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Ground deposition impact of aerially applied fenthion on the fiddler crabs, Uca pugilator.

Caged fiddler crabs, Uca pugilator, were exposed to field ULV applications to measure the impact of fenthion. Two nozzle systems, conventional flat-fan nozzles (Tee Jet 8002SS) and high-pressure hydraulic nozzles (1/8 MIS), were compared using single spray swaths. Fenthion residues were detected throughout the 4.83-km test zone for both systems. Heavy ground deposits (650-1,670 microg/m2) of fenthion were found within 1 km using the flat-fan nozzle systems, which resulted in 80% fiddler crab mortality. Less than 100 microg/m2 fenthion ground deposits were detected during the high-pressure nozzle trials. No fiddler crab mortality was observed within the first 1-km zone following 3 single swath applications repeated during 3 consecutive nights. We found also that when the fiddler crabs were exposed to 700-800 microg/m2 fenthion, mortality occurred. Significant crab mortality (>50%) was observed when residues exceeded 1,000 microg/m2.

Aerosols↗

Effects of topical fenthion on blood cholinesterase and vagal tone in dogs.

A 20% fenthion (0,0-dimethyl-0-(3-methyl-4-(methylthio)-phenyl) phosphorothionate) formulation was applied topically to dogs at 8 mg/kg, 2 treatments at 14-day intervals, and 33 mg/kg, 4 treatments at 7-day intervals. Control dogs received 4 treatments at 7-day intervals of the proprietary vehicle. Following the last dose, the dogs were observed for a 14-day period. Plasma cholinesterase (ChE) exhibited a significant dose-related response with maximum inhibition to 52% and 24% of pre-dose activity occurring 4 days after the final fenthion treatment of 8 and 33 mg/kg, respectively. Erythrocyte ChE activity showed a downward trend to 32% of normal activity measured 9 days following the last treatment of fenthion at 33 mg/kg. No cholinomimetic effects were observed. All dogs were challenged with atropine sulfate (0.02 mg/kg, sc) on the last day of the observation period. A 5 min electrocardiogram was analyzed to estimate V as that portion of the variance in the R-R intervals corresponding with the normal respiratory frequency band for dogs. The mean heart period, mean heart period variance, and mean of V had significant change when measured across time in the atropine challenge (0, 25, 70, and 100 min) with a pronounced decrease at 25 min. An attenuation of the V measure in the fenthion-treated groups indicated an altered muscarinic response to atropine from prior subacute fenthion exposure.

Administration, Topical↗

Effects of aerial thermal fog applications of fenthion on caged pink shrimp, mysids and sheepshead minnows.

Mosquito control applications of fenthion by aerial thermal fog equipment were studied at 2 sites in Collier County, FL, for sprays that occurred on June 20 and 23, 1984. Acute, lethal effects of fenthion deposited in these estuarine habitats were assessed for caged pink shrimp (Penaeus duorarum), mysids (Mysidopsis bahia) and sheepshead minnows (Cyprinodon variegatus). At Site 1, along a bay with substantial dilution and tidal mixing, fenthion concentrations of 1.5 and 0.29 micrograms/liter were measured in samples taken immediately after both sprays. Concentrations decreased to less than or equal to 0.020 microgram/liter 12 h postspray and no mortality was observed for caged pink shrimp and mysids. Site 2 was along a residential canal system that offered limited dilution and mixing. Maximum concentrations were 2.6 and 0.51 micrograms/liter and measurable concentrations (greater than 0.038 microgram/liter) of fenthion persisted at this site for 4 days. Fenthion concentrations in surface waters were toxic to caged pink shrimp and mysids after both sprays. No mortality occurred among caged sheepshead minnows at either site.

Animals↗

Retinal degeneration in rats exposed to an organophosphate pesticide (fenthion).

Pigmented (Long-Evans) and albino (Wistar) rats were chronically exposed to an organophosphate pesticide (fenthion). Fenthion (50 mg/kg) was administered subcutaneously twice a week for 1 year; the total dosage for each animal ranged from 1.6 to 1.8 g. Concurrent with the fenthion administration, the amplitude of the scotopic electroetinogram (ERG) gradually declined, disappearing by the 12th month in all treated pigmented rats. For the albino experimental rats, however, the ERG amplitude disappeared as early as the 6th month in 7 out of 15 treated animals. Funduscopically, degeneration of the retina was observed in all rats when ERG responses had disappeared. Histopathological studies confirmed degeneration of the sensory retina and marked abnormalities in the pigment epithelium cells. Treated pigmented rats also had reduced a rhodopsin concentration in the retina by the 3rd month even though the photoreceptors were structurally normal. Interestingly, the plasma vitamin A levels remained normal and liver stores of vitamin A actually increased during the course of the study. Levels of butylcholinesterase in plasma and liver, on the other hand, were extremely reduced after 3 months of fenthion treatment. In general, the biochemical and functional (ERG) changes appeared before any structural damage could be detected in the retina.

