The bioaccumulation and biotransformation of cis,trans-cypermethrin in the rat

The disposition of the pyrethroid insecticide cypermethrin, (RS)-a-cyano-3-phenoxybenzyl (1RS)-cis, trans-3-(2,2-dichlorovinly)-2, 2-dimethylcyclopropane-carboxylate, has been studied in male and female rats following a single toxic oral dose (200mg kg⁻¹) of two radiolabelled forms ([¹⁴C-benzyl] and [¹⁴C-cyclopropyl]) of the insecticide. The bioaccumulation and elimination of ¹⁴C-benzyl-labelled cypermethrin, following repeated administration at a sub-toxic dose (2mg kg⁻¹), has also been studied in male and female rats. Although, at the toxic dose, radioactivity from the two radiolabelled forms was rapidly eliminated in urine and faeces, the increased excretion in the faeces, over that for low doses, was evidence that absorption was incomplete. The major pathways of metabolism involved cleavage of the ester bond, with subsequent hydroxylation and glucuronidation of the cyclopropyl acid moieties, together with hydroxylation and sulphation of the 3-phenoxybenzyl moiety. The absence of sex- or dose-dependent changes was reflected by the constant proportions of these metabolites found in the urine. Constant levels of radioactivity in tissues were achieved rapidly, generally within the first week of repeated administration. Elimination was rapid on the cessation of dosing, although less rapid from the fat and skin. The material in the fat was mainly the cis-isomers of cypermethrin, which were eliminated with a mean half-life of 18.2 days, compared with 3.4 days for the trans-isomers.     

The metabolism of the pyrethroid insecticide (±)-α-cyano-3-phenoxybenzyl 2,2,3,3-tetramethyl-cyclopropanecarboxylate,WL 41706, in the rat

The metabolism of the pyrethroid insecticide α-cyano-3-phenoxybenzyl 2,2,3,3-tetramethylcyclopropanecarboxylate (WL 41706) has been studied in rats using two forms of ¹⁴C-labelling (benzyl- and cyclopropyl-). Excretion of benzyl^?14C was rapid, 57% of the administered dose being eliminated in the urine 48 h after treatment and 40% in the faeces. No significant sex difference was observed. The amount of radioactivity excreted via expired gases was 0.005% of the administered dose and less than 1.5% of the dose remained in the animals 8 days after treatment. The mean percentage recovery of administered dose was 104% for male rats and 97% for female rats. Urinary and faecal metabolites from these rats, and from rats dosed similarly with [cyclopropyl^?14C]-WL 41706 were studied. The rapid metabolism of WL 41706 is due to efficient cleavage of the ester bond by rats in vivo to afford 2,2,3,3-tetramethylcyclopropanecarboxylic acid (partly as glucuronide) and the 3-phenoxybenzyl moiety. Before this cleavage occurs, however, about half of the intake suffers aryl hydroxylation giving the α-cyano-3-(4-hydroxyphenoxy)benzyl ester, part of which is excreted in the bile as a conjugate(s) and part of which is cleaved and eliminated as the O-sulphate of 3-(4-hydroxyphenoxy)benzoic acid and the glucuronide of 2,2,3,3-tetramethylcyclopropanecarboxylic acid. A minor amount of hydroxylation occurs at a trans-methyl group on the cyclopropane acid moiety. The metabolism of WL 41706 by rat liver occurs mainly in the microsomes and mainly via oxidative processes.     

The pyrethrins and related compounds. Part XXII. Preparation of isomeric cyano-substituted 3-phenoxybenzyl esters

Preparation of 3-phenoxybenzyl chrysanthemates and their dihalovinyl analogues substituted with a cyano group at the 2-, 6-, (R)-α-, or (S)-α- positions is described. The (R)- and (S)- isomers of α-cyano-3-phenoxybenzyl esters of 2,2-difluoro-, -dichloro-, and -dibromo-vinyl analogues of cis- and trans- chrysanthemic acid are separated chromatographically, as are the separate pairs of enantiomers of fenvalerate, (RS)-α- cyano-3-phenoxybenzyl (RS)-2-(4-chlorophenyl)-3-methylbutyrate. An optically active ester of α-cyano-3-phenoxybenzyl alcohol (obtained using D -oxynitrilase) with 2,2,3,3-tetramethylcyclopropanecarboxylic acid is synthesised.     

