Effect of Benzoylphenyl Ureas on Survival and Reproduction of the Lace Bug, Leptopharsa gibbicarina

The lace bug, Leptopharsa gibbicarina is a vector of Pestalotiopsis fungal complex in oil palm crops in the Americas. The effects of four benzoylphenyl ureas (BPUs) (lufenuron, novaluron, teflubenzuron, and triflumuron) were evaluated against L. gibbicarina for toxicity, survival, reproduction, and mortality in semi-field conditions. Concentration-mortality bioassays demonstrated that novaluron (LC50 = 0.33 ppm), teflubenzuron (LC50 = 0.24 ppm), lufenuron (LC50 = 0.17 ppm), and triflumuron (LC50 = 0.42 ppm) are toxic to L. gibbicarina nymphs. The survival rate was 99% in control nymphs, decreasing to 50% in nymphs exposed to LC50 of triflumuron, 47% in nymphs treated with lufenuron, 43% in nymphs treated with teflubenzuron, and 43% in those treated with novaluron. Sublethal concentrations of BPUs showed detrimental effects on the adult emergence, longevity, fecundity, and fertility of this insect. The mortality of nymphs caused by these insecticides was similar in both laboratory and semi-field conditions. Our results suggest that novaluron, teflubenzuron, and triflumuron are highly effective against L. gibbicarina, and therefore, have potential applications for this oil palm pest.

Benzoylphenyl ureas as veterinary antiparasitics. An overview and outlook with emphasis on efficacy, usage and resistance

Six benzoylphenyl ureas are currently used in formulations approved as veterinary medicines: diflubenzuron for fly control mainly on cattle, lice and blowfly strike control on sheep, and lice control on farmed salmonids; lufenuron for flea control on dogs and cats and for lice control on farmed salmonids; triflumuron for lice and blowfly strike control on sheep; fluazuron for tick control on cattle; teflubenzuron for lice control on farmed salmon; and novaluron for fly and tick control on cattle and for flea control on dogs. Resistance to diflubenzuron and triflumuron has already been reported for sheep body lice and blowflies, and to fluazuron in cattle ticks. These and other minor veterinary usages, as well as the current status of resistance, are reviewed and perspectives for future opportunities are discussed based on unexplored potentials and threats posed by future resistance development.

Control of insect pests on fruit and field crops with hexaflumuron in North Greece

Experiments with hexaflumuron have been made against pests on apples, pears, peaches, potatoes and maize. On apples a predefined spray program was used for the combined control of Cydia pomonella (L) (Lepidoptera: Tortricidae), Phyllonorycter blancardella. (Fabr.) (Lepidoptera: Gracillariidae), P. corylifoliella (Hbn) (Lepidoptera: Gracillariidae), Leucoptera scitella (Zell.) (Lepidoptera: Lyonetiidae) and Adoxophyes orana (F.v. Roslerstamm) (Lepidoptera: Tortricidae). Sprays started when C. pomonella adults appeared and were continued every 2, 3 and 4 weeks. Against Cacopsylla pyri L. (Homoptera: Psyllidae), Anarsia lineatella Zell. (Lepidoptera: Gelechiidae) and Grapholitha molesta (Busck) (Lepidoptera: Tortricidae), trials were made to define efficacy and timing, while trials on Leptinotarsa decendineata (Say) (Coleoptera: Chrysomelidae) and Sesamia nonagrioides Lef. (Lepidoptera: Noctuidae) were only for efficacy. Hexaflumuron promised to be an excellent insecticide since it was at least as good as organophosphate standards, amitraz and the benzoylphenyl ureas (BPU) tested. With fewer sprays it gave seasonal and combined control on apple pests. It is a new BPU insecticide with low mammalian toxicity and fits IPM programs, since its toxicity to predators and parasites is low. Hexaflumuron had no effect on adults of the predator Coccinella septempunctata L. (Coleoptera: Coccinelidae) in the potato trial. Sprays must start at the beginning of the oviposition of fruit damaging pests and at the egg or early larva-nymph stage of the foliage damaging pests. The spray must fully cover fruit and foliage.

