Inhibitor Report for: Fenthion

Semi-field studies, using the larval implant technique, show that sheep may be protected against resistant larvae of Lucilia cuprina by thorough jetting with chlorfenvinphos, diazinon, dichlofenthion and fenthion ethyl, but not bromophos ethyl, for the normal duration of waves of bodystrike in New South Wales. The standard method of assessing implant data is to be preferred to analyses based on average protection due to the extra time required for the latter procedure.

The development of chemical control of Musca domestica on Danish farms 1945--72 is outlined. It has been strongly influenced by successive development of resistance and failure of control by one insecticide after another. The chlorinated hydrocarbons used as residual sprays failed 1947--51. Organophosphorus compounds (OPC) were widely used from 1953, first as strips impregnated with parathion and residual sprays with diazinon. Resistance to OPC was first found in 1955, diazinon was given up in 1957--59 and parathion strips failed in the early '60's. Trichlorfon paint-on baits were widelyused 1958--64 and serious resistance did not appear until 1967, induced by selective pressure of fenthion and dimethoate used as residual sprays. High resistance to the contact effect of trichlorfon now occurs everywhere in Denmark. However, trichlorfon baits are still able to kill many flies. Residual sprays with fenthion, ronnel and fenitrothion were used to some extent 1960--70, but increased resistance reducing the residual effect developed in 2--3 years. Dimethoate was used on the majority of farms 1965--72. It was very effective the first years and resistance increased slowly until 1971--72, when high to extreme dimethoate-resistance became general on Danish farms. This was associated with high resistance to other OPC for fly control, e.g. fenthion, fenitrothion, bromophos, and tetrachlorvinphos, and to carbamates, with the result that no generally effective residual sprays were available. In 1971--72 frequent treatments with synergized pyrethroids have been tried. However, the method is often expensive, and serious resistance problems have appeared on a few farms. In this situation preventive, sanitary measures to eliminate or reduce fly breeding in manure are becoming decisive again, but difficult to practise due to lack of farm labour. The extreme Danish situation is compared with those in other areas, and probable reasons for differences in resistance and control problems are discussed, as well as possibilities for strategies to reduce resistance development.

White leghorn laying hens were exposed to weekly dermal applications of either 1 mg fenthion/kg (FEN; low dose) or 4 mg FEN/kg (high dose) for 24 w with the objective of evaluating chronic FEN toxicity. Four of 24 hens at the high dose exhibited transitory loss of proprioception, perching ability, and righting reflex after 8 to 16 w exposure. All hens receiving the high dose lost the ability or desire to jump from a box during the latter half of the FEN exposure period. Inhibition of serum cholinesterase and brain acetylcholinesterase was greater in the high-dose hens. Brain neuropathy target esterase was not inhibited. Behavioral changes were not correlated with changes in brain concentrations of enzymes or neurotransmitters or their metabolites. Muscle fiber abnormalities were more common in the high-dose hens. Muscle electrical activity was recorded electromyographically via telemetry. Fibrillation (denervation) potentials were absent, but amplitude times duration values for motor unit potentials of the peroneus longus muscle for 5 of the 6 4-w evaluation intervals were higher in the high-dose hens. This EMG response suggested presence of a mild neuropathy which was supported by results of ultrastructural examinations of the sciatic nerve. The low dose initially produced 8% stimulation of egg production while the high dose inhibited egg production 10% during the latter 16 w of the study and reduced body weight 8% during this period.

