Metabolites were isolated from the urine and feces of male and female rats given [(14)C-phenyl] difenoconazole or [(14)C-triazole]difenoconazole as single oral dose at 0.5 or 300 mg/kg bw, or 0.5 mg/kg bw after pre-treatment with 14 daily oral doses of unlabelled difenoconazole at 0.5 mg/kg bw. Balance data for the phenyl and triazole ring labels ... showed that > 97% of the radiolabel in all cases was excreted with > 78% in all cases eliminated in the feces. Three main metabolites, A, B and C, were isolated from feces and together accounted for an average of 68% of the administered dose. Metabolite B (hydroxy-CGA 169374) was hydroxylated in the outer phenyl ring and spectral analysis showed that that it comprised two isomers, one with a rearrangement of the chlorine on the outer phenyl ring, attributed to a mechanism analogous to an NIH shift. Metabolite C (CGA 205375) was the hydroxyl product of cleavage of the dioxolane ring from the difenoconazole molecule and was present only in the feces of rats given the higher dose. Metabolite A (hydroxy-CGA 205375) was the outer phenyl-ring hydroxylated product of metabolite C and comprised two diastereoisomers, as described for metabolite B. The profile of urinary metabolites was more complex and showed more variability between the two radiolabelled forms. Free 1,2,4-triazole was identified in male urine, accounting for less than 10% of the administered dose and represented cleavage of the alkyl bridge between the ring systems. Other urinary metabolites included metabolite C, its sulfate conjugate, ring-hydroxylated metabolite C and its sulfate conjugate, as well as an hydroxyacetic acid metabolite of the chlorophenoxy-chlorophenyl moiety, all of which were present in minor quantities, each representing less than 3% of the administered dose. One metabolite CGA 189138 (chlorophenoxy-chlorobenzoic acid) was also isolated from the liver. The difenoconazole molecule was therefore extensively metabolized, although with limited cleavage of the triazole and dioxolane rings. The extensive biliary elimination observed was consistent with the major metabolites being of relatively high molecular mass.
The major steps of the metabolism of difenoconazole in the rat were deduced to involve hydrolysis of the ketal in difenoconazole, resulting in CGA 205375 (1-[2-chloro-4-(4-chloro-phenoxy)-phenyl]-2- (1,2,4-triazol)-1-yl-ethanol), with the ketone CGA 205374 (1-(2-chloro-4-(4-chloro-phenoxy)-phenyl)- 2-(1,2,4-triazol)-1-yl-ethanone) as a postulated but not identified intermediate, and hydroxylation on the outer phenyl ring of the parent (hydroxy-CGA 169374) and in CGA 205375 (hydroxy-CGA 205375). As a minor process, cleavage of the alkyl chain between the triazole and the inner phenyl ring occurs, resulting in a hydroxyacetic acid (NOA 448731) or CGA 189138 (2-chloro-4-(4-chlorophenoxy)-benzoic acid) and free triazole. Sulfate conjugates were identified for CGA 205375 and for hydroxy-CGA 205375.
Dissipation of fungicide difenoconazole (3-chloro-4-[(2RS,4RS;2RS,4SR)-4-methyl-2-(1H-1,2,4-triazol-1-ylmethyl)-1,3-dioxolan-2-yl]phenyl 4-chlorophenyl ether) was studied following its application on apples intended for production of baby food. The apples (varieties: Jonagold Decosta, Gala and Idared) were sprayed with the formulation to control pathogens causing fungal diseases: powdery mildew (Podosphaera leucotricha ELL et Ev./Salm.) and apple scab (Venturia inaequalis Cooke/Aderh.). A validated gas chromatography-based method with simultaneous electron capture and nitrogen phosphorus detection (GC-ECD/NPD) was used for the residue analysis. The analytical performance of the method was highly satisfactory, with expanded uncertainties 19% (a coverage factor, k = 2, and a confidence level of 95%). The dissipation of difenoconazole was studied in pseudo-first-order kinetic models (for which the coefficients of determination, R2, ranged between 0.880 and 0.977). The half-life of difenoconazole was 12-21 days in experiments conducted on three apple varieties. In these experiments, the initial residue levels declined gradually and reached the level of 0.01 mg/kg in 50-79 days. For the residue levels to remain below 0.01 mg/kg (the maximum acceptable concentration for baby foods), difenoconazole must be applied approximately 3 months before harvest, at a dose of 0.2 L/ha (50 g of an active ingredient per ha).
