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.     

New conjugated metabolites of 3-phenoxybenzoic acid in plants

The metabolism of 3-phenoxybenzoic acid, a common plant metabolite of deltamethrin, cypermethrin and fenvalerate, has been studied in abscised leaves of cabbage, cotton, cucumber, kidney bean and tomato plants. The [¹⁴C]-acid was readily converted into more polar conjugates by esterification with glucose, 6-O-malonylglucose, gentiobiose, cellobiose, glucosylxylose and two types of triglucose with different isomerism. Other metabolites identified were the glucosyl ether of 3-(4-hydroxyphenoxy)benzoic acid, and a 3-(2-hydroxyphenoxy)benzoic acid derivative with a total of two molar equivalents of glucose linked to the carboxyl and phenolic -OH groups. The conjugation pathways were somewhat plant-specific. The glucosylxylose ester was found only in cotton, and the cellobiose and triglucose esters were found only in tomato. All of the conjugates except the glucose and glucosylxylose esters were plant metabolites that had not been identified previously. Furthermore, this is the first report to show the presence of cellobiose and triglucose conjugates in plants. However, neither of the acetyl derivatives of the [¹⁴C]-triglucoside was identical with the synthetic deca-acetyl derivative of [1→6]-triglucoside.     

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.     

The conjugation and accumulation of metabolites of cypermethrin by earthworms

When earthworms are maintained in soil containing [¹⁴C]cypermethrin they accumulate radioactive residues. These residues are not eliminated when the worms are transferred to untreated soil. The accumulated radioactive residue is a complex mixture of conjugates of two metabolites of cypermethrin (3-phenoxybenzoic acid and (1RS)-cis, trans-3-(2,2-dichlorovinyl)-2,2-dimethylcyclopropanecarboxylic acid). One major constituent of this mixture of conjugates has been identified as N¹, N¹²-di-(3-phenoxybenzoyl)spermine. Feeding studies with quail and rats have established that the residues accumulated by the earthworms are not further bioaccumulated by earthworm predators.     

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 metabolism of fenvalerate in plants: The conjugation of the acid moiety

The metabolism of the pyrethroid insecticide fenvalerate [(RS)-α-cyano-3-phenoxybenzyl (RS)-2-(4-chlorophenyl)-3-methylbutyrate] ( I ), and of its most insecticidal (αS,2S) isomer ( II ), has been examined in cabbage plants grown and treated under laboratory conditions with [¹⁴C]chlorophenyl- and [ring-¹⁴C]benzyllabelled preparations of the two compounds. Both insecticides disappeared from the treated leaves with similar half-lives of approximately 12–14 days; they underwent ester cleavage to a significant extent, together with some hydroxylation at the 2- or 4-position of the phenoxy ring, and hydrolysis of the nitrile group to amide and carboxyl groups. Most of the carboxylic acids and phenols thus produced occurred as glycoside conjugates. In separate experiments, the uptake and metabolism of 2-(4-chlorophenyl)-3-methylbutyric acid ( X ), the acidic half of the molecule, were examined in the laboratory, using abscised leaves of kidney bean, cabbage, cotton, cucumber and tomato plants. The acid X was found to be readily converted, mainly into glucose and 6-O-malonylglucose esters in kidney bean, cabbage and cucumber plants, into glucosylxylose, sophorose and gentiobiose esters in cotton, and into two types of triglucose esters with differing isomerism in tomato. One of the acetyl derivatives of the trisaccharide conjugates was identical with the synthetic deca-acetyl derivative of the [1 → 6]-triglucose ester.     

The effect of organophosphate insecticides on adrenal corticosterone formation

In vitro and in vivo experiments with Sprague-Dawley rats showed that the three organophosphate insecticides tested (see below) depressed endogenous corticosterone synthesis and blocked corticosteroidogenesis in response to ACTH and cAMP stimulation of a suspension of adrenal cells. Pregnenolone stimulation of adrenal cells was not inhibited at the insecticide concentrations which blocked the ACTH and cAMP stimulation of corticosteroidogenesis. It was concluded that the insecticides act beyond the site of action of ACTH and at or beyond the level of cAMP metabolism and prior to the metabolism of pregnenolone.Insecticides tested were: dichlorvos (O,O-dimethyl-O,2,2-dichlorovinyl phosphate), Dursban (phosphorothioic acid: O,O-diethyl O-3,5,6-trichloro-2-pyridyl ester), and Diazinon (phosphorothioic acid: O,O-diethyl O-(2-isopropyl-6-methyl-4-pyrimidinyl ester).     