Separation and identification of short-lived free radicals formed by photolysis of the pyrethroid insecticide fenvalerate

Using a spin-trap reagent 3-nitrosodurene (1,2,4,5-tetramethyl-3-nitrosobenzene), the short-lived free radicals generated by ultraviolet irradiation of fenvalerate [(RS)-α-cyano-3-phenoxybenzyl (RS)-2-(4-chlorophenyl)-3-methylbutyrate] in degassed benzene or dichloromethane, were scavenged as the more stable nitroxide radicals. These radicals were separated by high-performance liquid chromatography and identified individually by electron-spin resonance spectroscopy, as well as by gas chromatography/mass spectrometry. As a result, they were found to be the spin adduct mixtures of the 4-chloro-α-isopropylbenzyl and α-cyano-3-phenoxybenzyl radicals, which are involved in the photo-induced decarboxylation process of fenvalerate. Discrimination of the radicals was also performed by the isotope-labelling method whereby the benzylic proton in the acid moiety was deuteriated. The spin numbers of the nitroxides decreased by about five-fold when photolysis was carried out in oxygenated benzene solution. N-Benzylidene-tert-butylamine N-oxide trapped both radicals but much less efficiently. The nitroxide of the 4-chloro-α-isopropylbenzyl radical was predominant at 25°C or –40°C, but the proportion of the α-cyano-3-phenoxybenzyl nitroxide radical increased at the lower temperature.     

The metabolism of the pyrethroid insecticide cypermethrin in rats; excreted metabolites

The metabolism of the pyrethroid insecticide cypermethrin has been studied in rats using three forms of ¹⁴C-labelling (benzyl-, cyclopropyl- and cyano-) and separate cis- and trans- isomers. The proportion of the dose absorbed from the intestines (50–70% at 2–3 mg kg^?1) is rapidly metabolised and eliminated. The major reaction is cleavage of the ester bond to afford the constituent cis- and trans- acids which are conjugated with glucuronic acid and eliminated in the urine. The 3-phenoxybenzyl portion of the molecule is probably released as the α-hydroxynitrile, which is converted via the aldehyde into 3-phenoxybenzoic acid. This compound is then largely hydroxylated and eliminated as a sulphate conjugate. The cyanide ion is metabolised via predictable routes, for instance, as thiocyanate. Cypermethrin is hydroxylated to some extent before hydrolysis. Most of this hydroxylation occurs at the methyl group trans to the cyclopropane carboxyl group, and at the 4-position of the phenoxy group. cis- Cypermethrin is slightly more stable than the trans-isomer.     

Metabolism in rats of 3-phenoxybenzyl alcohol and 3-phenoxybenzoic acid glucoside conjugates formed in plants

Upon single oral administration to rats, the mono-, di- and tri-glucose conjugates of [¹⁴C]-3-phenoxybenzyl alcohol ( I ) or the mono-glucose conjugate of [¹⁴C]-3-phenoxybenzoic acid ( II ) were rapidly hydrolysed and extensively eliminated in the urine mostly as the sulphate conjugate of 3-(4-hydroxyphenoxy)benzoic acid ( X ). The faecal elimination was a minor route, whereas the biliary excretion was about 42% of the dose and the glucuronide conjugates of I , II and X were common major metabolites. The biliary glucuronides were cleaved in the small intestine to the respective aglycones, which were reabsorbed, metabolised further, and excreted in the urine as the sulphate conjugate of X . Although small amounts of the mono-, di-and tri-glucosides were found in the 0.5-h blood and liver samples following oral administration of the tri-glucoside of I , they were not detected in the urine, bile or faeces. Similarly the sulphate conjugate was one of the major urinary metabolites of germ-free rats, dosed with the ¹⁴C-glucosides via the oral or the intraperitoneal route, although they were excreted unchanged in certain amounts in the urine and faeces. The glucose conjugates were cleaved in vitro by gut microflora and in various rat tissues, including blood, liver, small intestine and small intestinal mucosa. The tissue enzymes showed a different substrate specificity in hydrolysis of the glucosides. However, they were not cleaved in gastric juice, bile, pancreatic juice or urine.     

