Some laboratory investigations relevant to the possible use of new pyrethroids in control of mosquitoes and tsetse flies

Cypermethrin, fenvalerate, permethrin, (S)-α-cyano-3-phenoxybenzyl (1R,cis)-3-(2, 2-dibromovinyl)-2, 2-dimethylcyclopropanecarboxylate (NRDC 161) and (R,S)-α-cyano-3-phenoxybenzyl 2, 2,3, 3-tetramethylcyclopropanecarboxylate (S-3206; WL 41706) have been tested against adult mosquitoes (Anopheles stephensi) and tsetse flies (Glossina austeni). They possess many of the necessary characteristics such as high intrinsic toxicity, low volatility, and high stability but vary considerably in the contact action of their spray residues.     

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 activity of some pyrethroids against Periplaneta americana and Blattella germanica

The knockdown and contact killing actions of various pyrethroids were compared using Blattella germanica and Periplaneta americana. A wide range of knockdown activity was found; 5-benzyl-3-furylmethyl (1R)-cis-3-(dihydro-2-oxo-3-thienylidenemethyl)-2,2-dimethylcyclopropanecarboxylate (RU 15525) acted fastest, more rapidly than pyrethrins, against B. germanica as well as having a low LD₅₀ value. Topical application and direct spray tests showed that (S)-α-cyano-3-phenoxybenzyl (1R)-cir-3-(2,2-dibromovinyl)-2,2-dimethylcyclopropanecarboxylate (NRDC 161) was more active as a killing agent, by an order of magnitude, than cismethrin, the next most active compound, and also had considerable knockdown activity. Piperonyl butoxide generally had little synergist effect. Female P. americana were over three times more tolerant than males to a range of insecticides applied topically. Residual knockdown action in the WHO resistance test was observed to provide baseline data. There was little overlap in speed of action between pyrethroids and other insecticides among the compounds tested.     

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.     

Pharmacokinetic behavior of enantiomeric pyrethroid esters in the cockroach,Periplaneta americana L

The potent pyrethroid insecticide NRDC 157 (I; 3-phenoxybenzyl (1R, cis)-3 - (2,2-dibromovinyl)-2,2-dimethylcyclopropanecarboxylate) and its insecticidally inactive 1S, cis enantiomer (II) have similar cuticular penetration rates and are detectable in the hemolymph, nerve cord, fat body, and midgut of the American cockroach, Periplaneta americana, within 2 hr of topical application at 0.17 μg/g, a just-lethal dose of I. At this dose, both enantiomers show similar distribution patterns in these tissues, but symptoms of intoxication are seen only with I. Steady state concentrations of both enantiomers in the hemolymph and nerve cord are between 1.2 × 10^?7 and 1.7 × 10^?7M. I and II are not detectably hydrolyzed by fat body, nerve cord, and hemolymph preparations and are not detectably oxidized by fat body preparations in vitro, but a very low oxidation rate is measured for II, but not I, in nerve cord preparations. These results do not demonstrate a pharmacokinetic basis for the difference in insecticidal activity between enantiomers and therefore it is likely that the site of pyrethroid action is stereospecific. The use of the inactive enantiomer II as a model to study the effects of dose on penetration and distribution in the absence of symptoms is explored.     

The optical isomers of α-cyano-3-phenoxybenzyl 3-(1,2-dibromo-2,2-dichloroethyl)-2,2-dimethylcyclo-propanecarboxylate and their insecticidal activities

Bromination of the dichlorovinyl group of cypermethrin yielded a new compound which is a highly potent insecticide. This dibromo adduct has four asymmetric centres and therefore can exist as a mixture of 16 stereoisomers. To establish the influence of the absolute configuration at the chiral centres on the biological activities of these isomers, each of the isomers was isolated; their insecticidal activities against larvae of Heliothis virescens, and adult Calliphora erythrocephala and Blattella germanica were then determined and compared with those of (S)-α-cyano-3-phenoxybenzyl (1R)-cis-3-(2,2-dibromovinyl)-2,2-dimethylcyclopropanecarboxylate (deltamethrin NRDC 161), of fenvalerate, and of the eight stereoisomers of cyper methrin.     

