Academic literature on the topic 'Phosalone'

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Journal articles on the topic "Phosalone"

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Walia, S., P. Dureja, and S. K. Mukerjee. "Photochemical transformation of phosalone." Pesticide Science 25, no. 1 (1989): 1–9. http://dx.doi.org/10.1002/ps.2780250102.

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Bruneau, C., N. Soyer, and A. Brault. "Mild pyrolysis of phosalone." Journal of Analytical and Applied Pyrolysis 10, no. 2 (November 1986): 107–16. http://dx.doi.org/10.1016/0165-2370(86)85010-0.

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Espinosa-Mansilla, Anunciación, Agustina Guiberteau Cabanillas, Francisco Salinas, Nielena Mora, and Angel Zamoro. "Rapid Kinetic Spectrophotometric Determination of Phosalone (Zolone) in a Commercial Formulation." Journal of AOAC INTERNATIONAL 83, no. 1 (January 1, 2000): 1–7. http://dx.doi.org/10.1093/jaoac/83.1.1.

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Abstract A kinetic study of the degradation of phosalone in an alkaline medium was undertaken by using a pneumatic stopped-flow system. A rapid semiautomatic method is proposed for determining phosalone. Linear calibration graphs up to 8.0 × 10−5M (detection limit = 1.40 × 10−6M) were obtained, with a measurement period of only 3.5 s per sample and a relative standard deviation of 1.4%. Several pesticides were assayed as interference species, and several did not interfere even at a 6:1, M:M foreign species/phosalone ratio. A strong interference (ratio < 1) was generated by azinphos-methyl and carbaryl. The proposed method was applied to the analysis of a commercial formulation, and the results were validated by comparison with those for a chromatographic method.
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Wetzstein, Hazel Y. "Stigmatic Surface Degeneration and Inhibition of Pollen Germination with Selected Pesticidal Sprays during Receptivity in Pecan." Journal of the American Society for Horticultural Science 115, no. 4 (July 1990): 656–61. http://dx.doi.org/10.21273/jashs.115.4.656.

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Commercial pesticide formulations of triphenyltin hydroxide, benomyl plus triphenyltin hydroxide, and phosalone completely inhibited pollen germination of pecan [Carya illinoensis Wangenh C. Koch] when incorporated in in vitro germination media at one-fourth to one times the recommended rates. Scanning electron microscopic evaluations of spray effects on receptive stigmatic surfaces showed varying degrees of injury, ranging from minor surface wrinkling with triphenyltin hydroxide to severe collapse and degeneration of stigma papillae with phosalone treatments. Controlled pollinations 1 hour after pesticide sprays resulted in an inhibition of pollen germination and tube growth. Water sprays followed by pollination resulted in normal pollen adherence, hydration, and germination. Chemical names used: methyl[1-[(butylamino)carbonyl]-1H-benzimidazol-2-yl]carbamate (benomyl); S-[(6-chloro-2-oxo-3-(2H)-benzoxazolyl)methyl] 0,0-diethyl phosphorodithioate (phosalone).
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Robertson, Jacqueline L., and Haiganoush K. Preisler. "LABORATORY EVALUATION OF PHOSALONE FOR CONTROL OF WESTERN SPRUCE BUDWORM (LEPIDOPTERA: TORTRICIDAE)." Journal of Entomological Science 23, no. 4 (October 1, 1988): 374–78. http://dx.doi.org/10.18474/0749-8004-23.4.374.

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Phosalone was tested to estimate the optimal time and minimum application rate for 90% population mortality of western spruce budworm, Choristoneura occidentalis Freeman, larvae. The optimal time of application was estimated to be during the first 10 days after the first group of second instars emerged from diapause, especially between days 7 and 8. Aerial application rates necessary to bracket 90% mortality were estimated as 320, 640, and 960 g/ha. Because these rates are well below the application rates used for agricultural pests, phosalone is a candidate for field trials on western spruce budworm.
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Masoumi, Arameh, Khadijeh Hemmati, and Mousa Ghaemy. "Recognition and selective adsorption of pesticides by superparamagnetic molecularly imprinted polymer nanospheres." RSC Advances 6, no. 55 (2016): 49401–10. http://dx.doi.org/10.1039/c6ra05873f.

