muramidase and cypermethrin

The aim of this study was to assess acute health effects on planters caused by planting conifer seedlings treated with two insecticides, with active ingredients imidacloprid and cypermethrin, in comparison with untreated seedlings.. The investigation was a double-blind crossover study, which included a follow-up of 19 planters over a 3-week period. During Week 1, the 19 planters handled untreated conifer seedlings while they planted imidacloprid- and cypermethrin-treated seedlings during study Week 2 and 3, respectively. Signs and symptoms of acute health effects were documented by a questionnaire, administered by the field staff, during these 3 weeks. Inflammation markers in the nasal mucous membrane were also measured as an objective test. Exposure to cypermethrin was further assessed by measuring 3-phenoxybenzoic acid (3-PBA) in urine. No validated biomarker was available to assess internal exposure to imidacloprid.. No clear, acute adverse health effects could be found in planters during the week of exposure to conifer seedlings treated with imidacloprid (Merit Forest) or cypermethrin (Forester), as compared to during the week of planting untreated seedlings. During the week of cypermethrin exposure, the individuals had 3-PBA values that were 12-54% higher (P < 0.05), depending on the worker, than those observed during the untreated week. There were no statistically significant correlations between the raised levels of 3-PBA and self-reported health problems. These results have been obtained during planting in late summer/early autumn and with good use of protective clothing.. No clear, acute adverse health effects could be found in planters after exposure to conifer seedlings treated with imidacloprid (Merit Forest) or cypermethrin (Forester), as compared with planting untreated seedlings. The metabolite, 3-PBA, was found in low levels in urine and was increased after exposure to cypermethrin. However, no clear relationships could be found between exposure and reported symptoms or between elevated 3-PBA levels and reported symptoms.

Topics: Adult; Air Pollutants, Occupational; Albuminuria; Animals; Benzoates; Biomarkers; Cross-Over Studies; Double-Blind Method; Environmental Monitoring; Female; Follow-Up Studies; Forestry; Humans; Imidazoles; Inhalation Exposure; Insecticides; Logistic Models; Male; Middle Aged; Muramidase; Neonicotinoids; Nitro Compounds; Occupational Diseases; Occupational Exposure; Protective Clothing; Pyrethrins; Skin Absorption; Tracheophyta

Many current-use pesticides (CUPs) are found at increasing concentrations in aquatic environments, yet relatively little is known about their effects on the immune system of fish. We examined the in vivo effects of three pesticides (chlorothalonil, cypermethrin and pentachlorophenol) on the immune system of juvenile rainbow trout (Oncorhynchus mykiss) by assessing a suite of innate immune function tests, as well as a host resistance test using Listonella anguillarum. Increased activity of phagocytic leukocytes, as evidenced using flow cytometry, was observed following 28-day exposures to pentachlorophenol (1 microg/L and 2 microg/L), but not for cypermethrin or chlorothalonil, although a trend of increasing activity was noted for chlorothalonil. No recovery was observed during a 14-day post-exposure chlorothalonil experiment, as evidenced by continued elevation of respiratory burst and percent phagocytic cells at the lowest exposure concentrations (100 ng/L and 200 ng/L), suggesting a prolonged CUP-induced impact on the immune system. No effects of any pesticide on body weights, direct lethality, serum lysozyme or relative leukocyte differential were observed, suggesting that modulation of the cellular responses of the innate immune system represents a sensitive sub-lethal endpoint for these three pesticides. However, a lack of detectable effects of these CUPs on host resistance to L. anguillarum in our study may reflect a dose-response range that did not elicit an effect on those immune responses responsible for control and clearance of this particular pathogen. Additional research may provide more insight into the immunomodulatory effects of these and other CUPs, and the implications for host resistance against a variety of bacterial, viral and macroparasitic pathogens.

Topics: Animals; Dose-Response Relationship, Drug; Immunity, Innate; Kidney; Leukocytes; Listonella; Muramidase; Nitriles; Oncorhynchus mykiss; Pentachlorophenol; Pesticides; Phagocytosis; Pyrethrins; Toxicity Tests, Chronic; Water Pollutants, Chemical

The dimer of lysozyme was administered to carp (Cyprinus carpio L.) in an attempt to reduce the suppression of response in fish exposed to the cypermethrin. Experimental studies were carried out on cells isolated from blood and pronephros of carp. In the in vivo studies fish were intoxicated with cypermethrin (synthetic pesticide) at a dose of LD5. After 24 h fish were injected intraperitoneally with a modulator-the dimer of lysozyme (KLP-602) at a dose of 0.02 mg/kg of body weight. In the study we determined the metabolic activity of phagocyte cells and the proliferative ability of lymphocytes stimulated by ConA and LPS. The results indicate that this modulator is useful for stimulation of cellular and humoral immunity after experimentally induced suppression by selected pesticide.

Topics: Animals; B-Lymphocytes; Carps; Cell Proliferation; Cell Separation; Immunity, Cellular; Immunologic Factors; In Vitro Techniques; Injections, Intraperitoneal; Insecticides; Kidney; Lymphocytes; Mitogens; Muramidase; Phagocytes; Pyrethrins; Respiratory Burst; T-Lymphocytes; Tetrazolium Salts; Thiazoles