Animals↗

Worker exposure and a risk assessment of malathion and fenthion used in the control of Mediterranean fruit fly in South Australia.

In 2001, an outbreak of Mediterranean fruit fly in Adelaide was controlled by South Australian Government workers applying organophosphorus insecticides (OPs) to domestic gardens. Residents made claims of adverse effects associated with allegations that worker application practices were poor and led to contamination of homes, residents and pets. The concerns led to a Parliamentary enquiry, the suspension of OP applications for fruit fly control, and the investigation of alternative methods of combating fruit fly in metropolitan Adelaide. The extent of exposure of workers and residents was not estimated. This paper describes a simulated application of the OPs concerned (fenthion and malathion) with measurements of potential exposure through inhalation, dermal contact and deposition of pesticides on surfaces. The data were used as part of a toxicological risk assessment to determine the likely impact of the use of these insecticides. Malathion, used as a 1% suspension in a protein bait mixture, was found to have little potential for airborne exposure, although some workers were found to have up to 0.315 microg/cm(2) malathion deposited on overalls (principally on forearms) and over 500 microg deposited on liner gloves and hats, respectively. Risks to workers and residents were low, with exposures likely to be a small fraction of the acceptable daily intake. Fenthion, used as a 0.05% foliar cover spray, was found between 0.02 and 0.23 mg/m(3) in air 10 m downwind from spray activity and was unlikely to pose a significant risk to residents, since exposures were of short durations of up to 20 min. Personal air samples of spray workers averaged 0.55 mg/m(3) (Workplace Exposure Standard 0.20mg/m(3)). Since workers were usually engaged in spraying for a large proportion of the day, this demonstrates the need for respiratory protective equipment. Maximum deposition of fenthion on workers overalls ranged from 0.06 to over 0.20 microg/cm(2), although little was found on gloves and hats, suggesting workers were skilled in avoiding the plume of overspray. Dialkyl phosphates (metabolites of OP insecticides) were not detected in urine of workers, and there were no changes observed in serum cholinesterase (SChE) enzyme activities 24h following the simulation. These data suggest absorption of OP insecticides by workers was negligible. Deposition on surfaces 5 and 10 m downwind ranged from none detected to 145 microg/cm(2), suggesting that exposure of residents and children in contact with contaminated surfaces (such as garden furniture or play equipment) is possible. Estimates of the potential dermal intake of fenthion by children from contaminated surfaces suggested that risks of acute and chronic effects are slight, since exposures may occur for short periods at intervals of approximately 10 days during fruit fly outbreaks.

Air Pollutants, Occupational↗

Enzyme-linked immunosorbent assay for the organophosphorus insecticide fenthion. Influence of hapten structure.

Novel procedures for fenthion hapten synthesis are described following three different strategies. The first one attaches the spacer arm to the oxygen atom of the aromatic fenthion ring. The second one binds it through the thiophosphate moiety and the third strategy consists on the attachment of the spacer arm to the sulfur atom of the molecule. A total of nine fenthion haptens have been synthesized and used for immunoreagent production (protein conjugates and polyclonal antibodies). The developed conjugate-coated format ELISA exhibited a detection limit of 0.03 ng/ml, an IC50 of 0.05 ng/ml and a dynamic range between 0.03 and 1 ng/ml. There was little or no cross-reactivity to similar tested compounds. The ELISA was used to determine fenthion residues in white wine samples without any purification or preconcentration steps. Recoveries ranged between 81% and 113%.

Animals↗

Development of a microtiter plate ELISA and a dipstick ELISA for the determination of the organophosphorus insecticide fenthion.

In previous studies, polyclonal antibodies against the organophosphorus insecticide fenthion were obtained and an indirect competitive enzyme-linked immunosorbent assay (ELISA) was developed for this pesticide. In this study, using these antibodies and an enzyme tracer, direct competitive ELISAs for fenthion in microtiter plate and dipstick formats were developed. The microtiter plate ELISA showed an IC(50) value of 1.2 microg/L with a detection limit of 0.1 microg/L. The antibodies showed negligible cross-reactivity with other organophosphorus pesticides. The use of the dipstick format using Immunodyne as a support membrane allowed the quick visual detection of fenthion in concentrations >10 microg/L. The IC(50) value of the dipstick format using reflectance detection was 15 microg/L with a detection limit of 0.5 microg/L. The recoveries of fenthion from spiked vegetable samples using the two formats without any prior enrichment or cleanup steps were 87-116%.