Metabolism of the cis- and trans-isomers of cypermethrin in mice

Metabolism in mice of the separated cis- and trans-isomers of the pyrethroid insecticide cypermethrin (NRDC 149), (RS)-α-cyano-3-phenoxybenzyl (1RS)-cis, trans-3-(2,2-dichlorovinyl)-2,2-dimethylcyclopropanecarboxylate, was investigated in each case with preparations that were ¹⁴C-labelled in the benzyl and cyclopropyl moieties. Radioactivity from the trans-isomer was mainly excreted in the urine and that from the cis-isomer in the faeces. Elimination of both isomers was rapid except for a small portion (approximately 2%) of the cis-isomer which was released from the fat with a half-life of approximately 13 days. Metabolism of cypermethrin occurred mainly by ester cleavage and elimination of the cis- and trans-3-(2,2-dichlorovinyl)-2,2-dimethyl- cyclopropanecarboxylic acid moieties as glucuronide conjugates. The α-cyano-3-phenoxybenzyl alcohol released by ester cleavage was mainly converted to 3-phenoxy-benzoic acid which was partly eliminated unchanged, partly conjugated with aminoacids (mainly taurine) and glucuronic acid, and partly oxidised to 3-(4-hydroxyphenoxy) benzoic acid which was excreted as the sulphate conjugate. Metabolites retaining the ester linkage were formed by hydroxylation at various sites in the molecule with more hydroxylation of the cis- than of the trans-isomer occurring.     

Structure—activity relationships in pyrethroid esters derived from substituted 2-phenoxy-3-methylbutanoic acids

Non-cyclopropane pyrethroid esters of different substituted 2-phenoxy-3-methylbutanoic acids have been synthesised using the three alcohols—3-phenoxybenzyl alcohol, α-cyano-3-phenoxybenzyl alcohol and 3, 4-methylene-dioxybenzyl alcohol. Among the 35 esters synthesised and tested against Culex quinquefasciatus Say, the Bancroftian filariasis vector, for both larvicidal and adulticidal activities, α-cyano-3-phenoxybenzyl 2-(4-fluorophenoxy)-3-methylbu-tanoate, with an LC₅₀ value of 2.5 × 10^?3 mg litre^?1 for larvicidal activity, and α-cyano-3-phenoxybenzyl-2-(4-chlorophenoxy)-3-methylbutanoate, with an LD₅₀ value of 30 times; 10^?4 ug insect^?1 for adulticidal activity, were found to be as effective as fenvalerate, a well-known non-cyclopropane pyrethroid ester. Structure-activity studies showed that the insecticidal activity is dependent on the nature and position of the substituent in the phenyl ring of the acid moiety and also on the type of alcohol moiety.     

Pyrethroid toxicology in the frog

Adult Rana pipiens pipiens (Shreber) are highly sensitive to insecticidal α-cyano-3-phenoxybenzyl esters administered subcutaneously, i.e., LD₅₀ 0.13–0.35 mg/kg for deltamethrin and the most potent isomer of each of cis-cypermethrin, fenpropathrin, and fenvalerate and 0.65 mg/kg for (1R,αS)-trans-cypermethrin. Pyrethroids lacking the α-cyano substituent [pyrethrins, S-bioallethrin, kadethrin, and the Cis- and trans-isomers of (1R)-tetramethrin, (1RS)-resmethrin, (1R)-phenothrin, and (1R)-permethrin] vary greatly in their toxicity (LD₅₀ 0.14 to > 60 mg/kg) and the trans isomers are much less toxic than the corresponding cis isomers. The trans/cis specificity is due in large part to relative detoxification rates based on synergism studies with the resmethrin and permèthrin isomers and liver pyrethroid esterase assays with the permethrin and cypermethrin isomers. Poisoning by the noncyano compounds involves hyperactivity and tremors whereas by the cyanophenoxybenzyl esters involves tonic seizures and choreoathetosis, i.e., types I and II syndromes, respectively. Picrotoxinin, t-butylbicyclophosphate, and five other small cage compounds give a third type of syndrome with clonic seizures. Diazepam and its 2′-fluoro-4-methyl-4,5-dihydro analog (RO 5-3636) are more effective than 23 other compounds tested in protecting against deltamethrin toxicity. Diazepam is most effective in alleviating the Type II syndrome, intermediate with the type I syndrome, and is not active with picrotoxinin.     