Organophosphates, a widely used class of insecticidal compounds, have been shown to cross the placental barrier, and thus potentially affect the developing fetus. This study compared the maternal and fetal effects, including cholinesterase inhibition, following gestational exposure to six organophosphates: tribufos, oxydemeton-methyl, azinphos-methyl, fenamiphos, isofenphos, and fenthion in the Sprague-Dawley rat. All test compounds were administered via oral gavage on gestation days 6-15. Maternal cholinesterase activities (plasma, PChe; erythrocyte, RChe; and brain, BChe) were measured on gestation days 16 and 20, and fetal brain cholinesterase activity was measured on gestation day 20. Effects on gestational parameters (clinical signs, food consumption, and body weight) in adult rats, when observed, were only observed at the highest dose tested for each compound. The inhibition of maternal cholinesterase activities associated with these clinical findings was, for all compounds, always greater than 20%. Moreover, cholinesterase activities were inhibited at dose levels below that which elicited clinical effects. Statistically significant inhibition of at least two of the three cholinesterase enzymes (PChe, RChe, or BChe) was observed on gestation day 16, 24 h following exposure, with all of the organophosphates tested. By gestation day 20, the inhibition of cholinesterase activity was reduced; however, the high dose for all test compounds (except BChe in fenamiphos-treated dams) continued to demonstrate statistically significant inhibition of RChe and BChe. Despite significantly affected cholinesterase activity in the dams, no remarkable effects on fetal BChe were observed with any test compound. No embryotoxicity or teratogenicity were observed with any of the test compounds. These results demonstrate that for the six organophosphates tested: (1) inhibition of maternal cholinesterase activity was the most sensitive indicator of organophosphate exposure; (2) the level of cholinesterase inhibition associated with clinical findings was always greater than 20%; and (3) no effect on fetal cholinesterase activity (BChe) was observed, even at dose levels that continued to demonstrate significant inhibition of maternal cholinesterase activity.

H2-receptor antagonists inhibit cholinesterase (ChE) activity. We examined perturbations in ChE isoenzyme patterns and ChE activities of rats from the combined effects of fenthion (FEN) and cimetidine (CIM). Sixty-four female Sprague-Dawley rats were divided into 8 groups. Four rat groups were given FEN or gum arabic solution and each group divided into 2 small groups according to the CIM or gum arabic administration. FEN was administered po at 12.3 mg/kg (1/20 LD50) or 24.5 mg/kg (1/10 LD50) for 14 days or 49 mg/kg (1/5 LD50) every 4 days. CIM was given po at 1,500 mg/kg from days 7 to 13. Samples were collected 3 h after CIM administration on days 8 and 13. CIM did not influence ChE isoenzyme patterns or ChE activity. FEN inhibited both the ChE isoenzyme patterns and ChE activities without producing clinical signs. Although 1 rat in the 12.5 mg FEN/kg + CIM group died on day 10, all rats in other FEN (24.5 mg/kg or 49 mg/kg) + CIM groups died on days 8-10. Differences in suppression of ChE isoenzyme patterns were detectable between the FEN-dosed and FEN + CIM-dosed groups. There were no differences in ChE activities between the FEN-dosed and FEN + CIM-dosed groups. The i.p. administration of 500 mg CIM/kg (LD50) did not suppress ChE activities.

Populations of Culex pipiens were sampled from 8 locations in Cyprus between 1987 and 1993. All population samples generally revealed organophosphate resistance to malathion, temephos, chlorpyrifos, fenthion, dichlorvos, and pirimiphos methyl, in decreasing order of magnitude. Of 7 populations assessed with the carbamate propoxur, all proved to be resistant to different degrees. Of the 6 populations tested with permethrin, 2 were resistant to permethrin. Resistance was associated with the presence of 5 different overproduced esterases (esterases A1, A2, A5, B2, and B5) as well as an insensitive form of acetylcholinesterase. These results are discussed in relation to the ongoing mosquito abatement program in Cyprus and to similar programs in other parts of the world.

Susceptibility to six organophosphate (OP), two pyrethroid (PY), and one carbamate (C) insecticides was investigated in Culex pipiens quinquefasciatus Say, Aedes aegypti (L.), and Aedes polynesiensis Marks larvae from the island of Tahiti. Cx. p. quinquefasciatus and Ae. aegypti were compared with susceptible reference strains treated simultaneously. A low, but significant, resistance to bromophos (4.6x), chlorpyrifos (5.7x), fenthion (2.4x), fenitrothion (5.0x), temephos (4.3x) and permethrin (2.1x) was found in Cx. p. quinquefasciatus, and to malathion (1.5x), temephos (2.3x), permethrin (1.8x) and propoxur (1.7x) in Ae. aegypti. Cx. p. quinquefasciatus was shown to possess over-produced esterases A2 and B2, which are known to be involved in resistance to OPs in other countries. Ae. polynesiensis was less resistant than the Ae. aegypti reference strain to all insecticides except temephos (1.8x) and permethrin (6.7x). To determine whether Ae. polynesiensis had developed resistance to these insecticides in Tahiti, a geographical survey covering 12 islands of the Society, Tuamotu, Tubuai, Marquesas, and Gambier archipelagoes was undertaken with three insecticides (temephos, deltamethrin, and permethrin). Two- to threefold variations in LC50S were observed among collections. Results are discussed in relationship to the level of insecticide exposure on the different islands.