Antibody Specificity↗

Three-year study of fenthion and dimethoate pesticides in olive oil from organic and conventional cultivation.

Residues of fenthion and dimethoate pesticides were determined in organic and conventional olive oils by liquid-liquid and solid-phase extractions with subsequent gas chromatography and mass spectrometric analysis. The olive oil samples were collected from Crete during 1997-99. The average concentrations of fenthion in conventional olive oils were 0.1222, 0.145 and 0.1702 mg x kg(-1), and for dimethoate were 0.0226, 0.0264 and 0.0271 mg x kg(-1) for 1997, 1998 and 1999, respectively. The average concentrations of fenthion in organic olive oils were 0.0215, 0.0099 and 0.0035 mg x kg(-1) for 1997, 1998 and 1999, while for dimethoate they were 0.0098, 0.0038 and 0.0010 mg x kg(-1), respectively. All the olive oils contained residue levels lower than the maximum residue levels according to the FAO/WHO Codex Alimentarius. The organic olive oil contained significantly lower concentrations of the two pesticides. The levels of fenthion and dimethoate in organic olive oils exhibited a decreasing trend following the implementation of the new cultivation method. We propose procedures that should be established in the organic cultivation in order to maximize its effectiveness.

Dimethoate↗

Residues of fenthion and trichloron in olives and olive oil after olive tree treatments.

The residue levels of trichlorfon, fenthion and its metabolites were determined in olives, olive oil and vegetation water after treatment of olive trees at different times before harvest. The highest residues of fenthion were detected in oil, while the highest level of trichlorfon was found in vegetation water. The time gap between treatment and harvest strongly influences the residue levels of fenthion in olives and olive products. The levels of fenthion, which were lower than the maximum residue level (MRL) established by the Italian regulations, were obtained only when the treatment was carried out 60 days before harvest, so it may be necessary to use the insecticide trichlorfon 30 or 10 days before harvest since it leaves low residue levels in oils.

Agrochemicals↗

Laboratory bio-assay of temephos and fenthion against some vector species of public health importance.

Laboratory studies carried out using Temephos and Fenthion, two commonly used larvicides under Urban Malaria Scheme (NMEP) and NFCP for the control of mosquito larvae. The results revealed that the LC50 and LC90 values for temephos against Aedes aegypti 0.0177 and 0.0559, Anopheles stephensi 0.0148 and 0.0472, Culex quinquefasciatus 0.0157 & 0.0480 and for Culex vishnui group of mosquitoes 0.043 & 0.0118 ppm respectively. The results obtained revealed that there is a 62.8 & 94.12 times increase in the LC50 & LC90 of Cx. Quinquefasciatus which indicates that the species has developed resistance to temephos. There were 6.32 & 8.34 fold increase in Ae. aegypti and 2.27 & 2.34 fold increase in LC50 & LC90 values of An. stephensi are indicative of development of tolerance against temephos. Similarly LC50 and LC90 values estimated for fenthion against Ae. aegypti 0.0173 & 0.0392, An. stephensi 0.0274 & 0.0992 and Cx. quinquefasciatus 0.03 & 0.0469 respectively. The slope values were found to be higher in fenthion as compared to temephos. It was recorded to be 2.72 times higher in Cx. quinquefasciatus and 1.54 times against An. stephensi. However, much difference was not observed in the slope values of temephos and fenthion in Ae. aegypti.

Aedes↗

Effects of the organophosphorus insecticide fenthion on phyto- and zooplankton communities in experimental ponds.

The organophosphorus insecticide fenthion was applied to experimental ponds and its effects on phyto- and zooplankton communities were analysed. The sensitivity to fenthion differed among cladoceran and rotiferan species according to the following order: Daphnia galeata > Monia micrura > Bosmina fatalis >/= Polyarthra trigla > Keratella valga. The results suggest that large zooplankton species tend to be more sensitive to fenthion than small ones, large cladocerans more sensitive than small cladocerans, and cladocerans more sensitive than rotifers. The application of fenthion induced an increase in the density of rotifers and phytoplankton. This was a secondary effect of the chemical, which directly depressed cladoceran populations and consequently released rotifers and phytoplankton from competition with, and grazing by cladocerans.

Journal Article↗

Mechanisms of resistance to fenthion in Culex pipiens fatigans Wied.