IDENTIFICATION AND USE: Difenoconazole is a white crystalline solid. It is used as fungicide, insecticide, seed treatment/protectant. HUMAN EXPOSURE AND TOXICITY: Harmful if inhaled or absorbed through skin. Causes moderate eye irritation. It did not cause chromosomal aberrations in human lymphocytes. One case of allergic reaction to a formulated product was reported. ANIMAL STUDIES: Difenoconazole was moderately and transiently irritating to the eyes of rabbits. It was very slightly and transiently irritating to the skin of rabbits. Difenoconazole was considered to be essentially non-toxic when applied topically under occlusion to intact rabbit skin. In rats treated dermally for 28 days there was an increased incidence of minimal centrilobular hepatocellular hypertrophy in males and females at 1000 mg/kg bw. In the thyroid, the incidence of minimal to moderate severity grades of hypertrophy of the follicular epithelium was slightly increased in the group of rats at 1000 mg/kg bw. The liver appeared to be the target organ for toxicity. There was no evidence for carcinogenicity or oncogenicity in rats. There were no indications of embryotoxicity, fetotoxicity or teratogenicity at a dose up to 75 mg/kg bw per day in rabbits. There were no indications of embryotoxicity or teratogenicity at any dose up to 200 mg/kg bw in rats. Microscopic examination of the central and peripheral nervous system of rats showed no effects of treatment with difenoconazole at dietary concentrations of up to 1500 ppm in males or females. Difenoconazole did not induce gene mutations in either bacterial cells or cultured mammalian cells. ECOTOXICITY STUDIES: In zebrafish experiments, a large suite of symptoms was induced in embryonic development by different dosages of difenoconazole, including hatching inhibition, abnormal spontaneous movement, slow heart rate, growth regression and morphological deformities. Exposure to difenoconazole could alter thyroid hormone levels and gene transcription in zebrafish larvae, indicating endocrine disruption. Genes related to hatching, retinoic acid metabolism and lipid homeostasis were up-regulated by difenoconazole in zebrafish embryos. Difenoconazole exposure could also change lipid metabolism and profiles in marine medaka (Oryzias melastigma). Difenoconazole inhibited the respiration of mitochondria of the flight muscles of bumblebee.
来源:Hazardous Substances Data Bank (HSDB)
毒理性
致癌物分类
对人类无致癌性(未列入国际癌症研究机构IARC清单)。
No indication of carcinogenicity to humans (not listed by IARC).
/SRP:/ Immediate first aid: Ensure that adequate decontamination has been carried out. If patient is not breathing, start artificial respiration, preferably with a demand valve resuscitator, bag-valve-mask device, or pocket mask, as trained. Perform CPR if necessary. Immediately flush contaminated eyes with gently flowing water. Do not induce vomiting. If vomiting occurs, lean patient forward or place on the left side (head-down position, if possible) to maintain an open airway and prevent aspiration. Keep patient quiet and maintain normal body temperature. Obtain medical attention. /Poisons A and B/
/SRP:/ Basic treatment: Establish a patent airway (oropharyngeal or nasopharyngeal airway, if needed). Suction if necessary. Watch for signs of respiratory insufficiency and assist ventilations if needed. Administer oxygen by nonrebreather mask at 10 to 15 L/min. Monitor for pulmonary edema and treat if necessary ... . Monitor for shock and treat if necessary ... . Anticipate seizures and treat if necessary ... . For eye contamination, flush eyes immediately with water. Irrigate each eye continuously with 0.9% saline (NS) during transport ... . Do not use emetics. For ingestion, rinse mouth and administer 5 mL/kg up to 200 mL of water for dilution if the patient can swallow, has a strong gag reflex, and does not drool ... . Cover skin burns with dry sterile dressings after decontamination ... . /Poisons A and B/
来源:Hazardous Substances Data Bank (HSDB)
毒理性
解毒与急救
/SRP:/ 高级治疗:对于昏迷、严重肺水肿或严重呼吸困难的病人,考虑进行口咽或鼻咽气管插管以控制气道。使用气囊面罩装置的正压通气技术可能有益。考虑使用药物治疗肺水肿……。对于严重的支气管痉挛,考虑给予β激动剂,如沙丁胺醇……。监测心率和必要时治疗心律失常……。开始静脉输注D5W TKO /SRP: "保持开放",最低流量/。如果出现低血容量的迹象,使用0.9%生理盐水(NS)或乳酸钠林格氏液(LR)。对于伴有低血容量迹象的低血压,谨慎给予液体。注意液体过载的迹象……。用地西泮或劳拉西泮治疗癫痫……。使用丙美卡因氢氯化物协助眼部冲洗……。/毒物A和B/