Degradation of the pyrethroid cypermethrin NRDC 149 (±)-α-cyano-3-phenoxybenzyl (±)-cis,trans-3-(2,2-dichlorovinyl)-2,2-dimethylcyclopropanecarboxylate and the respective cis-(NRDC 160) and trans- (NRDC 159) isomers in soils

The degradation of the pyrethroid insecticide cypermethrin and the geometric isomers NRDC 160 (cis-) and NRDC 159 (trans-) in three soils has been studied under laboratory conditions. Samples of the insecticides labelled separately with ¹⁴C in the cyclopropyl and benzyl rings were used. The rate of degradation was most rapid on sandy clay and sandy loam soils, 50% of the NRDC 160 and NRDC 159 applied to both soils being decomposed in 4 weeks and 2 weeks respectively. The major degradative route in all soils was hydrolysis of the ester linkage leading to the formation of 3-phenoxybenzoic acid and 3-(2,2-dichlorovinyl)-2,2-dimethylcyclopropanecarboxylic acid; soil treated with the cis-isomer (NRDC 160) was found to contain both cis- and trans-isomer forms of the cyclopropanecarboxylic acid. Further degradation of these carboxylic acids was evident since ¹⁴CO₂ was released from cyclopropyl- and benzyllabelled cypermethrin in amounts equivalent to 24 and 38% of the applied radioactivity over a 22 week period. A minor degradative route was ring-hydroxylation of the insecticide to give an α-cyano-3-(4-hydroxyphenoxy)benzyl ester followed by hydrolysis of the ester bond. Under waterlogged conditions the rate of hydrolysis of cypermethrin on sandy loam soil was slower than under aerobic conditions and 3-phenoxybenzoic acid accumulated in the anaerobic soil.     

Metabolism of cisanilide (cis-2,5-dimethyl-1-pyrrolidinecarboxanilide) by excised leaves and cell suspension cultures of carrot and cotton

Major methanol-soluble metabolites of cisanilide (cis-2,5-dimethyl-1-pyrrolidinecarboxanilide) were isolated from excised, pulse-treated carrot and cotton leaves. They were identified as O-glucoside conjugates of primary aryl and alkyl oxidation products, 2,5-dimethyl-1-pyrrolidine-4-hydroxycarboxanilide and 2,5-dimethyl-3-hydroxy-1-pyrrolidinecarboxanilide. Comparative studies with carrot and cotton cell cultures showed similar initial pathways of cisanilide metabolism. Time-course studies with [¹⁴C-pyrrolidine]- and [¹⁴C-phenyl]cisanilide showed little, if any, cleavage of the herbicide molecule in either excised leaves or cell cultures. Quantitative differences in the metabolism of cisanilide by cell cultures and excised leaves included; a reduced capacity of cell cultures to form secondary glycoside conjugates and an increased ability of cell cultures to form methanol-insoluble residues.     

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 of permethrin isomers in American cockroach adults,house fly adults,and cabbage looper larvae

Forty-two insect metabolites of [1RS,trans]-and [1RS,cis]-permethrin are tentatively identified in studies with Periplaneta americana adults, Musca domestica adults, and Trichoplusia ni larvae involving administration of ¹⁴C preparations labeled in either the alcohol or acid moieties. The less-insecticidal trans isomer is generally metabolized more rapidly than the more-insecticidal cis isomer, particularly in cabbage looper larvae, and metabolites retaining the ester linkage appear in larger amount with cis-permethrin. Although the dichlorovinyl group effectively blocks oxidation in the acid side chain, the permethrin isomers are metabolized by hydrolysis and hydroxylation at the geminal-dimethyl group (either trans- or cis-methyl substituent) and the phenoxybenzyl group (predominantly at the 4′-position in all species but also at the 6-position in house flies). The alcoholic and phenolic metabolites are excreted as glucosides, and the carboxylic acids are excreted as glucosides and amino conjugates (glycine, glutamic acid, glutamine, and serine) with considerable species variation in the preferred conjugating moiety.     

The uptake of metabolites of permethrin by plants grown in soil treated with [14C]permethrin

Sugar beet, wheat, lettuce and cotton were grown in soil treated with [¹⁴C]permethrin, the crops being sown at intervals of 30, 60 and 120 days after treatment of the soil. The uptake of radioactive residues into these crops was measured. Low radioactive residues (up to 0.86 μg g^?1) were detected in the mature plants sown 30 days after soil treatment, and this uptake declined significantly as the interval between soil treatment and sowing increased. Metabolites derived from the acid moiety of the permethrin molecule were shown to constitute the greater part of the residue transferring from the soil to the crops. (1RS)-cis- and (1RS)-trans-3-(2,2-dichlorovinyl)- 2,2-dimethylcyclopropanecarboxylic acid and 3-(2,2-dichlorovinyl)-1-methylcyclopropane-1,2-dicarboxylic acid were identified as the major acidic metabolites. The latter compound is a metabolite of permethrin which has not previously been identified in soil or plants.     