Pharmacokinetics of cis- and trans-substituted pyrethroids in the American cockroach

The pharmacokinetic behavior of cis and trans isomers of pyrethroids after topical application to adult male American cockroaches (Periplaneta americana L.) was examined using the insecticidal 1R,cis (NRDC 157; I) and 1R,trans (NRDC 163; III) isomers of 3-phenoxybenzyl 3-(2,2-dibromovinyl)-2,2-dimethylcyclopropanecarboxylate and their insecticidally inactive 1S,cis (II) and 1S,trans (IV) enantiomers. III was detected in the hemolymph, nerve cord, and fat body of animals receiving a just-lethal dose (0.6 μg/g) within 2 hr after topical application. The pattern of accumulation of III was similar to that previously determined for I at a just-lethal dose, but quantitative comparisons revealed that the cis isomer I was delivered from the site of application to the nerve cord eightfold more efficiently than III. The inactive enantiomers II and IV were administered at the same dose (0.60 μg/g) to compare the rates of cuticular penetration and in vivo degradation of cis and trans isomers in the absence of intoxication symptoms. II penetrated somewhat more rapidly than IV and achieved higher levels in whole body extracts, but there was no difference between isomers in the rates of overall degradation of applied pyrethroid. These studies demonstrated a twofold difference in internal availability, but they did not reveal sufficient pharmacokinetic selectivity to explain the large difference in the access of I and III to the nerve cord observed in the tissue uptake studies. III was hydrolyzed by nerve cord homogenates in vitro at a rate 5 times greater than that of I, but neither ester underwent detectable oxidative metabolism in this system. Local selective metabolism by the nerve cord is suggested as an important determinant of the levels of parent pyrethroid found in this tissue. These results demonstrate the significance of pharmacokinetic selectivity in determining the relative access of topically applied cis- and trans-substituted pyrethroids to the insect nervous system.     

Further evaluation of permethrin for biting-fly control

Laboratory tests in a fly chamber and field trials in the UK and Australia have shown that permethrin, (3-phenoxybenzyl (1R,1S)-cis,trans-3-(2,2-dichlorovinyl)-2, 2-dime-thylcyclopropanecarboxylate) containing 25: 75 cis: trans isomers, applied as water emulsions to cattle and horses will control biting flies. Satisfactory protection against the stable fly, Stomoxys calcitrans (L.) and excellent control against the horn fly, Haematobia (Lyperosia) irritans (L.) was achieved on cattle. Good control was obtained on horses against the stable fly and the sand fly Culicoides spp. These early results are encouraging and toxicity and residue data suggest that permethrin would be a safe insecticide to use on livestock for the control of biting flies of veterinary importance.     

Response of susceptible and resistant peach-potato aphids Myzus persicae (Sulz.) to insecticides in leaf-dip bioassays

The response of susceptible (S), moderately resistant (R₁) and strongly resistant (R₂) peach-potato aphids, Myzus persicae (Sulz.) to organophosphorus, carbamate and pyrethroid insecticides was tested by a leaf-dip bioassay. The aphids were placed on potato leaves (dipped in insecticide solutions 1–2 or 24 h before infestation) and their mortality examined 48 h later. R₁ aphids were virtually susceptible to most of the carbamates, demephion and acephate, but were slightly to moderately resistant (2.1–9.4 times) to permethrin, cypermethrin and (S)-α-cyano-3-phenoxybenzyl (1R)-cis-3-(2,2-dibromovinyl)-2,2-dimethylcyclopropanecarboxylate (I), (NRDC 161), to 5,6,7,8-tetrahydro-2-methylquinolin-4-yl dimethylcarbamate (II), (Hoechst 25 682) and demeton-S-methyl. R₂ aphids resisted more strongly or very strongly (between 65 and 1280 times) the pyrethroids, demeton-S-methyl (×94), II (×83) and demephion (×9), and were slightly to moderately (2–5 times) resistant to acephate, pirimicarb, ethiofencarb and 2-(dimethylcarbamoyloxyimino)-3-methoxyimino-N,N- dimethylbutyramide (III), (DPX 3853). Both resistant strains were susceptible to nitrilacarb [4,4-dimethyl-5-(methylcarbamoyloxyimino)pentanenitrile] complex (1:1) with zinc chloride (IV), (AC 85 258). The implications of these results in terms of practical aphid control are discussed.     

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.     

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.     

The vinylogous relationship in some pyrethroids

Attention is drawn to a vinylogous relationship between the structure of certain biologically-active pyrethroids. A series of racemic α-cyano-3-phenoxybenzyl 2-(2,2-dichlorovinyl)-1-phenylcyclopropanecarboxylates, based on this relationship, were synthesised and were found to be only moderately toxic to Musca domestica, Spodoptera littoralis and Leptinotarsa decemlineata.     

