HEXACONAZOLE EXPLANATION First draft prepared by Dr E.M. den Tonkelaar and Dr J.E.M. v. Koten-Vermeulen National Institute of Public Health and Environmental Protection, Bilthoven, Netherlands Hexaconazole is a broad spectrum triazole fungicide that is used against powdery mildew, scab and rust of apples and powdery mildew and blackrot of grapes. Hexaconazole is considered for the first time by the present meeting. EVALUATION FOR ACCEPTABLE DAILY INTAKE BIOLOGICAL DATA Biochemical aspects Absorption, distribution and excretion Alpk/AP rats were given single oral doses of 1 or 200 mg 14C-phenyl hexaconazole (purity 99.3%)/kg b.w. Radioactivity was determined in urine and faeces daily and whole body autoradiograms were made at termination. About 90% of the administered radioactive dose was excreted in the urine and faeces within 72 hours after dosing; exhaled radioactivity after 48 hours was negligible. After 7 days radioactivity recovered in the urine was 43% and 66.4% and in the faeces 53% and 29% of the administered dose for males and females, respectively. A total of 96% of the radioactivity was recovered after 7 days with less than 1% of the administered dose present in the tissues and carcass. Although there were no marked differences in the relative proportions of dose excreted via urine and faeces over seven days, the rate of excretion was more rapid at the 1 mg/kg bw level. Autoradiography showed highest tissue residues after 24 hours in the liver, intestinal tract and adrenal cortex. After 72 hours the radioactivity in the liver and adrenal cortex had declined. Male tissues generally showed higher residues than female tissues (Jones et al., 1984). In a similar experiment rats were given single oral doses of 200 mg 14C-phenyl ring-labelled hexaconazole (purity 92.3%)/kg b.w. Over a period of 72 hours or 7 days male rats excreted 37% and 42% in the urine and 40% and 52% in the faeces, respectively. The female rats excreted most of the dose within 72 hours (63% via the urine and 30% via the faeces). After 24 hours highest tissue residues were found in the liver, kidneys, and pancreas. After seven days 95.6% and 98.5% of the radioactivity had been recovered for males and females, respectively, and tissue levels were 0.7% of the administered dose (Trivedi et al., 1986). Tissue distribution was measured in groups of rats over a period up to 96 hours following single oral doses of 1 or 200 mg 14C-hexaconazole (phenyl ring labelled; purity 99.3%)/kg bw). At the 1 mg/kg bw dose peak tissue concentrations of radioactivity did not markedly differ between the sexes. The highest concentration was found 6 to 10 hours after dosing in the adrenal glands of male and female rats, respectively, although the liver contained the highest proportion of the dose (7.1% and 5.4%, respectively). The elimination of radioactivity for all tissues was fairly rapid with elimination half-lives of 10 to 14 hours in males and 7 to 16 hours in females. Peak tissue concentrations of radioactivity were higher in male rats than in females at the 200 mg/kg bw dose. Highest levels were found in the liver in both males (3.6%) and females (2.4%) after 6 and 3 hours, respectively. Elimination half lives ranged from 10-19 hours in males and from 10-27 hours in females. Ninety-six hours after dosing (both at 1 and 200 mg/kg bw) all tissue residues were either very low or were below the limit of detection (Jones, 1989a, 1989b). Four male and four female rats were given 14 consecutive daily oral doses of 1 mg/kg bw unlabelled hexaconazole followed by a single oral dose of 1 mg 14C-hexaconazole (phenyl-labelled). Males excreted 41% via urine and 55% via faeces over a period of 7 days, whereas females eliminated 63% via the urine and 35% via the faeces. Excretion was fairly rapid with 88.7 and 93.1% of the dose excreted within three days by males and females, respectively. Highest tissue concentrations were found in the liver of male rats (0.12% of the dose). In female rats, only 0.02% of the dose was found in the liver and all other tissue residues were lower. No differences were found in metabolic profiles in urine and methanol extracts of faeces collected from rats given either repeated doses or a single oral dose of hexaconazole (Jones, 1988a). Fourteen consecutive daily oral doses of 1 mg/kg 14C- hexaconazole (phenyl labelled) were administered to 2 male and 2 female rats. Tissue distribution was measured at 24 (1/sex) and 48 hours (1/sex) by autoradiography. In both sexes at 24 hours after dosing, highest concentrations were observed in the adrenal gland and a much lower