Cholinesterase activities

ACETYLCHOLINESTERASE INHIBITING PESTICIDES Cholinesterase activity in red Discretionary 70% of individuals Ns... 

FIGURE 14.11 The pH activity profiles of four different enzymes. Trypsin, an intestinal protease, has a slightly alkaline pH optimnm, whereas pepsin, a gastric protease, acts in the acidic confines of the stomach and has a pH optimmn near 2. Papain, a protease found in papaya, is relatively insensitive to pHs between 4 and 8. Cholinesterase activity is pH-sensitive below pH 7 but not between pH 7 and 10. The cholinesterase pH activity profile suggests that an ionizable group with a pK near 6 is essential to its activity. Might it be a histidine residue within the active site ... 

A Crystalline Serum Mucoprotein with High Cholinesterase Activity, R. Bader, F. Schultz, and M. Stacey,Nature, 154(1944) 183-184. 

M (decreased plasma 67-88%, erythrocyte 9-20%, and brain 76-79% cholinesterase activity)... 

When methyl parathion was given orally to rats at doses of 1.5 mg/kg and to guinea pigs at 50 mg/kg, plasma, erythrocyte, and brain cholinesterase activity was maximally inhibited within 30 minutes after administration. In rodents of both species that died after acute intoxication, brain cholinesterase levels decreased to 20% of control values and often to 5-7% (Miyamoto et al. 1963b). The species difference in susceptibility to orally administered methyl parathion is noted in Section 3.2.2.1. 

A dose-response relationship was noted in dogs exposed to 0.03, 0.3, or 3.0 mg/kg/day methyl parathion in the diet for 13 weeks (Daly 1989). Significant reductions in erythrocyte cholinesterase activity (20-23%) and cholinesterase activity in the pons and cerebellum of the brain (43-54%) occurred in dogs... 

Routine gross and histopathological examinations revealed no treatment-related effects on the nervous system of dogs exposed to 0.03, 0.1, or 0.3 mg/kg/day methyl parathion in the diet for 1 year (Suba 1981). In addition, there were no treatment-related effects on cholinesterase activity in plasma, red blood cells, or brains in dogs under these exposure conditions. These data are in agreement with the NOAEL established above for dogs exposed to these levels for 13 weeks. 

Mean plasma, erythroc54e, and brain cholinesterase activities were significantly reduced by 67-88%, 9-20%, and 76-79%, respectively, in rats of both sexes following 2-year exposures to 2.5 mg/kg/day methyl parathion (Suba 1984). This effect did not occur in rats exposed to either 0.025 or 0.25 mg/kg/day methyl parathion. 

Permethrin, a pyrethrin pesticide, decreased the inhibition of brain cholinesterase activity by methyl parathion, but methyl parathion decreased the LD50 of permethrin when the two pesticides were simultaneously administered to rats (Ortiz et al. 1995). The potentiation of permethrin lethality may be due to the inhibition by methyl parathion of carboxylesterase, which metabolizes permethrin. 

Individuals with hereditary low plasma cholinesterase levels (Kalow 1956 Lehman and Ryan 1956) and those with paroxysmal nocturnal hemoglobinuria, which is related to abnormally low levels of erythrocyte acetylcholinesterase (Auditore and Hartmann 1959), would have increased susceptibility to the effects of anticholinesterase agents such as methyl parathion. Repeated measurements of plasma cholinesterase activity (in the absence of organophosphate exposure) can be used to identify individuals with genetically determined low plasma cholinesterase. 

Organophosphates, such as methyl parathion, are known to inhibit cholinesterase activity. A method has been developed to measure the extent of this inhibition and relate it to organophosphate exposure (EPA 1980d Nabb and Whitfield 1967). In this EPA-recommended method, blood is separated into plasma and red blood cell fractions. The fractions are treated with saline solution, brought to pH 8 with sodium hydroxide, and dosed with acetylcholine perchlorate. The ensuing acetic acid releasing enzyme reaction... 

Brock A. 1991. Inter and intraindividual variations in plasma cholinesterase activity and substance concentration in employees of an organophosphorus insecticide factory. Br J Ind Med 48 562-567. 

De Peyster A, Willis WO, Liebhaber M. 1994. Cholinesterase activity in pregnant women and newborns. Clinical Tox 32 683-696. 

Howard JK, East NJ, Chaney JL. 1978. Plasma cholinesterase activity in early pregnancy. Arch Environ Health September/October 277-278. 