Insecticidal activity of the pyrethrins and related compounds. VII. Insecticidal dihalovinyl analogues of cis and trans chrysanthemates

Eighteen esters of resolved cis- and trans-3-(2,2-difluoro, -dichloro or -dibromovinyl)-2,2-dimethylcyclopropanecarboxylic acids with 5-benzyl-3-furylmethyl, 3-phenoxybenzyl and α-cyano-3-phenoxybenzyl alcohols were prepared and evaluated for insecticidal activity against Musca domestica L. and Phaedon cochleariae Fab. Chlorine and bromine substituted esters are more active, in general, than those with fluorine, and in the most active esters, the cis isomer is more effective than the trans.     

The pyrethrins and related compounds. Part XXX: Esters from acids with mono-halovinyl side chains

Esters of 3-phenoxybenzyl alcohol and its α-cyano derivative with 2,2-dimethylcyclopropanecarboxylic acids bearing (E)- or (Z)-3-monohalovinyl side chains (haloiodo, bromo, chloro or fluoro) were synthesised and had moderate to high insecticidal activities, but these were generally lower than those of established pyrethroids with the corresponding 3-(dihalovinyl) side chains. Compounds with 3-(2-chloroprop-1-enyl) side chains were intermediate in potency between the related chrysanthemates and 3-(dichlorovinyl) esters.     

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.     

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.     

Comparison of symptomatic and neurophysiological activities of enantiomers of the insecticide 3-phenoxybenzyl 1-(4-ethoxyphenyl)-2,2-dichlorocyclopropane-1-carboxylate

The insecticidal activities of optical isomers of 3-phenoxybenzyl 1-(4-ethoxyphenyl)-2,2-dichlorocyclopropanecarboxylate and related compounds were measured with American cockroaches and their knockdown activities were evaluated with house flies. The activities of the S(?)-isomer of the dichlorocyclopropanecarboxylate were higher than those of the R(+)-isomer. The effects of the compounds on the inward membrane currents induced by a stepdepolarizing pulse in crayfish axonal membranes were examined under voltage clamp conditions by the sucrose gap method. The compounds induced a tail current upon step repolarization of the membrane. The tail current decayed to zero in each record, but developed with time after the start of application of the compound until a steady level was reached. The rate of decay of the tail current observed in axonal membranes treated with the S(?)-isomer was slower than with the R(+)-isomer. The rates of development of the tail current induced by the two isomers were not very different.     

α-氰基-3-苯氧基苄醇乙酸酯立体选择性水解酯酶产生菌的筛选及酶学特性初探

经过酵母菌富集培养,以α-氰基-3-苯氧基苄醇乙酸酯为唯一碳源培养和分离,并进一步用手性HPLC法复筛,得到了两株优先立体选择性水解(S)-α-氰基-3-苯氧基苄醇乙酸酯的酵母菌菌株S11和S25。两株酵母菌均能产生耐酸酯酶,在pH 3.0时对α-氰基-3-苯氧基苄醇乙酸酯进行立体选择性水解,产物对映体过量值(ee/em>p)均在95％以上,转化率(C)分别达50％和46％。测定了菌株S11的生长曲线,并对其产酶特性进行了初探,发现其所产酶为生长偶联型的胞内酶。     

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.     

Comparative fungitoxicity of the insecticide permethrin and ten degradation products

The toxic effects of permethrin and ten of its degradation products on the growth of ten fungi were determined. Permethrin was relativelynon-toxic, with an EC₅₀ of > 100 mg litre^?1 but six of the degradation products were significantly (P= 0.05) more inhibitory. The ester hydrolysis products, 3-phenoxybenzyl alcohol and 3-(2,2-dichlorovinyl)-2,2-dimethylcyclopropanecarboxylic acid, had EC₅₀ values ranging from 8 to > 100 and 20 to > 50 mg litre^?1, respectively. Other degradation products that were more toxic than permethrin included 3-phenoxybenzaldehyde and 3-phenoxybenzoic acid, with EC₅₀ values as low as < 1 mg lite^?1. Hydroxylated and substituted-benzene metabolites were non-toxic. Combinations of selected test compounds yielded both synergistic, antagonistic and additive interaction responses, depending upon the test system employed.