The inhibitory mode of action of the pyridazinone herbicide norflurazon on a cell-free carotenogenic enzyme system

The inhibition site of the phenylpyridazinone herbicide, norflurazon [SAN 9789, 4-chloro-5-(methylamino)-2-(3-trifluoromethylphenyl)-pyridazin-3(2H)one] was determined in a cell-free carotenogenic enzyme system from a mutant strain of Phycomyces blakesleeanus (Mucoraceae). The presence of norflurazon resulted in a reduced flow of radioactivity from [2-¹⁴C]mevalonic acid to phytoene (7,8,11,12,7′,8′,11′,12′-octahydro-ψ,ψ-carotene) and β-carotene (β,β-carotene), whereas an increased incorporation occurred in the C₃₀ terpenoids, squalene, and ergosterol. Furthermore, radioactivity accumulated in geranylgeranyl pyrophosphate. Since no radioactivity was found in prephytoene pyrophosphate and the radioactivity in phytoene decreased upon addition of norflurazon, this herbicide exerts its primary inhibitory action on the reaction catalyzed by phytoene synthetase. The nonbleaching phenylpyridazinone BAS 13761 [4-chloro-5-methoxy-2-phenyl-pyridazin-3(2H)-one] did not show this effect. Other inhibitory sites of norflurazon, either on prenyl pyrophosphate synthetase or on the desaturation of phytoene, were excluded.     

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.     

Studies of the metabolism of 3-phenoxybenzoic acid in plants

The metabolism of ¹⁴C-labeled 3-phenoxybenzoic acid, PBA, has been studied in cotton, vine, broad bean, soya bean, pea, lettuce, and tomato, using abscised leaves. PBA was converted into a range of polar products by esterification with glucose (in cotton and other species) and with glucosylarabinose and glucosylxylose (especially in vine leaves). Uptake of the glucose ester itself by cotton leaves also led to conversion into a more polar conjugate, probably the glucosylarabinose ester, which was not detectable following uptake of PBA. When PBA was applied to the surface of intact cotton leaves, it was slowly converted into products similar to those above.     

Metabolism of four resmethrin isomers by liver microsomes

Microsomal esterases of mouse and rat liver readily cleave the trans- but not the cis-isomers of resmethrin (5-benzyl-3-furylmethyl chrysanthemate). The ester linkage also appears to undergo oxidative cleavage when esterase attack is minimal, i.e., with (+)-cis- and particularly (?)-cis-resmethrin in microsome-NADPH systems and with any of the isomers when NADPH is added to microsomes pretreated with TEPP. Metabolites retaining the ester linkage are detected in significant amounts only with (+)-cis-resmethrin in which case they are formed by oxidation at either the trans(E)- or cis(Z)-methyl group of the isobutenyl moiety with or without oxidation of the benzylfurylmethyl group. Metabolites of each acid moiety include chrysanthemic acid and up to six derivatives of this acid formed by oxidation at the trans(E)- or cis(Z)-methyl group yielding the corresponding alcohol, aldehyde, or acid, with chrysanthemate isomer and enzyme source variations in the preferred site of oxidation. The major identified metabolite of the alcohol moiety is either benzylfurylmethanol or the corresponding carboxylic acid depending on the enzyme system used. In the course of microsomal oxidation, a fragment from the alcohol but not the acid moiety of (+)-trans- and (+)-cis-resmethrin is strongly bound to microsomal components. These findings confirm in vivo studies on the isomeric variations in metabolism of the resmethrin components.     

Partial purification and properties of S-cysteinyl-hydroxychlorpropham transferase from oat (Avena sativa L.)

S-Cysteinyl and glutathione conjugates of isopropyl-3′-chloro-4′-hydroxycarbanilate (4-hydroxychlorpropham) were synthesized directly in the presence of soluble enzyme systems isolated from etiolated shoots of oat seedlings. The enzyme systems responsible for these reactions were partially purified and charaterized. Enzyme A appeared to be a multicomponent system, equally reactive with either cysteine or glutathione. Enzyme B was twice as active as enzyme A in the formation of S-cysteinyl-hydroxychlorpropham. Affinity chromatography of enzyme A produced an enzyme fraction with properties similar to those of enzyme B. Both enzymes (A and B) were significantly inhibited by increased cysteine concentrations. The reaction of glutathione with enzyme B was limited. However, when low concentrations of a nonreacting effector, cysteine ethyl ether, were added, glutathione conjugation increased significantly. At higher concentrations, cysteine ethyl ester formed a conjugate with 4-hydroxychlorpropham. Isopropyl-5′-chloro-2′-hydroxycarbanilate (2-hydroxy-5-chlorpropham) did not conjugate with either cysteine or glutathione but did react with cysteine ethyl ester. Isopropyl-3′-chlorocarbanilate (chlorpropham) was not a substrate for thioether conjugation. These data suggest that para- and/or ortho-hydroxylated carbanilates and cysteine-related substrates may form thioether conjugates when incubated under appropriate conditions with these complex enzyme systems.     