/SRP:/ Advanced treatment: Consider orotracheal or nasotracheal intubation for airway control in the patient who is unconscious, has severe pulmonary edema, or is in severe respiratory distress. Positive-pressure ventilation techniques with a bag valve mask device may be beneficial. Consider drug therapy for pulmonary edema ... . Consider administering a beta agonist such as albuterol for severe bronchospasm ... . Monitor cardiac rhythm and treat arrhythmias as necessary ... . Start IV administration of D5W TKO /SRP: "To keep open", minimal flow rate/. Use 0.9% saline (NS) or lactated Ringer's (LR) if signs of hypovolemia are present. For hypotension with signs of hypovolemia, administer fluid cautiously. Watch for signs of fluid overload ... . Treat seizures with diazepam or lorazepam ... . Use proparacaine hydrochloride to assist eye irrigation ... . /Poisons A and B/
A single oral dose of [(14)C-phenyl]difenoconazole at 0.5 mg/kg bw was rapidly and almost completely absorbed by male and female rats. A single oral dose of [(14)C-phenyl]difenoconazole at 300 mg/kg bw was less extensively absorbed since bile-duct cannulated male and female rats excreted 17% and 22%, respectively, of the dose in feces. Maximum blood concentrations were reached within 2 hr, followed by a rapid decline for the lower dose and after approximately 4 hr, with an initial slow decline up to 24 hr, for the higher dose, after which the rate of decline was similar to the lower dose. In females the difference in area under the blood concentration-time curve (AUC) measurements between the lower and higher doses matched the dose differential, while in males the AUC differential was 400-fold. The systemic dose was eliminated predominantly via bile where it accounted for 73% of the administered dose (0.5 mg/kg bw) in males and 76% in females. Urinary excretion by bile-duct cannulated rats accounted for 14% of the administered dose in males and 9% in females, with fecal excretion representing less than 4% of the dose and thereby confirming the almost complete absorption at the lower dose. When bile from male rats at 0.5 mg/kg bw was administered intraduodenally to other bile duct cannulated rats, 80% of the dose was re-eliminated via the bile and just 4% in the urine, thereby demonstrating enterohepatic recirculation. Bile was also the major route of elimination at 300 mg/kg bw, accounting for 56% of the administered dose in males and 39% in females, while urinary excretion represented only 1% of the dose. In non-cannulated male and female rats given a single oral dose of [(14)C-phenyl] difenoconazole or [(14)C-triazole]difenoconazole at 0.5 mg/kg bw, 13-22% of the administered dose was excreted in the urine and 81-87% in the feces. In non-cannulated male and female rats given a single oral dose of [(14)C-phenyl]difenoconazole or [(14)C-triazole]difenoconazole at 300 mg/kg bw, 8-15% of the administered dose was excreted in the urine and 85-95% in the feces. There was no pronounced difference in excretion profiles, either between the sexes or between the two radiolabelled forms at either dose. When a similar dose of [(14)C-phenyl]difenoconazole or [(14)C-triazole]difenoconazole was given to rats pre-treated with 14 daily oral doses of unlabelled difenoconazole at 0.5 mg/kg bw, there was neither a sex difference nor any marked difference in excretion profiles from the rats with no pre-treatment. The excretion data for rats at 0.5 mg/kg bw showed that while enterohepatic recirculation was evident, biliary metabolites were largely excreted in the feces. At the lower dose, the half-life of excretion was approximately 20 hr. At 300 mg/kg bw, more of the administered dose was excreted in the urine by noncannulated rats than by bile-duct cannulated rats, apparently after reabsorption and further metabolism of some biliary metabolites; however, the predominant route of excretion of biliary radioactivity was again in feces, as observed at the lower dose. At the higher dose, the half-life of excretion was approximately 33-48 hr. At both doses, elimination kinetics were thus independent of sex and radiolabel position.