radioactivity was measured in the liver, kidneys and lungs. Forty-eight hours after dosing radioactivity was markedly reduced or was negligible (Jones, 1988b). Biotransformation The metabolism of hexaconazole in male and female rats was established following the administration of 1, 100 or 200 mg/kg bw 14C-hexaconazole (phenyl- and/or triazole-labelled). Biliary elimination was characterized at a dose of 200 mg/kg bw 14C-phenyl-labelled hexaconazole and the fate of the triazole component of the molecule was established using 100 or 200 mg/kg bw 14C- triazole-labelled hexaconazole. Urinary, faecal and biliary metabolites were identified and quantified. In both male and female rats hexaconazole was extensively metabolized via two pathways involving oxidation of the n-butyl chain and some cleavage of the triazole substituent. The major pathway involved the conversion of hexaconazole to 5-hydroxy-hexaconazole and 5-keto-hexaconazole; the minor pathway was a two-stage oxidation of the methyl group to form hexaconazole acid via 6-hydroxyhexaconazole. The biliary route of elimination was important in both sexes (80% in males and 40% in females). In both sexes half of the radioactivity eliminated in the bile was reabsorbed and half was excreted via the faeces as the biliary conjugates or their aglycones. The sex difference in the proportions excreted in urine and faeces was due to quantitative differences in biliary elimination of hexaconazole metabolites. Metabolites in the urine were derived from initial metabolism or following reabsorption of biliary metabolites. Biliary metabolites in males were predominantly glucuronide conjugates such as 5-hydroxy hexaconazole (24% of the dose), hydroxy-keto hexaconazole (22%), 5-keto hexaconazole (8%) and hexaconazole (4%) and to a lesser extent some unidentified metabolites including 14C-phenyl labelled products after triazole cleavage. In female rats the same metabolites were detected in the same relative proportions. Male urinary metabolites included triazole (18% of a 100 mg/kg bw dose, in females 13%), hexaconazole acid (7-9%), hydroxy-keto hexaconazole (6-7%), an unidentified conjugate of 5-hydroxyconazole (5%, in females 27-34%) and hexaconazole. Less than 5% of unchanged hexaconazole was detected in the urine. Only trace amounts of triazole or related metabolites were detected in faeces. The proposed metabolic pathway is described in Figure 1 (Jones, 1989c). Toxicological studies Acute toxicity The acute toxicity of hexaconazole to rats and mice is presented in Table 1. The most common signs of toxicity (less marked after dermal administration) were piloerection, upward curvature of the spine, side pinched-in, hypothermia, decreased activity, urinary incontinence, dehydration, comatosis, reduced righting reflex and decreased respiration rate. Table 1. Acute toxicity of hexaconazole Species Sex Route LD50 LD50 Reference (mg/kg b.w.) (mg/1) Mouse M&F oral >557 Southwood, 1984a M oral 612 Leah, 1989 F oral 918 Leah, 1989 Rat M oral 2189 Southwood, 1984a F oral 6071 Southwood, 1984a M oral 4013 Davison, 1988 M&F dermal >2000 Southwood, 1984a M&F inhal >5.9* Hext, 1987 *4-hr aerosol exposureShort-term studies Mice Groups of C57BL/10JfCD-1/Alpk mice were fed diets containing 0, 25, 100, 500 or 1500 ppm hexaconazole (purity not given) in the diet for 29 days. At 500 and 1500 ppm pronounced effects were observed on body weight, food consumption, food efficiency and liver weight. A slight to moderate microcytosis with a compensatory increase in red cell numbers to maintain haemoglobin levels was observed in males at 1500 ppm and in females at 500 and 1500 ppm. Red cell counts were also increased in males at 500 and 100 ppm. At histopathology a dose-related liver hypertrophy and increased hepatocyte lipid accumulation with associated cytoplasmic vacuolation were observed. A lack of corpora lutea in the ovaries and a reduction in the size of the uterus were observed in females receiving doses of 100 ppm hexaconazole and above. At 1500 ppm and possibly at 500 ppm there was some evidence of an effect on the male reproductive system with increased abnormal precursor cells in testicular tubules and epididymis and reduced seminal vesicular secretion. Cortical enlargement of the adrenal glands was observed at 500 and 1500 ppm. The NOAEL in this study was 25 ppm hexaconazole (equivalent to 3.5 mg/kg bw/day) (Forbes, 1988). Rats Groups of Wistar (Alpk/AP) rats (20/sex/group) were fed diets containing 0, 50, 500 or 5000 ppm hexaconazole (purity 92.3%) for 90 days. Observations included clinical examinations, mortality, food