Foliar Persistence and Residual Activity of Tebufenozide Against Spruce Budworm Larvae

A field study was conducted to investigate the persistence of tebufenozide in white spruce foliage. An aqueous suspension concentrate formulation, RH-5992 2F, was sprayed over single trees at three dosage rates, 35, 70 and 140 g of the active ingredient (AI), in 2·0 litre ha⁻¹, using ground application equipment. Foliage was collected at different intervals of time up to 64 days after treatment and tebufenozide residues were measured by high-performance liquid chromatography. Foliage was also fed to laboratory-reared 4th- and 6th-instar spruce budworm (Choristoneura fumiferana Clemens). The data indicated that tebufenozide residues in foliage declined with time according to first-order kinetics. The average rate-constant and half-life of disappearance (DT₅₀) were 0·0340 and 20·45 days, respectively. Larval mortality declined gradually, corresponding to the residues, but was still appreciable (49 to 70%) when the larvae were fed with foliage collected 64 days after treatment. The amount of foliage consumed by the larvae decreased when foliar residues of tebufenozide increased, thus indicating anti-feedant activity of the chemical. The LD₅₀ values for both instars were similar and averagedc.25 ng per insect, but the LD₉₀ values were significantly lower for 4th-instar than for 6th-instar, at 63·6 and 96·1 ng per insect respectively. This implies that, theoretically, at a foliar concentration of 1·0 μg tebufenozide g⁻¹ foliage (fresh wt), the spruce budworm larva needs to consume 65 to 100 mg of foliage in 10 days to cause mortality in about 90% of a population of the insect.     

Response of two lacewing species to biorational and broad-spectrum insecticides

Green lacewings, includingChrysoperla rufilabris (Burmeister) andCeraeochrysa cubana (Hagen), are predators of small, soft-bodied insects including whiteflies. The silverleaf whitefly,Bemisia argentifolii Bellows & Perring [formerlyB. tabaci (Gennadius) strain B], is an important pest of agronomic, vegetable and ornamental crops. Practical use of these lacewings as biological control agents would be facilitated by better understanding of their responses to both biorational (selective) and broad-spectrum insecticides. The topical and residual toxicity of azadirachtin (Azatin-EC^TM), insecticidal soap (M-Pede^TM), paraffinic oil (Sunspray Ultra-Fine Spray Oil^TM) and the pyrethroid bifenthrin (Brigade^TM) to eggs, larvae and adults of the lacewings were studied in the laboratory. Larvae ofC. cubana were much more tolerant to residues of bifenthrin than wasC. rufilabris and were somewhat more tolerant to topically applied soap. At normal field concentrations, azadirachtin (0.005%, by wt a.i.), paraffinic oil (1.0% by volume) and soap (1.0% by volume) were not toxic to larvae or adults of either species either topically or residually. Oil was toxic topically to eggs but azadirachtin and soap were not. Bifenthrin was toxic topically and residually to larvae and adults but was not so toxic to eggs as was oil. Thus, selectivity of all materials tested was relative to lacewing species and lifestage. The relative tolerance to insecticide residues exhibited byC. cubana larvae may be related to its trash-carrying habit, suggesting that use of trash-carrying chrysopids in place of non-trash carriers for augmentative biological control would increase options for non-disruptive chemical intervention when necessary.     

Toxicity of ddt and malathion to various larval stages of Mamestra brassicae L.

The toxicity of DDT and malathion to the larvae of Mamestra brassicae was determined following several methods of application. The toxicity (LD₅₀), expressed as μg insecticide per g of insect, did not change significantly between larval instars (a) when either insecticide was injected into fourth to sixth instars; (b) when DDT was applied in the food of fifth and sixth instars; or (c) when malathion was applied topically to second to sixth instars. Significant changes in toxicity were found between successive instars when DDT was applied topically, but there was no clear trend. When malathion was applied in the food, the fifth instars were more susceptible than the sixth instars; it was found that the former consumed a toxic dose of malathion at a greater rate, and that probably malathion was degraded in the gut at a slower rate. In a contact test, the first to third instars were far more susceptible than the later instars to malathion; with DDT this trend was much less marked. Uptake studies with [¹⁴C]malathion showed that differences in the contact toxicity of malathion between instars could be explained, at least partly, by the decline in uptake per unit weight with increasing larval size.     