Comparative metabolism and disposition of [14C-benzyl] cypermethrin in quail,rat and mouse

The excretion and metabolism of cis + trans-[¹⁴C-benzyl] cypermethrin has been compared in quail, rat and mouse. Radioactivity was rapidly eliminated by quail dosed orally with [¹⁴C]cypermethrin (2 mg kg^?1), as was the case in the rat and the mouse. When the birds were dosed intraperitoneally (IP) with the ¹⁴C-labelled pyrethroid, radioactivity was excreted more slowly than after oral dosing, and almost 20% of the IP dose of ¹⁴C remained in the tissues after 7 days. Both mammalian species excreted [¹⁴C]cypermethrin more rapidly than did the avian species after IP administration, and less than 6% of the dose remained in their tissues after several days. The biotransformation of the pyrethroid was more complex in the avian species (34 metabolites) than in the two mammals (some 10 metabolites in each species). In quail the predominant reactions were ester bond cleavage of cypermethrin together with either aromatic hydroxylation or amino acid conjugation of the 3-phenoxybenzyl moiety. The hydroxylated derivatives were eliminated mainly as sulphates. 3-Phenoxybenzoic acid was conjugated with a variety of amino acids including glycine, taurine, glutamic acid, serine, α-N-acetylornithine and the dipeptide glycylualine. The last two conjugations are unique to avian species. The major metabolite of cypermethrin in the rat was the sulphate conjugate of 3-(¹⁴-hydroxyphenoxy)benzoic acid, whereas in the mouse the major products were 3-phenoxybenzoic acid and its taurine conjugate. Thus, in the mammalian species where hydroxylation was maximal, amino acid conjugation was a minor metabolic route und vice versa. However, in the quail, aromatic hydroxylation and amino acid conjugation of the 3-phenoxybenzyl moiety of cypermethrin were both major reactions. The influence of the rates and sites of metabolism, and of the enzymology of amino acid conjugation, in determining this species difference are discussed. The rapid metabolism of cypermethrin to a variety of polar conjugates that are readily excreted, together with the low brain sensitivity of birds compared with mammals to its neurotoxic effects, explains the low acute toxicity of this pyrethoid to avian species.     

Effects of pyrethroid structure on rates of hydrolysis and oxidation by mouse liver microsomal enzymes

Studies on the metabolism rates of 44 pyrethroids and 24 model compounds in mouse liver microsomal systems serve to divide the substrates into three groups based on their ease of hydrolysis and oxidation. Primary alcohol esters of trans-substituted cyclopropanecarboxylic acids are most rapidly metabolized with hydrolysis generally serving as the major component of the total metabolism rate. Although hydrolyzed slowly or not at detectable rates, the primary alcohol cis-substituted cyclopropanecarboxylates, tetramethylcyclopropanecarboxylates, and p-chlorophenyl-α-isopropylacetates are rapidly oxidized. The highly insecticidal α-cyano-3-phenoxybenzyl esters are least susceptible to metabolic attack due to both reduced esterase rates attributable to α substitution in the alcohol moiety and reduced oxidase rates for which no adequate explanation is currently available. Other structural modifications in the acid and alcohol moieties are less important in determining the metabolism rates. The substrate specificities of the microsomal esterases and oxidases are compared with in vivo pyrethroid structure-biodegradability relationships.     