The concentration of radiolabel in the blood reached a maximum concentration (Cmax) at 2 hr after oral administration in male rats at 0.5 mg/kg bw and declined rapidly thereafter. The AUC up to 168 hr after administration was 6.19 ug equivalent/hr per mL. Tmax was shorter in females than in males and Cmax and AUC in females reached only about 50% of the respective values in males. The disappearance of radioactivity in female rats was slightly faster than in male rats. Tissue depletion results showed that at 2 hr and 24 hr after a dose of [(14)C-phenyl]difenoconazole at 0.5 mg/kg bw, only in the liver and kidney were concentrations consistently higher than those in plasma for both sexes. Consistent results were observed in whole-body autoradiography sections of similarly-dosed male rats, since at 2 hr and 24 hr after dosing most of the radioactivity was present in the gastrointestinal tract contents and in bile, with lower concentrations in the liver and kidneys. Other tissues with concentrations initially higher than in plasma were adrenal glands in both sexes and Harderian glands and adipose tissue in females; however, these concentrations declined rapidly. After 168 hr, [(14)C-phenyl]difenoconazole residues in tissue were very low, with only fat showing concentrations comparable to those present in plasma, while all tissue residues of [(14)C-triazole]difenoconazole were either below the limit of detection or below the limit of quantification. For both radiolabelled forms of difenoconazole, residues in female tissues also tended to be slightly lower than those in males and pre-treatment with unlabelled test substance had no effect on tissue distribution.
Tissue depletion results showed that at 4 hr after a dose of [(14)C-phenyl]difenoconazole at 300 mg/kg bw, most tissue concentrations were similar to or higher than those in plasma in both sexes. The highest tissue concentrations were present in fat in both sexes, with progressively lower concentrations in the liver, Harderian glands, adrenal glands, kidney and pancreas. In all other tissues that initially showed concentrations higher than those in plasma concentrations declined rapidly by 48 hr after dosing and by 168 hr all tissue residues of [(14)C-phenyl] difenoconazole had declined markedly, only fat showing residues that were higher than in plasma. Tissue residues of [(14)C-triazole]difenoconazole were significantly lower than those of [(14)C-phenyl]difenoconazole residues and by 168 hr were measurable only in the liver. Measurements in the contents of the gastrointestinal tract were consistent with the observed absorption and elimination profiles.
After 14 days of [4-chloro-phenoxy-U-(14)C]difenoconazole at a dose of at 0.5 mg/kg bw per day, the absorbed radiolabel was rapidly and almost completely excreted, predominantly via the feces. More than 90% of the total administered radiolabel was excreted within 24 hr after the last dose and 98.5% of the total radiolabel was recovered within 7 days. At that time, less than 0.5% of the administered dose remained in the tissues and carcass. Metabolite profiles in the urine and feces were qualitatively similar at each time-point, although small quantitative differences were observed after the administration of single and multiple oral doses. Concentrations of radioactive residues reached a plateau in most tissues after 7 days. Residue concentrations increased with continued dosing in liver, kidneys, fat and pancreas and did not reach a plateau during the dosing period; however, it was estimated that residue concentrations would reach a plateau within 3 weeks. The depletion of radioactive residues from tissues was moderately fast. Assuming first-order kinetics and monophasic depletion kinetics for the depuration of radiolabel from tissues, the half-lives ranged typically from 4-6 days. Depletion was more rapid in the liver, kidneys and pancreas, with half-lives of 1-3 days, and slower in fat, with a half-life of 9 days. Experiments with position-specific radiolabelled compounds demonstrated that the highest tissue concentrations were found in the liver for the triazole label, and in fat and plasma for the phenyl label. Residues from the triazole-labelled compound were significantly less than those from the phenyl-labelled compound. Tissue residues in females were slightly less than in males. Multiple pre-treatment with unlabelled difenoconazole had no effect on tissue distribution.