Toxicity of chlordimeform and amitraz to the egyptian cotton leafworm (Spodoptera littoralis) and the tobacco budworm (Heliothis virescens)

The relative toxicity (μg a.i. g^?1 body wt) of the formamidine insecticide chlordimeform (CDM) and the triazapentadiene insecticide amitraz was examined in two species of noctuid moth Spodoptera littoralis and Heliothis virescens. When applied topically, there was an unexpected and marked difference in the toxicity of CDM base and its hydrochloride to adults of both species, the salt being appreciably more toxic. For H. virescens at least, this difference in toxicity could not be explained by differences in penetration. This trend was reversed for larval instars of S. littoralis; while there was relatively little difference in the toxicity of the base to adult and larval stages, the salt was at least 1000-fold more toxic to adults than to larvae. N¹-Demethylchlordimeform (DCDM) was the only metabolite of CDM to show biological activity against either species, but was much less toxic than the parent compound. Amitraz was far less toxic than either CDM or DCDM; like the CDM salt, it appeared to be more toxic to adult than larval stages of S. littoralis. Application of piperonyl butoxide significantly increased the toxicity of the CDM salt, DCDM and amitraz to adult H. virescens, the synergist being particularly effective with DCDM and amitraz. In contrast, piperonyl butoxide had no significant effect on the toxicity of DCDM, and slightly antagonised the toxicity of DCDM to fourth-instar larvae of S. littoralis.     

Comparative toxicology of AC 217,300 in various species of insects

AC 217,300 was highly toxic by topical application to adult Musca domestica and Blattella germanica, and larvae of Spodoptera eridania, with LD₅₀ values in μg/g of 20, 19, and 61, respectively. It was relatively nontoxic to Diabrotica undecimpunctata howardi beetles and Heliothis virescens larvae with LD₅₀ values of 165 and >883. When incorporated into baits, AC 217,300 was still highly toxic to M. domestica, B. germanica, and S. eridania. A significant increase in toxicity to H. virescens was observed although the percentage mortality was only 45%. AC 217,300 was not effective against D. undecimpunctata with either mode of application. A comparison of toxicity with tissue residues indicated that AC 217,300 was highly toxic to M. domestica, B. germanica, H. virescens, and S. eridania if it was absorbed. However, D. undecimpunctata appeared to be much less sensitive to AC 217,300, as only 18% mortality was observed with corresponding tissue concentrations two to six times those producing 95–100% mortality in M. domestica and S. eridania. Exposure of M. domestica to an AC 217,300-treated bait for 3–6 hr was sufficient to cause 50–100% mortality after 2 days and 95–100% mortality by 7 days. With B. germanica, a 1- to 3-day exposure resulted in 75–90% control within 7 days, while exposure for 3–7 days gave 90–100% control. Environmental temperature had a pronounced effect on the toxicity of AC 217,300 to both M. domestica and B. germanica. A 20-fold increase in toxicity was observed when the environmental temperature was raised from 21 to 32°C. This observation, in concert with the symptoms of intoxication, support the hypothesis that AC 217,300 is an inhibitor of energy production. Approximately 85 and 87% of the total residue of AC 217,300 extracted from treated M. domestica and B. germanica, respectively, was parent material. Six minor metabolites were detectable, of which three were tentatively identified by cochromatography with authentic standards. None of the identified metabolites had any insecticidal activity in vivo, suggesting that AC 217,300 is the actual toxicant.     