The metabolism of 3-phenoxybenzyl alcohol,a pyrethroid metabolite,in plants

The metabolism and conjugation of 3-phenoxybenzyl alcohol, a plant metabolite of permethrin and cypermethrin, have been examined in abscised cotton leaves. Mature cotton leaves were treated by petiole uptake of an aqueous solution of [α-¹⁴C]-3-phenoxybenzyl alcohol. Initially there was rapid formation of a compound identified as the glucosyl 3-phenoxybenzyl ether. Subsequently more polar compounds were formed and these were shown to be disaccharide conjugates of the alcohol with glucose and pentose sugars. The alcohol and its mono- and disaccharide conjugates were shown to undergo interconversion in cotton leaves, and evidence was obtained from experiments with [¹⁴C]glucose for the ready exchange of the glucose units on the conjugates with free glucose in the leaves. No larger carbohydrate conjugates of 3-phenoxybenzyl alcohol were detected under the conditions used.     

Metabolism of O,O,S-trimethyl phosphorothioate in rats after oral administration of a toxic dose,and the effect of coadministration of its antagonistic thionate isomer

The in vivo metabolism of [¹⁴CH₃S]- and [¹⁴CH₃O]O,O,S-trimethyl phosphorothioate (OOS) was followed in rats after oral administration of threshold or LD₅₀ toxic doses of 20 or 60 mg/kg. Similar metabolic studies were conducted with coadministration of 1% O,O,O-trimethyl phosphorothionate (OOO), which prevented all signs of delayed toxicity, including weight loss. When administered alone, OOS was metabolized mainly (50–60%) via removal of the CH₃S moiety, which was largely converted to expired CO₂. Approximately 20% of the compound was O-demethylated, presumably by conjugation with glutathione, and then further metabolized to CO₂. Major urinary products were identified as O,O-dimethyl phosphoric acid (50–60%) and O,S-dimethyl phosphorothioic acid (～20%). Coadministration of OOO caused a slight decrease (～5%) in the cleavage of the CH₃S moiety, indicated by a reduction in ¹⁴CO₂ from [¹⁴CH₃S]OOS and a quantitatively similar increase in the formation of O,S-dimethyl phosphoric acid. Limited pharmacokinetic studies indicated that OOS was rapidly absorbed and distributed throughout the body. Coadministration of 1% OOO caused a slight increase in the blood half-life of parent OOS when administered at 60 mg/kg. It was concluded that a small proportion of the cleavage of the CH₃S moiety from OOS is involved in the intoxication process, and that this intoxication reaction is specifically inhibited by OOO.     

Further studies of the degradation of the pyrethroid insecticide cypermethrin in soils

Studies of the degradation of the pyrethroid insecticide cypermethrin (NRDC 149) and its cis- and trans-isomers (NRDC 160 and NRDC 159, respectively), have been extended. In soils stored in the laboratory for up to 52 weeks, cypermethrin continued to be degraded by hydrolysis and oxidation. A previously unidentified product has now been identified as the dicarboxylic acid 3-(2, 2-dichlorovinyl)-1-methylcyclopropane-1, 2-dicarboxylic acid. Comparative experiments carried out under indoor and outdoor conditions showed that essentially the same products were formed under these different conditions. However, α-carboxy-3-phenoxybenzyl 3-(2, 2-dichlorovinyl)-2, 2-dimethyl-cyclopropanecarboxylate was one minor product detected only under outdoor conditions. Evidence is presented for the further degradation of bound residues arising in soil from cypermethrin treatments. There was limited uptake of the radiolabel into wheat grown in soil containing radiolabelled bound residues.     

The action of pyrethroids in the insect central nervous system. I. Features of molecular structure associated with toxicity to cockroaches and to their giant fibre axons

To investigate relationships between the molecular structure of pyrethroids and their mode of action, toxicities to adult male Periplaneta americana by topical application and injection were compared with toxicities to their giant fibre nerve axons. From the tests against intact insects it was concluded that: (i) although ED₅₀S ranged from 0.04 to 65 μg/insect, each compound was equally toxic, with one exception, when administered by either route; (ii) esters of (1 R)-cis- were more toxic than esters of the corresponding (1 R)-trans-3-substituted-2, 2-dimethylcyclopropanecarboxylic acids; (iii) α-cyano-3-phenoxybenzyl esters were more toxic than the corresponding 3-phenoxybenzyl esters; (iv) changes in the alcoholic component of some compounds (particularly trans-isomers of esters of 5-benzyl-3-furylmethanol and esters of α-cyano-3-phenoxybenzyl alcohol) affected a recovery phase in their ED₅₀/time curves more than changes in the acid component; (v) the amount of recovery was positively correlated with molecular polarity. The concentration required to decrease the amplitude of the action potential of giant fibres by 30% in 1 h ranged from 0.26 μM for the most active compound to 100 μM for the least active. There was no clear relationship between neurotoxicity and toxicity to whole insects and little association between neurotoxicity and features of molecular structure. Neurotoxicity was, however, positively correlated with polarity. Giant fibre axons seem unlikely to be critical sites of action of pyrethroids.     

