBPS) to channel catfish brain P2 membranes suggested a single population of receptors with a Kd (56.6+/-2.6 nM) and Bmax (2435+/-276 fmol/mg protein) that are similar to published values for other fish species. The competition of several chlorinated compounds for TBPS binding was investigated. The most potent inhibitors of TBPS binding were 12-ketoendrin, photoheptachlor epoxide, photoheptachlor, telodrin, and endrin, respectively, with IC50s of 20-90 nM. Photooxychlordane, photo alpha-chlordane, and oxychlordane were intermediate in potency (122-219 nM), as were isodrin, dihydroisodrin, heptachlor epoxide, and alpha-chlordane, which were similar in potency (311-397 nM). Dieldrin, lindane, and dihydroaldrin were much less potent (592-1103 nM). Heptachlor, aldrin, and gamma-chlordane were weak inhibitors of TBPS binding (2073-2738 nM). Chlordene and chlordecone had the lowest potency of all compounds studied (10,201-21,178 nM) with the exception of mirex, which did not inhibit binding at a concentration of 50 microM. There is a good correlation between binding potency and the available toxicity data for several of these compounds in channel catfish. There is also a good correlation between the inhibitory potency in channel catfish by these types of compounds with that in rats.