Fumigant toxicity is the major route of insecticidal activity of citruspeel essential oils

Dosages (>10 ml mg⁻¹ against Callosobruchus maculatus F. or Sitophilus zeamais Motsch; >20 ml kg⁻¹ against Dermestes maculatus Deg.) of citruspeel oils reduced oviposition or larval emergence through parental adult mortality, but had no residual activity on the eggs or larvae produced by survivors. Oil-treated grains (7 ml kg⁻¹ against C. maculatus) or dried fish (28 ml kg⁻¹ against D. maculatus) which caused 100% mortality 1 h after application lost all activity within 24 h, thus confirming the non-residual nature of the effects. The activity of limepeel oil against test insects was found to be dependent on the time interval between the application of oil and start of bioassays. The non-volatile residues of limepeel oil were not toxic to insects on glass and dried-fish surfaces. Topical toxicity trials against D. maculatus adults also illustrated the relative unimportance of contact toxicity of citrus oils, as appreciable mortality (at application rates of up to 2 μl per insect) was obtained only when treated insects were confined in air-tight glass chambers. The volatility of toxic constituents in the oils was further illustrated by mortality of untreated C. maculatus adults confined in air-tight chambers with topically treated D. maculatus. A more efficient way to use citruspeel essential oils to control insects would be as a fumigant in relatively enclosed or air-tight systems.     

Compatibility of spinosad with predaceous mites (Acari) used to control Frankliniella occidentalis (Pergande) (Thysanoptera: Thripidae)

BACKGROUND: Spinosad is a biopesticide widely used for control of Frankliniella occidentalis (Pergande). It is reported to be non‐toxic to several predatory mite species used for the biological control of thrips. Predatory mites Typhlodromips montdorensis (Schicha), Neoseiulus cucumeris (Oudemans) and Hypoaspis miles (Berlese) have been used for control of F. occidentalis. This study investigated the impact of direct and residual toxicity of spinosad on F. occidentalis and predatory mites. The repellency of spinosad residues to these predatory mites was also investigated. RESULTS: Direct contact to spinosad effectively reduced the number of F. occidentalis adults and larvae, causing > 96% mortality. Spinosad residues aged 2–96 h were also toxic to F. occidentalis. Direct exposure to spinosad resulted in > 90% mortality of all three mite species. Thresholds for the residual toxicity (contact) of spinosad (LT₂₅) were estimated as 4.2, 3.2 and 5.8 days for T. montdorensis, N. cucumeris and H. miles respectively. When mites were simultaneously exposed to spinosad residues and fed spinosad‐intoxicated thrips larvae, toxicity increased. Residual thresholds were re‐estimated as 5.4, 3.9 and 6.1 days for T. montdorensis, N. cucumeris and H. miles respectively. Residues aged 2–48 h repelled T. montdorensis and H. miles, and residues aged 2–24 h repelled N. cucumeris. CONCLUSION: Predatory mites can be safely released 6 days after spinosad is applied for the management of F. occidentalis. Copyright © 2011 Society of Chemical Industry     

Sulfur in pesticide action and metabolism: Edited by J. D. Rosen,P. S. Magee,and J. E. Casida,American Chemical Society,Washington, D.C., 1981. 172 pp., $33.00

The distribution of ¹⁴C-acid-, ¹⁴C-alcohol-, and ¹⁴C-cyano-labeled deltamethrin and selected metabolites were followed in the liver, blood, cerebrum, cerebellum, and spinal cord after iv administration of a toxic, but nonlethal dose (1.75 mg/kg) to rats. Approximately 50% of the dose was cleared from the blood within 0.7–0.8 min, after which the rate of clearance decreased. 3-Phenoxybenzoic acid (PBacid) was isolated from the blood in vivo, and was also the major metabolite when ¹⁴C-alcohol-labeled deltamethrin was incubated with blood in vitro. Deltamethrin levels in the liver peaked at 7–10 nmol/g at 5 min and then decreased to 1 nmol/g by 30 min. In contrast, peak central nervous system levels of deltamethrin were achieved within 1 min (0.5 nmol/g), decreasing to 0.2 nmol/g at 15 min, and remaining stable until 60 min. peak levels of deltamethrin did not correspond to the severity of toxicity, although the levels of non-pentane-soluble radiolabel did appear to correlate with motor signs of toxicity. Experiments with brain homogenates, using in vivo concentrations of deltamethrin, failed to reproduce the pentane-unextractable radioactivity in vitro nor was any metabolism demonstrated.     