One of the insecticides of choice to control the mosquito Culex pipiens fatigans, a vector of Bancroftian filariasis, is fenthion. The mechanism of resistance to this insecticide which could develop in C. p. fatigans was investigated in a strain from Rangoon, Burma, made 8 times more fenthion-resistant than normal by laboratory selection, by exposing the larvae to (32)P-fenthion and examining the metabolites.Larvae of the resistant strain were found to absorb about half as much fenthion as those of the corresponding normal strain, and they degraded proportionately about twice the amount absorbed to water-soluble metabolites. Thus, the larval content of chloroform-soluble toxicants remaining was only one-third to one-seventh as much in the resistant as in the normal strain. The production of the non-toxic hydrolytic (water-soluble) metabolites was 70% greater in the resistant strain in absolute terms, despite the lower amount absorbed into the larvae. The greatest increase (4-fold) was in the oxonase activity, although the thionase activity was more important in both strains.Esterase zymograms from agar-gel electrophoresis revealed a principal band which was much more intense in the resistant than in the susceptible strain, as judged by its hydrolysis of alpha- and beta-naphthyl acetates and phosphates. This band was comparatively insensitive to the toxicant fenoxon, and could hydrolyse it.

Animals↗

Environmental hazards of mobile ground spraying with cyanophos and fenthion for quelea control in Senegal.

Seven roosts of red-billed quelea, Quelea quelea, in the Senegal River Valley and Delta were visited during and after aerial or terrestrial treatments with either Cyanox (cyanophos 500 g a.i. liter-1, five roosts) or Queletox (fenthion 640 g a.i. liter-1, two roosts). The primary goal of the observations was to provide data on environmental effects of cyanophos after mobile ground spraying operations. Twenty-six species of vertebrates (birds, reptile, fish) were found dead or debilitated near the spray sites. Effects on nontarget fauna were most pronounced among owls (cyanophos and fenthion) and blue-naped mousebirds, Urocolius macrourus (fenthion). Among terrestrial invertebrates ants and carabid, and tenebrionid beetles were the most conspicuously affected. Among aquatic invertebrates affected tadpole shrimps, Triops cancriformis, dominated. Extremely high residues were found immediately after spraying on tree leaves in the spillway of a vehicle-mounted Berthoud Super Puma airblast sprayer (up to 1380 mg kg-1) and on birds found dying under these trees (125-11,277 microg bird-1, average 2720 microg bird-1) in two roosts treated with cyanophos. Blue-naped mousebirds were identified as being particularly at risk. Side effects were not dose related. They were most severe after routinely practiced mobile ground spraying applications which led to overdosing. These application methods impose severe environmental hazards, and should be abandoned.

Animals↗

A comparison of two spray nozzle systems used to aerially apply the ultra-low-volume adulticide fenthion.

Field experiments with the mosquito adulticide fenthion (Baytex) compared the conventional flat-fan nozzle system (Tee Jet 8002SS) and a new high-pressure hollow-cone nozzle system (1/8 MISS). Ground deposition and aerial flux of the mosquito adulticide fenthion were measured up to 4.83 km downwind by using filter paper and yarn collectors, respectively. Biological efficacy was investigated by using caged salt-marsh mosquitoes (Ochlerotatus taeniorhynchus), and caged fiddler crabs (Uca pugilator) were exposed to quantify nontarget impact. Peak deposits to the ground were 1,729 microg/m2 and 240 microg/m2 for the flat-fan nozzles and high-pressure cones, respectively. Deposits from the flat-fan nozzles resulted in a cumulative fiddler crab mortality of 80%, whereas no deaths were recorded with the high-pressure system. The range of fenthion flux detected in the air when using the yarn collectors was similar for the 2 systems, with both showing drift through 4.83 km. For the flat-fan spray nozzle system, the aerosol flux ranged from 3.02 to 67.33 microg/yarn collector. The range of aerosol flux for the high-pressure nozzle spray system was 0.15-50.66 microg/yarn collector. Although the 2 systems produced comparable ranges of flux, the high-pressure system provided higher control efficacy against mosquitoes. Maximum mosquito control when using the flat-fan spray nozzle system against female salt-marsh mosquitoes was 26.6%, whereas maximum control with the high-pressure spray system was 92.9%.

Aerosols↗

Determination of the half life of fenthion in New Zealand White rabbits using three routes of administration.