2-anilino-3-methylbutyrates and 2-(isoindolin-2-yl)-3-methylbutyrates,two novel groups of synthetic pyrethroid esters not containing a cyclopropane ring

A new series of substituted 2-anilino-3-methylbutyrates has been prepared; bioassay data for these compounds on Heliothis virescens, Musca domestica, Aphis fabae and Tetranychus urticae are presented and discussed. Some unexpected relationships were observed between the nature of the substituents and the biological activity. Increases in foliar stability were noted with certain substitution patterns. Both α-cyano-3-phenoxybenzyl 3-methyl-2-(α, α, α,2-tetrafluoro-p-toluidino)butyrate and the corresponding 2-(2-chloro-α, α, α-trifluoro-p-toluidino)-3-methylbutyrate showed good stability in air and light, and exhibited biological activities of a similar nature and potency to those of previously known synthetic pyrethroids. Esters of the (R)-2- anilino-3-methylbutyric acids are far more active than those prepared from the (S)-enantiomers. The (R)-configuration at C-2 in these acids is sterically equivalent to the active absolute configuration at the chiral carbon α to the carboxylate group in both the permethrin and the fenvalerate types of pyrethroids. A new class of insecticidal 2-(isoindolin-2-yl)alkanoates is also reported. In this series the most biologically active analogue was α-cyano-3-phenoxybenzyl 3-methyl-2-(4,5,6,7-tetrafluoroisoindolin-2-yl)butyrate. These esters were considerably less stable than the anilino analogues on exposure to air and light.     

Degradation of the pyrethroid insecticide WL 41706, (±)-α-cyano-3-phenoxybenzyl 2,2,3,3-tetramethylcyclopropanecarboxylate,in soils

The degradation of the insecticide WL 41706, (±)-α-cyano-3-phenoxybenzyl 2,2,3,3-tetramethylcyclopropanecarboxylate, (I), in two soils from Spain and one from the UK has been studied in the laboratory. Samples of (I) labelled separately with ¹⁴C in the benzyl ring (uniform labelling) and at C₍₁₎ of the cyclopropyl ring were used. The insecticide underwent degradation by hydrolysis at the cyano group to form the amide and carboxylic acid analogues. However, the major degradative route was hydrolysis at the ester linkage leading initially to the formation of 3-phenoxy-benzoic acid and 2,2,3,3-tetramethylcyclopropanecarboxylic acid. When a sandy clay soil was treated with [benzyl^?14C]-WL 41706 under balance conditions, ¹⁴CO₂ was evolved at a steady rate and 16 % of the applied radiolabel was detected as ¹⁴CO₂ over a 26 week period. The rate of degradation of I was most rapid on a moist sandy clay (loss of 50 % initial quantity in 4 weeks) but it was considerably slower on dry sandy clay and moist clay soils (> 16 weeks). Under flooded, anaerobic conditions the rate of hydrolysis of the insecticide was slower than under aerobic conditions and the 3-phenoxybenzoic acid and 2,2,3,3-tetramethylcyclopropanecarboxylic acid were found to accumulate over the 24 weeks of the experiment.     