Toxicity,persistence and efficacy of indoxacarb and two other insecticides on Plutella xylostella (Lepidoptera: Plutellidae) immatures in cabbage

Toxicities of indoxacarb on eggs and 5-day-old larvae of diamondback moth, Plutella xylostella L., on cabbage and those of field-aged leaf residues on 5-day-old larvae were determined in the laboratory. The persistence and efficacies of indoxacarb and two other newer insecticides (spinosad and emamectin benzoate) to P. xylostella were tested under field conditions. Results from laboratory bioassays indicate that indoxacarb was highly toxic to P. xylostella larvae through food ingestion, with LC₅₀ and LC₉₀ values of 24.1 and 90.1 mg AI l ^{- 1}, respectively. However, indoxacarb had no significant effects on eggs and larvae through direct contact compared with water control. The toxicity of field-aged leaf residues of indoxacarb (0-, 3-, 5-, 7-, 10-, 14-, 17- and 21-day-old residues) declined slowly and gradually under the field conditions in South Texas. Almost all larvae died on day 5 after feeding on the leaves with 0 - 14-day residue, and the mortalities were as high as 94 and 78% for the 14- and 17-day-old leaf residues. With one application, indoxacarb suppressed P. xylostella larvae below the economic threshold for 14 - 21 days. Two field trials showed that indoxacarb at 0.05 - 0.07 kg AI ha ^{- 1} was effective against P. xylostella, providing marketable cabbage with three applications per season. In addition, indoxacarb was as effective as spinosad, and significantly more effective than emamectin benzoate.     

Biological activity of neem seed kernel extracts and synthetic azadirachtin against larvae of Plutella xylostella L

The activity of two neem extracts, AZT and NEEM-AZAL (containing 30 and 3 mg azadirachtin ml^?1 respectively) and synthetic azadirachtin (AZ) against second-instar larvae (L2) of Plutella xylostella L. was examined using leafdip bioassays. On Chinese cabbage, AZ was significantly (P <0.05) less toxic (3 to 4-fold; LC₅₀ 0.54 μg AZ ml^?1) than either neem extract against a laboratory strain of P. xylostella (FS). The LC₅₀ values for AZT against the FS and another laboratory strain (Wellcome) were not significantly different on Chinese cabbage. The activity of AZT against the FS and Wellcome strains was similar on Chinese cabbage and Brussels sprout. AZT was significantly less toxic (3-fold) on Brussels sprout against an acylurea-resistant field strain (Sawi) when compared with the FS strain on Chinese cabbage. Larval mortality (at day 13) was found to increase with increasing exposure time of P. xylostella (FS) larvae to AZT-treated Chinese cabbage, although there was little difference in mortality between 48 and 120 h exposure. When AZT, NEEM-AZAL and AZ were applied at a dose (1 μg AZ ml^?1) which gave end-point mortalities between 50 and 90% (at day 13), all treatments delayed the development of a proportion of surviving larvae but no morphogenetic abnormalities were observed in larvae which reached pupation. Evidence for antifeedant (reduced weight gain) and repellant effects (choicechamber) for AZT were observed with L2 P. xylostella (Wellcome) on Chinese cabbage. AZT was also shown to have ovicidal activity against P. xylostella (Wellcome) at relatively high dose ranges (10-1000 μg AZ ml^?1) as well as some contact activity (FS strain) in topical bioassays. In residual bioassays on glass with adults of the hymenopteran endo-larval parasitoid of P. xylostella, Diadegma semiclausum (Ichneumonidae), AZT showed little or no activity at rates up to 1000 μg AZ ml^?1. In medium-volume (MV, 200 litre ha^?1) and ultra-low-volume (c. 1 litre ha^?1) spray bioassays on Brussels sprout, AZT gave 16-92% and 88-100% mortality respectively (Wellcome strain) at rates approximating to 1-20 g AZ ha^?1. The residual activity of AZT and NEEM-AZAL against P. xylostella (FS) on Brussels sprout (MV spray) was observed to decrease appreciably after three days, the decline in activity being particularly marked for NEEM-AZAL.     