The purpose of this research was to determine if the route of administration influenced the biological half life of fenthion, an organophosphorous insecticide. Twenty mg/kg fenthion was given to groups of New Zealand White Rabbits via the oral, subcutaneous and intravenous routes respectively. The distribution of fenthion in the blood of New Zealand rabbits followed an open two compartment model. There were no significant differences in the kinetic parameters (2, beta, K12, K21, Kel) derived for the three different routes of administration. The biological half life of slightly over 11 hours, did not differ significantly with the route of administration.

Administration, Oral↗

Clinical and toxicological data in fenthion and omethoate acute poisoning.

This study paper reports on two cases of poisoning with the organophosphorus insecticides, fenthion and omethoate. The two victims were admitted in the Intensive Care Unit (ICU) a few hours after ingestion of the two insecticides. They received appropriate treatment for organophosphorous poisoning (gastric lavage, activated charcoal, atropine and pralidoxime) and supportive care. Both patients survived. Organophosphate blood levels were determined on admission (fenthion 2.9 micrograms/ml, omethoate 1.6 micrograms/ml) and during the hospitalisation and proved to be considerably high. Slow elimination rate of the poison already distributed in the body was indicated for both pesticides. The patient with omethoate poisoning remained clinically well (Glasgow Coma Scale: 15) and was discharged three days later. The patient with fenthion poisoning, who had also ingested 30 mg of bromazepam and 720 mg of oxetoron, developed cholinergic crisis six hours after admission and was intubated for 24 days, with concomitant complications.

Adult↗

Effects of multiple dosing of fenthion, fenitrothion, and desbromoleptophos in young chicks.

The effects of multiple doses of desbromoleptophos, fenitrothion, and pure fenthion on brain acetylcholinesterase (AChE), brain neurotoxic esterase (NTE), and walking were investigated in immature chicks, below the age of sensitivity to organophosphorus ester-induced delayed neurotoxicity (OPIDN). Ten milligrams per kilogram per day of delayed neurotoxicant desbromoleptophos (DBL), 15 mg/kg.d of the non-neurotoxicant fenitrothion (FTR), and 3 mg/kg.d of the suspected neurotoxicant fenthion (FEN) were given orally for 7 d to 3-d-old chicks. Behavioral testing was performed for treated and control chicks on various days after treatment. Brain NTE and AChE assays were carried out for treated and control chicks on each day of behavioral testing. DBL altered gait and inhibited both NTE and AChE; FEN altered gait and inhibited AChE but not NTE; and FTR did not affect gait, while inhibiting AChE but not NTE. NTE and AChE inhibition were 70% and 55%, respectively, 24 h after the last treatment, for the chicks treated with DBL. NTE returned to normal levels by around d 25 and AChE by 20 d after the last treatment. FTR caused more than 50% AChE inhibition but no NTE inhibition, 24 h after last treatment. NTE inhibition for the FEN-treated chicks never exceeded 11% during the whole period of the experiment, whereas 54% inhibition of AChE was seen 1 d after last treatment. DBL and FEN significantly altered the gait of treated chicks, but the non-OPIDN-inducing FTR did not. This study confirms that alterations in the gait of young chicks are not direct consequences of either NTE or AChE inhibition, and that fenthion-induced functional deficits can be distinguished from classical OPIDN.

Animals↗

Analysis of fenthion in postmortem samples by HPLC with diode-array detection and GC-MS using solid-phase extraction.

Fenthion (O,O-dimethyl-O-[3-methyl-4-(methylthio)-phenyl]-thiophos-phate ) is an organophosphate insecticide. A specific method to quantitate fenthion in postmortem matrices with solid-phase extraction combined with high-performance liquid chromatography-diode-array detection (HPLC-DAD) and gas chromatography-mass spectrometry (GC-MS) is presented. Fenitrothion (O,O-dimethyl-O-[3-methyl-4-nitrophenyl]-thiophosphate) is selected as the internal standard. For sample cleanup, a simple but selective solid-phase extraction is chosen after comparison with traditional liquid-liquid extraction procedures. Homogenized and appropriately diluted aqueous samples are applied, and the analytes are desorbed with 5 mL of dichloromethane. Aliquots of the extract are used for HPLC-DAD and GC-MS analysis, Liquid and GC conditions are as follows: gradient elution with a mixture of methanol and water (10:90 to 90:10, v/v) containing 0.0125M NaOH on an Aluspher RP-Select B column monitoring at 250 nm, and temperature programming from 60 to 300 degrees C on a dimethylpolysiloxane column in the SCAN mode, respectively. This method is applied to a suicidal case involving unsuspected acute intoxication with fenthion (concentration in blood, 3.8 micrograms/mL).

Aged↗