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Ahmad, R., R. S. Kookana, A. M. Alston, and R. H. Bromilow. "Differences in sorption behaviour of carbaryl and phosalone in soils from Australia, Pakistan, and the United Kingdom." Soil Research 39, no. 4 (2001): 893. http://dx.doi.org/10.1071/sr00021.

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Sorption of 2 nonionic pesticides, carbaryl (1-naphthyl methylcarbamate) and phosalone (S-6-chloro-2,3-dihydro-2-oxobenzoxazol-3-ylmethyl O,O-diethyl phosphorodithioate), was investigated for 48 soils from Australia, Pakistan, and the United Kingdom. A wide variation in sorption affinities of the soils to carbaryl and phosalone was observed. The sorption coefficient (K d) values for carbaryl ranged from 0.19 to 23.0 L/kg in Australian soils, from 0.99 to 59.7 L/kg in Pakistani soils, and from 1.09 to 23.0 L/kg in the UK soils. The K d values for phosalone ranged from 4.8 to 443 L/kg in Australian soils, from 15.5 to 1182 L/kg in Pakistani soils, and from 18.1 to 205 L/kg in the UK soils. To eliminate the effect of variation in organic carbon content among the soils, the K d values were normalised to the fraction of soil organic carbon (K oc ). However, K oc values for both pesticides varied by about an order of magnitude across the soils, decreasing in the following order: Pakistani > Australian > UK soils. Correlation between K d and organic carbon content of the soils was poor (r 2 = 0.44 and 0.46). The particulate organic C (53 µm–2 mm) was only slightly better correlated with K d than the total organic C in the <2 mm fraction of the soils. Thus soil organic C content alone is not a good predictor of sorption even for nonionic pesticides such as carbaryl and phosalone. Caution is needed during extrapolation of overseas data to predict sorption under local conditions.
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Xu, Liping, Jiebin Li, Jiajia Zhang, Junyong Sun, Tian Gan, and Yanming Liu. "A disposable molecularly imprinted electrochemical sensor for the ultra-trace detection of the organophosphorus insecticide phosalone employing monodisperse Pt-doped UiO-66 for signal amplification." Analyst 145, no. 9 (2020): 3245–56. http://dx.doi.org/10.1039/d0an00278j.

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Ramalingam, K., and R. Kasinathadurai. "Blood Carbohydrates and Phosalone Poisoning inRana Tigrina(Daudin)." Archives Internationales de Physiologie et de Biochimie 97, no. 5 (January 1989): 369–74. http://dx.doi.org/10.3109/13813458909104549.

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Campi, Valentina, Daniele Ferrario, Maria Carfi’, Cristina Croera, and Laura Gribaldo. "Estrogen-like activity of phosalone on MCF7 cell line." Toxicology Letters 164 (September 2006): S166. http://dx.doi.org/10.1016/j.toxlet.2006.07.004.

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Dissertations / Theses on the topic "Phosalone"

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Fischer, Luc. "Étude comparée de l'incidence de trois insecticides : deltamethrine, dimethoate, phosalone sur la faune des arthropodes épiges des Agrosystèmes céréaliers : cas d'un traitement à la floraison en culture de blé d'hiver." Paris 11, 1987. http://www.theses.fr/1987PA112047.