Toxicology and metabolism of chloromethiuron in Boophilus microplus larvae

The toxicity of the acaricide chloromethiuron, 3-(4-chloro-o-tolyl)-1,1-dimethyl- (thiourea), and of nine related compounds to Boophilus microplus larvae was determined by a spray-tower method. Four of these compounds were toxic but only chloromethiuron and its N-demethyl derivative were of practical importance. Metabolism of [¹⁴C]chloromethiuron, in the formamidine-susceptible but organo-phosphorus-resistant Mt. Alford strain, was compared with that in a chlordimeform-selected Mt. Alford strain, which in laboratory tests was two to three times resistant to chloromethiuron, chlordimeform and amitraz. The latter strain produced smaller quantities of the toxic N-demethyl derivative than the Mt. Alford strain; this was the only resistance mechanism determined. Rates of degradation of chloromethiuron were the same in both strains. Piperonyl butoxide strongly antagonised the toxicity of chloromethiuron by 18 to 33 times and depressed the production of the N-demethyl derivative in both strains (0.3 times that of the control), while degradation rates of chloromethiuron itself were halved by piperonyl butoxide in both strains. These results indicated that the parent material was not toxic until oxidised to the N-demethyl derivative. As, in addition, some symptoms of chloromethiuron toxicosis in larvae were similar to those caused by formamidine acaricides, a common mode of lethal action is suggested.     

Foliar residues and toxicity to Aphis citricola of three systemic insecticides applied to the soil in a citrus grove

A study was made of the accumulation of aldicarb, ethiofencarb and dimethoate in citrus leaves and fruit; the toxicity of these insecticides to the spirea aphid (Aphis citricola Van der Goot) was also studied. The effectiveness of the treatments was affected mainly by the rate of accumulation of the toxicant in the leaves. At 18 g a.i. per tree, the greatest residues found in the leaves were 106, 12.2 and 1.3 μg 8^?1 fresh weight for aldicarb, ethiofencarb and dimethoate, respectively. The concentration in mature leaves was very similar to that in young leaves. The residue levels in the mature fruits were much lower than in the leaves. The main components of the residues in the leaves were aldicarb sulphoxide [2-methyl-2-(methylsulphinyl)- propionaldehyde O-methylcarbamoyloxime], dimethoate, omethoate and ethiofencarb sulphoxide [2-(ethylsulphinylmethyl)phenyl methylcarbamate]. A laboratory study with synthetic diets showed similar toxicity for all three insecticides, whereas in detached leaves, or when taken up by citrus trees, ethiofencarb was the least toxic to the aphids.     

Lethal and sublethal effects of the neem insecticide formulation, ‘Margosan-O’, on the pea aphid

The effects of ‘Margosan-O’ (MO) on the pea aphid, Acyrthosiphon pisum (Harris), were determined. MO significantly reduced population increase of A. pisum in a concentration-dependent manner. At a concentration equivalent to 100 mg litre^?1 of azadirachtin, population increase was c. 3.5 times lower than the control. In more detailed studies, MO significantly reduced the number of molts, longevity, and fecundity of A. pisum that had been reared on treated broad bean. Viciafaba L., plants. MO also reduced the longevity and fecundity of young adult A. pisum exposed to MO-treated broad bean. MO was slow-acting against A. pisum. Mortality caused by MO stabilised seven days after newborn A. pisum were exposed to treated broad bean and 10 days for adults. The seven day LC₅₀ for individuals exposed from birth was 27.50 mg azadirachtin liter^?1 while the 10 day LC₅₀ for adults was 53.32 mg liter^?1. Contrary to previous studies suggesting that neem insecticides are not contact toxicants, we found that MO applied topically to adult A. pisum caused effects similar to those found in individuals that fed upon treated plants. However, MO was slower-acting when applied topically. Mortality in adult A. pisum caused by topically applied MO stabilised 17 days after treatment with a resultant LD₅₀of 2.91 μg azadirachtin g^?1.     