Studies of dermal penetration in rats given difenoconazole as an application to the skin in vivo and studies with rat and human skin in vitro were conducted using non-radiolabelled difenoconazole (purity, 99.3%) and [triazole-U-(14)C]difenoconazole. The absorption, distribution and excretion of radioactivity was studied in male HanBrlWIST (SPF) rats after a single dermal administration of (14)C-labelled difenoconazole mixed with the nonlabelled difenoconazole formulated as SCORE 250 EC. At the highest dose, the specific activity was 54 kBq/mg (1.5 uCi/mg). For the highest dose, difenoconazole was dissolved in blank formulation at a concentration of 250 g/L, representing the undiluted product. For the intermediate and lowest dose, this formulated material was mixed with water in a ratio of 1:200 (w/v) and 1:5000 (w/v), respectively. The applied nominal doses were 0.5, 13 and 2600 ug/sq cm and these were left in place for 6 hr. The determination of dermal absorption at the highest dose was repeated in a separate experiment, using an application of 2400 ug/sq cm. ... At the lowest, intermediate and highest doses, respectively, systemic absorption within 6 hr was 15.3%, 7.5% and 7.1% and the penetration rates was 0.013, 0.162 and 30.4 ug/sq cm per hr. The ratios of these penetration rates, i.e. 1:12:2400 were proportional to the application concentrations, i.e. 1:26:5100. There was, however, a substantial variation in the data that was attributed to the irritancy of the formulation vehicle, SCORE 250 EC; this resulted in a broad range of individual values for dermal absorption of up to 45% of the administered dose. For the study in rats in vivo, in a worst-case scenario the mean dermal absorption values at the lowest intermediate and highest doses, respectively, were 37.6%, 14.6% and 10.6%. Nevertheless, concentrations of residues in the blood were generally very low: the highest concentrations (as difenoconazole equivalents) were 0.01 ug/mL and 0.26 ug/mL at the intermediate and highest doses, respectively, 6-8 hr after appliciation. The penetration of non-radiolabelled difenoconazole (purity, 99.3%) and [triazole-U-14C] difenoconazole through isolated rat and human epidermal membrane preparations in vitro after stripping the stratum corneum from skin was determined after an exposure of 24 hr to difenoconazole at a concentration of 0.05, 1.28 or 250 mg/mL, achieving applications of 0.5, 12 or 2345 ug/sq cm. ... Within 24 hr, the proportions of radiolabel penetrating the membranes at the lowest, intermediate and highest concentrations, respectively, were 71%, 64% and 23% for the preparations of rat skin and 7.6%, 7.0% and 0.7% for the preparations of human skin. Although the studies with human skin in vitro indicated that dermal absorption was approximately 8% (7.6%) for the lowest concentration, if the amount retained in skin is considered as potentially absorbable it increases to 15%. However, the main objective of the comparative studies of rat and human skin in vitro was to evaluate the differences in the percentage actually absorbed, permitting the estimation of an appropriate species ratio. The flux (i.e. rate of penetration under steady-state conditions) at the lowest, intermediate and highest concentrations, respectively, was 0.020, 0.455 and 26.0 ug/sq cm/hr for the rat skin and 0.002, 0.037 and 0.82 ug/sq cm/hr for the human skin. The flux ratios rat:human were therefore about 1:10, 1:12 and 1:32 at the lowest, intermediate and highest concentrations, respectively. Comparison of the penetration rates at the different doses (concentration ratio, 1:25:5000), revealed an increase in the penetration rates of 1:23:1300 for rat epidermal membranes, while the penetration rates for human epidermal membranes revealed a ratio of only 1:24:500.
[EN] ACC INHIBITORS AND USES THEREOF<br/>[FR] INHIBITEURS DE L'ACC ET UTILISATIONS ASSOCIÉES
申请人:GILEAD APOLLO LLC
公开号:WO2017075056A1
公开(公告)日:2017-05-04
The present invention provides compounds I and II useful as inhibitors of Acetyl CoA Carboxylase (ACC), compositions thereof, and methods of using the same.
[EN] BICYCLYL-SUBSTITUTED ISOTHIAZOLINE COMPOUNDS<br/>[FR] COMPOSÉS ISOTHIAZOLINE SUBSTITUÉS PAR UN BICYCLYLE
申请人:BASF SE
公开号:WO2014206910A1
公开(公告)日:2014-12-31
The present invention relates to bicyclyl-substituted isothiazoline compounds of formula (I) wherein the variables are as defined in the claims and description. The compounds are useful for combating or controlling invertebrate pests, in particular arthropod pests and nematodes. The invention also relates to a method for controlling invertebrate pests by using these compounds and to plant propagation material and to an agricultural and a veterinary composition comprising said compounds.
The present invention relates to azoline compounds of formula (I) wherein A, B1, B2, B3, G1, G2, X1, R1, R3a, R3b, Rg1 and Rg2 are as defined in the claims and the description. The compounds are useful for combating or controlling invertebrate pests, in particular arthropod pests and nematodes. The invention also relates to a method for controlling invertebrate pests by using these compounds and to plant propagation material and to an agricultural and a veterinary composition comprising said compounds.
[EN] SUBSTITUTED QUINAZOLINES AS FUNGICIDES<br/>[FR] QUINAZOLINES SUBSTITUÉES, UTILISÉES EN TANT QUE FONGICIDES
申请人:SYNGENTA PARTICIPATIONS AG
公开号:WO2010136475A1
公开(公告)日:2010-12-02
The present invention relates to a compound of formula (I) wherein wherein the substituents have the definitions as defined in claim 1or a salt or a N-oxide thereof, their use and methods for the control and/or prevention of microbial infection, particularly fungal infection, in plants and to processes for the preparation of these compounds.