Izmirova H, Shalash S, Kaloianova F. 1984. [Dynamics of inhibition of cholinesterase activity in methyl parathion intoxication]. Probl Khig 9 42-49. (Russian)... 

Venkataraman BV, Niyer GY, Narayanan R, et al. 1990. Er34hrocyte and plasma cholinesterase activity in normal pregnancy. Indian J Physiol Pharmacol 34 26-28. 

Fleming, W.J. and Grue, C.E. (1981). Recovery of cholinesterase activity in 5 avian species exposed to dicrotophos, an organo-phosphorus pesticide. Pesticide Biochemistry and Physiology 16,129-135. 

Grue, C.E., Hart, A.D.M., andMineau, P. (1991). Biological consequences of depressed brain cholinesterase activity in wildlife. In Mineau, P. (Ed.) Cholinesterase Inhibiting Insecticides— Their Impact on Wildlife and the Environment, 151-210. Amsterdam Elsevier. 

Cholinesterase activity in red cells Parathion Discretionary 70% of individual s baseline B, Ns,... 

Serat WF, Mengle DC (1973) Quality control in the measurement of blood cholinesterase activities among persons exposed to pesticides. Bull Environ Contam Toxicol 9 24-27. 

DF and its precursor, methylphosphonic dichloride (DC), are organophos-phonic acids. They will react with alcohols to form crude lethal nerve agents, such as crude GB. High overexposure may cause inhibition of cholinesterase activity. Although much less toxic than GB, DF and DC are toxic and corrosive materials. 

DF and its precursor, DC are organophosphonic acids. They will react with alcohols to form crude lethal nerve agents, such as crude GB. High overexposure may cause inhibition of cholinesterase activity. Although much less toxic than GB, DF and DC are toxic and corrosive materials. Because DF and DC are relatively volatile compounds, the primary route of exposure is expected to be the respiratory system. However, ingestion also results from inhalation exposures in animals and could occur in humans. DF and DC vapors have a pungent odor and may cause severe and painful irritation of the eyes, nose, throat, and lungs. Data provided is for DF only, DC has similar properties. 

Consistent decreases in plasma cholinesterase may not have been observed in rats and dogs because they were treated with lower doses of diisopropyl methylphosphonate. In general, depression of plasma cholinesterase, also known as pseudocholinesterase or butyrylcholinesterase, is considered a marker of exposure rather than an adverse effect. Depression of cholinesterase activity in red blood cells (acetylcholinesterase) is a neurological effect thought to parallel the inhibition of brain acetylcholinesterase activity. It is considered an adverse effect. Acetylcholinesterase is found mainly in nervous tissue and erythrocytes. Diisopropyl methylphosphonate was not found to inhibit RBC... 

Although this study (Hart 1980) did not identify an effect level, the NOAEL is below the LOEL found in all studies examining the toxicity of diisopropyl methylphosphonate. The LOEL for diisopropyl methylphosphonate is 262 mg/kg/day for male mink and 330 mg/kg/day for female mink (Bucci et al. 1997), doses at which statistically significant decreases in plasma cholinesterase (butyrylcholinesterase) but not RBC cholinesterase (acetylcholinesterase) activity were observed (Bucci et al. 1997). In general, a decrease in plasma cholinesterase activity is considered to be a marker of exposure rather than a marker of adverse effect, while a decrease in RBC acetylcholinesterase activity is a neurological effect thought to parallel the inhibition of brain acetylcholinesterase activity and is thus considered an adverse effect. Diisopropyl methylphosphonate was not found to inhibit red blood cell cholinesterase at doses at which plasma cholinesterase was significantly inhibited. No effects were observed in males at 45 mg/kg/day (Bucci et al. 1997) or at 63 mg/kg/day (Bucci et al. 1994), and no effects were observed in females at 82 mg/kg/day (Bucci et al. 1994), or at 57 mg/kg/day (Bucci et al. 1997). 

Hydraulic fluids themselves cannot be measured in blood, urine, or feces, but certain chemicals in them can be measured. Aliphatic hydrocarbons, which are major components of mineral oil hydraulic fluids and polyalphaolefin hydraulic fluids, can be detected in the feces. Certain components of organophosphate ester hydraulic fluids leave the body in urine. Some of these fluids inhibit the enzyme cholinesterase. Cholinesterase activity in blood can be measured. Because many other chemicals also inhibit cholinesterase activity in blood, this test is not specific for organophosphate ester hydraulic fluids. This test is not available at most doctor s offices, but can be arranged at any hospital laboratory. See Chapters 2 and 6 for more information. 

---