Residual toxicity of lambda-cyhalothrin on apple foliage toAmblyseius fallacis and the tarnished plant bug,Lygus lineolaris

The residual toxicity of lambda-cyhalothrin on leaves from a treated apple orchard to a mite predator,Amblyseius fallacis (Garman), in the laboratory, declined to one-third of its original level within 3 weeks. The absence ofA. fallacis on apple trees during the pink bud stage coupled with the results of this study pave the way for the development of integrated pest management strategies where key pre-bloom pests, such as the tarnished plant bug,Lygus lineolaris (Palisot de Beauvois), may be controlled with lambda-cyhalothrin with little if any toxic effects to the predator later in the season. Two years of field testing indicated that 10 g a.i./ha of lambda-cyhalothrin applied at pink was very effective against the tarnished plant bug.     

Distribution and excretion of [14CH3S]methamidophos after intravenous administration of a toxic dose and the relationship with anticholinesterase activity

The tissue distribution and excretion of [¹⁴CH₃S]methamidophos was followed in female Sprague-Dawley rats after intravenous injection at a toxic, but nonlethal, dose (8 mg/kg). Radiolabel was rapidly distributed to all tissues at approximately equal concentrations. Peak tissue levels were achieved within 1–10 min except in the central and peripheral nervous system where peak levels (40 nmol/g) were found between 20 and 60 min, corresponding to peak signs of toxicity. Within 24 hr of dosing, 47% of the radioactivity was recovered in the urine and 34% as ¹⁴CO₂ with <5% in the feces over 7 days. Cholinesterase (ChE) inhibition was measured in erythrocytes, plasma, and various regions of the central nervous system (CNS) at selected times after administration of methamidophos at 8 mg/kg. The degree of acetylcholinesterase (AChE) inhibition in the three CNS regions was similar, reaching a minimum of 15–20% of control values at 30–60 min, when toxicity was most severe. The degree of erythrocyte AChE inhibition was less than that of the CNS although the time course was similar. Plasma ChE inhibition was more rapid than that of the CNS or erythrocytes and reactivation was slower. When similar concentrations of methamidophos to those found in vivo were incubated with CNS homogenates, plasma, or erythrocytes in vitro (5 × 10^?5M) a similar degree of inhibition occurred over the same time course. It is, therefore, concluded that the cholinergic toxicity produced by methamidophos is a result of the in vivo stability of this compound combined with its entry into the nervous system in sufficiently high concentrations to inhibit AChE.     

Distribution and loss of phorate residues in the foliage of broad bean plants following root uptake of 14C-labelled phorate

¹⁴C-Methylene labelled phorate was added to nutrient solutions supplying the roots of young broad bean plants and after 24 h absorption, fresh nutrient was substituted. The radiolabel accumulated at the leaf margins was initially associated with solvent-soluble toxic metabolites. Radiolabel extracted from foliage which developed after the treatment was mainly in water-soluble form. The maximum concentration of toxic material occurred in the marginal areas of the leaves after 5 or 6 days and in the central portions after 2 days. The concentrations declined to half of their peak values in 4–6 days from leaf-margin tissue and in 2 days from the central tissues. Water-soluble label did not accumulate to any significant extent. Most was found in the marginal areas but concentrations built up slowly reaching a maximum after about 2 weeks, declining slowly thereafter.     