Sub-lethal influences of different insecticides on oviposition preference of Helicoverpa armigera (Hübner) (Lepidoptera: Noctuidae) on cotton in relation to altered plant morphology

We investigated the sub-lethal influences of spinosad, chlorpyriphos, endosulfan, acephate and cypermethrin on the oviposition responses of Helicoverpa armigera (Hübner) to cotton plants, under cage and laboratory conditions. The rank order of toxicity (LC₅₀ values as a per cent) of test insecticides against third instar larvae using the leaf disc method was: spinosad > chlorpyriphos > endosulfan > acephate > cypermethrin. On whole plants, females laid more eggs on acephate LC₅₀-, acephate LC₃₀- and cypermethrin LC₅₀-treated cotton plants than on the control. The chlorpyriphos-treated plants were least preferred for oviposition. When excised cotton leaves from different treatments were used in a multiple-choice test, cypermethrin LC₅₀- and endosulfan LC₃₀-treated leaves received more eggs than the control. The repeated application of sub-lethal concentrations of different insecticides reduced plant height in the case of acephate LC₃₀ and cypermethrin LC₅₀, while plant spread and upper canopy leaf area were reduced in both treatments of acephate and cypermethrin. Reduced plant spread, upper canopy leaf area followed by plant height were found associated with oviposition preference by H. armigera females.     

Response of wheat and oat seedlings to root-applied diclofop-methyl and 2,4-dichlorophenoxyacetic acid

Roots of wheat and oat seedlings were treated with diclofop-methyl (methyl 2-[4-(2′,4′-dichlorophenoxy)phenoxy]propanoate) in a specially designed Plexiglas treatment apparatus. Diclofopmethyl severely inhibited the root growth of susceptible oat seedlings but roots of resistant wheat seedlings were unaffected. Diclofop-methyl at 0.3 μM reduced the growth of oat roots to 50% of the control. Direct contact between diclofop-methyl and the inhibited root zone was necessary for growth inhibition since other parts of the seedling (roots and shoots) isolated from contact with diclofop-methyl solution by a physical barrier were unaffected. Diclofop (2-[4-(2′,4′-dichlorophenoxy)phenoxy]propionic acid), the free acid metabolite of diclofop-methyl, was somewhat more phytotoxic than the parent compound. The herbicide, 2,4-dichlorophenoxyacetic acid (2,4-D), which engenders auxin responses, slightly enhanced the inhibition of oat root growth by diclofop-methyl. The primary wheat metabolite, ring-hydroxylated diclofop, was nonphytotoxic to oat root growth, whereas the acetylated derivative of the primary water-soluble oat metabolite (neutral glucose ester of diclofop) inhibited oat root growth to the same extent as diclofop-methyl. These results support the hypothesis that the basis for selectivity between resistant wheat and susceptible oat is the metabolism of diclofop-methyl by aryl hydroxylation and conjugation but not glucose ester conjugation. Translocation is also not an important factor in the phytotoxic activity of diclofop-methyl.     

Excretion,distribution and depletion of [14C]cypermethrin and cis and trans isomers of 3-(2,2-dichlorovinyl)-2,2-dimethylcyclopropanecarboxylic acid administered orally to laying hens

Radiolabelled racemic cypermethrin, and the cis and trans isomers of 3-(2,2-dichlorovinyl)-2,2-dimethylcyclopropanecarboxylic acid (labelled at C-1 of the cyclopropane ring) were each separately administered orally in feed for three consecutive days to White Leghorn laying hens. The amount of individual compound dosed was approximately 7.5 mg per hen per day. Radiocarbon was eliminated very rapidly in excreta. Tissue residues were generally very low with the exception of fat depots, but trace amounts of radiocarbon residues were still detectable in fat, liver and kidney 11 days post-treatment. Residues were detected in the egg albumen of hens treated with cypermethrin and cis isomer of the acid, but none was detected from trans acid. Metabolites identified included products arising from the hydrolysis of the ester bond of cypermethrin, followed by oxidative attack on one or both methyl groups. The rate of oxidative attack on methyl groups was influenced by the geometry of the dichlorovinyl group. On the basis of the metabolites identified a metabolic pathway for cypermethrin in laying hens was proposed which included hydrolysis of the ester bond followed by oxidation of methyl group(s). The data indicate that use of cypermethrin as recommended should not produce residues in eggs and meat of laying hens at levels that are of toxic concern.