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Étude menée dans une culture de blé dans les bassins parisiens en 1983, 84 et 85. Échantillonnage réalis& à l'aide de pots-pièges, pièges jaunes, d-vac, prélèvements d'épis, bâches et gouttières. Insecticides actifs sur le puceron des épis (sirobion avenae), les diptères phytophages, les homoptères, les thysanoptères, les diptères prédateurs et les araignées. Pas d'action des insecticides sur les d’étripages (sciaridae, chironomidae), les coléoptères prédateurs (carabidae, staphylinidae) et certains microhyteroptères. Pas d'effet des traitements d'une année sur l'autre
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Fischer, Luc. "Etude comparée de l'incidence de trois insecticides, delthaméthrine, diméthoate, phosalone sur la faune des arthropodes épiges des agrosystèmes céréaliers." Grenoble 2 : ANRT, 1987. http://catalogue.bnf.fr/ark:/12148/cb37605090c.

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Mergnat, Thierry. "Devenir de contaminants majeurs d'aliments végétaux (nitrates, nitrites, phosalone, mancozebe et éthylène thiourée) en relation avec un process de déshydratation." Bordeaux 1, 1995. http://www.theses.fr/1995BOR10570.

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Les fruits et legumes deshydrates, susceptibles d'etre abondamment utilises en alimentation infantile, doivent etre d'une excellente qualite bacteriologique avec des teneurs en contaminants generalement inferieure a 0,1 mg/kg. Les nitrates, les nitrites, la phosalone, le mancozebe et un de ses metabolites, l'ethylene thiouree sont parmi les principaux contaminants des fruits et legumes frais ou transformes. Lors du process de deshydratation, selon la technique du secheur hatmacker, le lavage et les deux chocs thermiques successifs, modifient les taux de nitrates et de nitrites de plusieurs legumes et des produits phytosanitaires precites. Parmi l'ensemble des procedes technologiques utilises, seul l'effet de la temperature en milieu humide permet de reduire de 30 a 55% les teneurs en nitrates des legumes etudies. Les taux de nitrites dans les legumes frais etudies sont a plus de 96% inferieur a 1 mg no#2/kg et les procedes technologiques employes n'augmentent pas ces valeurs. Pour les produits phytosanitaires selectionnes, la totalite des procedes contribuent a une reduction des taux de phosalone des pommes superieur a 80%, quelle que soit la dose initiale comprise entre 0 et 4,29 mg/kg. Le lavage contribue a une reduction de 30 a 50%, vraisemblablement par une solubilisation partielle de la phosalone dans les eaux. Le choc thermique en milieu humide et plus particulierement la filtration des homogenats eliminent d'une maniere mecanique et sans degradation constatee 40% a 70% de la quantite de phosalone. Par contre, le sechage, effectue en fin de process, n'entraine pas de variations significatives. De plus, tous nos essais de traitement de pommes avec des doses de mancozebe comprises entre 0 et 23 mg/kg temoignent d'une reduction de 92 a 99%. Les effets de la temperature en milieu humide produisent une reduction moyenne de 66% de la dose de mancozebe dont 15% sont convertis en ethylene thiouree. De meme lors du deuxieme choc thermique correspondant a la deshydratation, on a mis en evidence un double phenomene: une reduction du taux d'etu issus du premier traitement thermique et une reduction du mancozebe comprise entre 30 et 70% accompagnee d'une formation d'etu correspondant en moyenne a 9%. Globalement, ces deux procedes technologiques generent de l'ethylene thiouree dont la quantite dans le produit fini represente de 2 a 5% de la dose initiale de mancozebe. Ce mode de fabrication contribue pour une grande part a une plus grande securite alimentaire. De plus, nous avons mis en evidence plusieurs possibilites pour accroitre la qualite de ce type de produits deshydrates. En revanche pour l'ethylene thiouree et pour les residus elimines non identifies, il convient de poursuivre nos travaux pour ameliorer les techniques de detection et pour etudier d'eventuelles consequences toxicologiques
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Book chapters on the topic "Phosalone"

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Unger, Thomas A. "Phosalone." In Pesticide Synthesis Handbook, 431. Elsevier, 1996. http://dx.doi.org/10.1016/b978-081551401-5.50340-3.

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