Significant increase of sister-chromatid exchanges (SCE) in V79 cells treated with 2 organophosphorus pesticides (OPP), fenthion and oxydemeton-methyl, was observed. The other 7 compounds (6 OPP and 1 defoliant) namely, amaze, azinphos-methyl, bolstar, DEF-defoliant, fensulfothion, monitor and nemacur caused no increase of SCE frequencies at the doses tested. All the compounds except fensulfothion and oxydemeton-methyl induced cell-cycle delay in varying degrees. Cell-cycle delay caused by an OPP was found to be dose-dependent. Based on these data as well as others reported, it would appear that OPP which induce no SCE increase and no or slight cell-cycle delay could be considered as good candidates to substitute the pesticides that have been found to be harmful to the environment.

Brain and plasma cholinesterase (ChE) activities were determined for mallard ducklings (Anas platyrhynchos) exposed to dicrotophos and fenthion. Recovery rates of brain ChE did not differ between ducklings administered a single oral dose vs. a 2-week dietary dose of these organophosphates. Exposure to the organophosphates, followed by recovery of brain ChE, did not significantly affect the degree of brain ChE inhibition or the recovery of ChE activity at a subsequent exposure. Recovery of brain ChE activity followed the general model Y = a + b(logX) with rapid recovery to about 50% of normal, followed by a slower rate of recovery until normal ChE activity levels were attained. Fenthion and dicrotophos-inhibited brain ChE were only slightly reactivated in vitro by pyridine-2-aldoxime methiodide, which suggested that spontaneous reactivation was not a primary method of recovery of ChE activity. Recovery of brain ChE activity can be modeled for interpretation of sublethal inhibition of brain ChE activities in wild birds following environmental applications of organophosphates. Plasma ChE activity is inferior to brain ChE activity for environmental monitoring, because of its rapid recovery and large degree of variation among individuals.

Semi-field studies, using the larval implant technique, show that sheep may be protected against resistant larvae of Lucilia cuprina by thorough jetting with chlorfenvinphos, diazinon, dichlofenthion and fenthion ethyl, but not bromophos ethyl, for the normal duration of waves of bodystrike in New South Wales. The standard method of assessing implant data is to be preferred to analyses based on average protection due to the extra time required for the latter procedure.

The development of chemical control of Musca domestica on Danish farms 1945--72 is outlined. It has been strongly influenced by successive development of resistance and failure of control by one insecticide after another. The chlorinated hydrocarbons used as residual sprays failed 1947--51. Organophosphorus compounds (OPC) were widely used from 1953, first as strips impregnated with parathion and residual sprays with diazinon. Resistance to OPC was first found in 1955, diazinon was given up in 1957--59 and parathion strips failed in the early '60's. Trichlorfon paint-on baits were widelyused 1958--64 and serious resistance did not appear until 1967, induced by selective pressure of fenthion and dimethoate used as residual sprays. High resistance to the contact effect of trichlorfon now occurs everywhere in Denmark. However, trichlorfon baits are still able to kill many flies. Residual sprays with fenthion, ronnel and fenitrothion were used to some extent 1960--70, but increased resistance reducing the residual effect developed in 2--3 years. Dimethoate was used on the majority of farms 1965--72. It was very effective the first years and resistance increased slowly until 1971--72, when high to extreme dimethoate-resistance became general on Danish farms. This was associated with high resistance to other OPC for fly control, e.g. fenthion, fenitrothion, bromophos, and tetrachlorvinphos, and to carbamates, with the result that no generally effective residual sprays were available. In 1971--72 frequent treatments with synergized pyrethroids have been tried. However, the method is often expensive, and serious resistance problems have appeared on a few farms. In this situation preventive, sanitary measures to eliminate or reduce fly breeding in manure are becoming decisive again, but difficult to practise due to lack of farm labour. The extreme Danish situation is compared with those in other areas, and probable reasons for differences in resistance and control problems are discussed, as well as possibilities for strategies to reduce resistance development.