三种杀螨剂对山楂叶螨的毒力评价

为筛选出高效防治山楂叶螨Amphitetranychus viennensis Zacher的杀螨剂,利用玻片浸渍法和叶片残毒法测定了3种杀螨剂对其3种螨态的室内毒力,并对不同浓度杀螨剂的田间防效进行了测定。结果表明:240 g/L螺螨酯、110 g/L乙螨唑和43%联苯肼酯中仅联苯肼酯对山楂叶螨雌成螨有毒力,其LC50为37.65 mg/L;3种杀螨剂均能毒杀卵及幼螨,毒力大小依次为乙螨唑联苯肼酯螺螨酯;同一杀螨剂对幼螨的毒力均高于对卵的毒力。240 g/L螺螨酯和110 g/L乙螨唑对山楂叶螨的总体防效较好,除螺螨酯4 000倍液处理的防效在药后30 d达到最大97.11%外,其余各处理均在药后15 d达到最大,防效为88.76%~96.14%;但二者速效性较差,药后1~7 d防效均低于对照;而螺螨酯4 000、5 000倍液处理及乙螨唑5 000倍液处理的持效性较好,药后30 d防效仍有97.11%、90.90%和93.06%,均显著高于对照。43%联苯肼酯对山楂叶螨的总体防效在3种杀螨剂中最高,其1 800、2 500倍液处理分别在药后7 d和3 d时防效达到最大99.79%和98.64%;1~7 d防效为97.45%~99.79%,显著高于其余杀螨剂和对照;30 d时防效分别达98.14%和96.19%,速效性和持效性均较好。表明螺螨酯和乙螨唑对山楂叶螨的持效性较好,联苯肼酯则有良好的速效性和持效性,可以按照其不同特点推广应用。     

Toxicity,penetration, and metabolism of AC 217,300 (AMDRO) in the tobacco budworm (Heliothis virescens) by various methods of application

Penetration was found to be the major factor in the selective toxicity of AC 217,300 in Heliothis virescens larvae. When applied topically in either acetone or dimethyl sulfoxide solutions, less than 3 and 11%, respectively, of the applied dose penetrated the cuticle after 72 hr. Ingestion resulted in tissue residues of 45–55% of the applied dose, and increased toxicity 40 to 140-fold over topical application. Five primary metabolites were tentatively identified by cochromatography with authentic standards. At least 10 other minor metabolites were detected. The lack of insecticidal activity with any of the known metabolites, as well as the tissue residues and metabolic profile, suggested that AC 217,300 is the actual toxicant.     

Topical and residual toxicity of six pesticides to <Emphasis Type="BoldItalic">Orius majusculus</Emphasis>

The toxicity of six pesticides (four insecticides and two fungicides) to Orius majusculus (Reuter) (Hemiptera: Anthocoridae) adults and nymphs was determined using different exposure methods. Mortality upon topical exposure to abamectin, endosulfan and spinosad at recommended field doses ranged from 56% to 100% after 24 h. However, in leaf residue tests, toxicity to both life stages decreased significantly, ranging from 0% to 33% mortality. Benomyl and copper salts + mancozeb (fungicides) were much less toxic to O. majusculus, with less than 15% mortality of either adults or nymphs in topical and residue bioassays. In persistent toxicity tests, insects were exposed to the same three insecticides for 4 days; mortality varied from 38% to 100%. Egg hatching was not significantly affected when abamectin, endosulfan and spinosad were topically applied. Number of eggs laid per female in choice and no-choice tests did not differ significantly from the control. The insecticides did not show considerable repellent effect in the choice tests. Topical, residue and systemic uptake methods were also compared to determine the differences in the toxicity levels of imidacloprid, a systemic insecticide. However, 100% mortality occurred with all methods.     

Contact activity of diflubenzuron against Spodoptera littoralis larvae

The effect of diflubenzuron as a residue on glass or applied topically to Spodoptera littoralis larvae was investigated. Diflubenzuron was active as a residue on glass against 100 and 200 mg larvae; the toxicity of residues was identical whether a dispersable formulation or a wettable powder or the technical substance were used. By topical application, diflubenzuron had an ED₅₀ for cumulative percentage mortality up to the adult stage of 004 and 0066 μg/larva for 100 and 200mg larvae respectively. Neither the site of the topical application nor whether the larvae were kept singly or in groups of ten after the treatment had an influence on toxicity. The data indicate that diflubenzuron has contact toxicity to at least one insect species as well as the known stomach poison action.