Insecticide and Food Consumption of Spanish Slug (Arion Lusitanicus Mabille 1868) / Insektycydy A Konsumpcja Pokarmu Przez Ślinika Luzytańskiego (Arion Lusitanicus Mabille 1868)

In the years 2007 and 2011, research was carried out on the impact of: pyrethroid group agents (beta-cyfluthrin, lambda-cyhalothrin, deltamethrin, esfenvalerate, alpha-cypermethrin, bifenthrin) benzoylphenyl ureas (teflubenzuron), derivatives of pyridine (pyriproxyfen), organophosphorus (diazinon) and neonicotinoid insecticides (acetamiprid) on the food consumption by Spanish slug (Arion lusitanicus Mab). The quantity of food consumed by animals treated by plant protection agents, the quantity of food treated by insecticides consumed and food preferences of A. lusitanicus individuals were analysed. The slugs were made available a selection between food with an addition of insecticide and without it. The results obtained indicate that the preparations which contained lambda-cyhalothrin and deltamethrin with which the animals were treated increase the quantity of food consumed by the Spanish slug. It was also shown that the food treated with lambdacyhalothrin and alpha cypermethrin is consumed in a larger amount than the food not treated by this preparation. Deltamethrin and lambda-cyhalothrin and pyriproxyfen probably constitute food attractants for A. lusitanicus individuals and also alpha-cypermethrin, bifenthrin, beta-cyfluthrin and esfenvalerate are additive, which reduces the attractiveness of food for slug.

The availability and use of chemotherapeutic sea lice control products

An international survey revealed that eleven compounds representing five pesticide types are currently being used on commercial salmon farms for sea lice control. These include two organophosphates (dichlorvos and azamethiphos); three pyrethrin/pyrethroid compounds (pyrethrum, cypermethrin, deltamethrin); one oxidizing agent (hydrogen peroxide); three avermectins (ivermectin, emamectin and doramectin) and two benzoylphenyl ureas (teflubenzuron and diflubenzuron). The number of compounds available in any one country is highly variable, ranging from 9 (Norway) to 6 (Chile, United Kingdom) to 4 (Ireland, Faeroes, Canada) to 2 (US)). Dichlorvos, Azamethiphos and cypermethrin were the most widely used compounds (5 countries) followed by, hydrogen peroxide, ivermectin and emamectin (4 countries each), teflubenzuron (3 countries), diflubenzuron (2 countries), and deltamethrin, pyrethrum and doramectin (1 country each). Although, like trichlorfon, dichlorvos use is being discontinued in several countries notably Norway and the Faeroes. In most instances the availability of sea lice chemotherapeutants is limited, many being used under extra-label veterinary prescription or exemption, and special investigation permits. Access to a broad range of compounds with different modes of action, as well as application methods, has only recently been acquired making assessment of chemotherapy, and therefore integrated pest management, difficult.

COMPARATIVE OPTIMAL TIMES OF APPLICATION OF BENZOYLPHENYL UREAS TO WESTERN SPRUCE BUDWORM, CHORISTONEURA OCCIDENTALIS FREEMAN (LEPIDOPTERA: TORTRICIDAE)

Four benzoylphenyl ureas (BPU’S) were tested on the four feeding larval instars of western spruce budworm, Choristoneura occidentalis Freeman, from a nondiapausing laboratory colony. BPU’s compared were chlorfluazuron, penfluron, triflumuron, and XRD-473 (N-(((3,5-dichloro-4-(1,1,2,2-tetrafluoroethoxy)phenyl-amino)carbonyl)-2, 6-difluorobenzymide). Although previous evidence suggested that BPU’S were generally most active on younger instars, last-instar western spruce budworm larvae were most susceptible to three of the four tested. Contour plots of estimated effectiveness during development of a western spruce budworm laboratory population indicated that the optimal time of application (lowest LC90) for XRD-473 would be ca. 16 days after the first group of larvae hatched, but the optimal time for the other three BPU’s would be between 40 and 50 days after hatch began. However, chronological age of insects in natural populations is difficult to estimate because of the influence of factors such as climatic conditions (e.g. temperature) and other ecological factors. The need to estimate optimal timing for application of BPU’s and other chemicals in terms of physiological time during population development is discussed.