Substrate-specificity and toxicological significance of pyrethroid-hydrolyzing esterases of mouse liver microsomes

An esterase or esterases in acetone powder preparations of mouse liver microsomes hydrolyze the cyclopropanecarboxylate ester linkage of pyrethroid insecticide chemicals derived from primary alcohols. The rate of cleavage of (+)-trans-chrysanthemates with various alcohol moieties decreases in the following order: 5-propargyl-2-furylmethyl; 5-benzyl-3-furylmethyl (bioresmethrin); 3-phenoxybenzyl; tetrahydrophthalimidomethyl esters. The hydrolysis rate of benzylfurylmethyl esters with various acid moieties decreases in the order: (+)- or (?)-trans-chrysanthemate; (+)-trans-ethanochrysanthemate; tetramethylcyclopropanecarboxylate; (+)- or (?)-cis-chrysanthemate or (+)-cis-ethanochrysanthemate. The trans-isomers of chrysanthemates and ethanochrysanthemates are hydrolyzed from 2.6- to more than 50-fold more rapidly than the corresponding cis-isomers. This enzyme system does not hydrolyze secondary alcohol esters, i.e., allethronyl (+)-trans- and (+)-cis-chrysanthemates.On intraperitoneal administration to mice, the (+)-trans-chrysanthemate and -ethanochrysanthemate of benzylfurylmethanol are of very low toxicity relative to the corresponding (+)-cis-isomers and the tetramethylcyclopropanecarboxylate. S,S,S-tributyl phosphorotrithioate (DEF) pretreatment increases the toxicity of these five compounds by 2.6- to more than 188-fold, with the exception of bioresmethrin whose toxicity is not altered. When the toxicity is increased, it is probably the result of esterase inhibition since DEF strongly inhibits the esterase activity of fresh liver microsomes while the mixed-function oxidase system remains active. The oxidase system metabolizes the chrysanthemates more rapidly than the ethanochrysanthemates of benzylfuryl-methanol. Depending upon the pyrethroid involved, the esterase or the mixed-function oxidase system, or both may be responsible for limiting the toxicity of these pyrethroids to mice.     

Photodegradation of the pyrethroid insecticide fenpropathrin in water,on soil and on plant foliage

The photodegradation of fenpropathrin [(RS)-α-cyano-3-phenoxybenzyl 2,2,3,3-tetramethylcyclopropanecarboxylate] ( I ), in water, on soil and on plant foliage, was investigated using ¹⁴C-preparations labelled separately at the cyano group, cyclopropyl-C₁ or in the benzyl ring. On exposure to sunlight, I was photodecomposed with initial half-lives of >6 weeks in distilled water, 6.0 weeks in humic acid aqueous solution, 2.7 weeks in river water, 1.6 weeks in sea water and 0.5 of a day in 2% aqueous acetone. A triplet photosensitiser, acetone, together with naturally occurring substances in river and sea water, including humic acid, enhanced the photodegradation of I . On three kinds of soil, I was rapidly photodegraded with initial half-lives of 1–5 days, whereas it was fairly photostable on a mandarin orange leaf. The photoreactions involved were: decarboxylation, hydration of the cyano group to carboxamide, cleavage of the ester or the diphenyl ether linkage, hydrolysis of the carboxamide group to carboxyl, and hydroxylation at either or both of the gem dimethyl groups. The predominant reactions in water were decarboxylation, ester bond cleavage and photo-induced evolution of [¹⁴C] carbon dioxide from the [¹⁴C] cyano label; on soil, hydration or ester bond cleavage predominated. The hydration was also of importance in river and sea water. Decarboxylation did not occur on soil and plant foliage.     

The pyrethrins and related compounds; Part XXIV: synthesis, 13C-nuclear magnetic resonance spectra and insecticidal activity of cycloalkyl analogues of fenvalerate

Close isosteres of fenvalerate [(RS)-α-cyano-3-phenoxybenzyl (RS)-2-(4-chlorophenyl)-3-methylbutyrate], in which cyclopropyl groups replace isopropyl have insecticidal activity close to or greater than the parent compounds, and diminished intravenous toxicity to rats. A direct toxicological relationship of these compounds to fenvalerate itself and to chrysanthemate esters is indicated by the consistently greater activity of esters from one of an enantiomeric pair of acids. Other esters with larger alkyl or cycloalkyl groups, or spiropentane analogues of chrysanthemates are less active insecticides. ¹³C-Nuclear magnetic resonance spectra suggest that in the α-cyanobenzyl esters there is an intramolecular through-space interaction in solution. The relationships between the chemical structures of the compounds synthesised and their relative activities to different insect species and toxicity to rats are discussed.