consumption and food efficiency, body weight, haematology, clinical chemistry, hepatic aminopyrine-N-demethylase activity (APDM) and urinalysis, ophthalmoscopy, macroscopy, organ weight and histopathology. An increased incidence of staining of the pelt around the nose was observed in rats at 5000 ppm. Body weight gain was significantly reduced in both male and female rats at 5000 ppm (accompanied by reduced food consumption), in males at 500 ppm (first 3 weeks of the study) and in females at 500 and 50 ppm (at several timepoints over the treatment period). Final body weight was significantly reduced in high dose rats. In males at 5000 ppm Hb (also at 500 ppm), Ht and RBC counts were significantly decreased and WBC count was significantly increased. Prothrombin-time was significantly reduced in males at 5000 and 500 ppm. Inconsistent changes in blood biochemistry (ALAT, ASAT, albumin, protein, glucose and triglycerides and cholesterol) were observed at 5000 and in some parameters also at 500 ppm. Relative liver weight was significantly increased in both sexes at 5000 and 500 ppm. Relative weight of spleen, adrenal and testes were significantly decreased in males and kidney weight was increased in females at 5000 ppm. Hepatic APDM activity was significantly increased at all dose levels in both male and females. At the highest dose enlarged and discoloured pale livers were observed in 16/20 males and 6/20 females. At histopathology hepatocellular swelling and fatty change were seen in males (also at 500 ppm) and females at 5000 ppm. Cortical parenchymal vacuolation in the adrenal glands was observed in both sexes at 5000 ppm and in males also at 500 and 50 ppm. Haemorrhages in the thymus were observed in both sexes at 5000 ppm. The LOAEL in this study was 50 ppm (equivalent to 2.5 mg/kg bw/day) (Kinsey et al., 1984). Dogs Groups of beagle dogs (4/sex/group) received 0, 5, 25 or 125 mg hexaconazole (purity 92.3%)/kg bw daily by capsule for 90 days. After 7 days the high dose group was terminated because of severe toxic effects (body weight loss, vomiting, abnormalities in gait and behaviour and one death). An additional group was then started (4/sex) at 75 mg/kg bw/day. After 10 days this dose, showing similar signs of toxicity, was reduced to 50 mg/kg bw/day. After the initial effects at 75 mg/kg bw/day no dose-related effects were observed on mortality, clinical signs, ophthalmoscopy, body weight and food consumption at 50 mg/kg bw/day. Platelet count was significantly increased in both sexes at 50 mg/kg bw/day. Urea, albumin, triglycerides and cholesterol in plasma were significantly reduced and ALAT and SAP were increased in males and in females at 50 and 25 mg/kg bw Relative kidney weight and relative liver weight were significantly increased in both sexes at 50 mg/kg bw/day and there was a tendency to increased liver weight at 25 mg/kg bw. Weights of ovaries and testes were slightly decreased at the highest dose. At macroscopy enlargement and pallor of the liver was observed at both the mid- and the high-dose level. These findings were accompanied by microscopic evidence of an increase in hepatocyte lipid accumulation. The NOAEL in this study was 5 mg/kg bw/day (Stonard, 1989). Groups of beagle dogs (4/sex/group) received 0, 2, 10 or 50 mg hexaconazole (purity 90.0%)/kg bw daily by capsule for one year. Two dogs died during the study, 1 male dog at 50 mg/kg bw/day on day 5 (the dog was replaced by another male dog) and another dog (female) given 2 mg/kg bw/day in week 36. Neither death was considered to be treatment-related. There were no effects on clinical condition, ophthalmoscopy, food consumption and urinalysis. At the highest dose body weight gain was significantly reduced during the first 5 weeks of the study. At 50 mg/kg bw/day platelet count was significantly increased in both sexes throughout the study and in females at 10 mg/kg bw at weeks 13 and 26. At the high dose level reductions in plasma total protein and albumin, urea, cholesterol and triglycerides were observed in both sexes. SAP and ALAT were increased in both male and female dogs at 50 mg/kg bw/day (significantly) and at 10 mg/kg bw/day. Relative liver weight at 50 and 10 mg/kg bw/day and relative kidney weight at 50 mg/kg bw/day were significantly increased. At macroscopy pallor, enlargement and accentuation of the lobular pattern of the liver was observed in high dose dogs. Fatty changes of the liver were observed in both male and female dogs at 50 mg/kg bw and to a lesser extent in males at 10 mg/kg bw/day. The NOAEL in this study was 2 mg/kg bw/day (Stonard, 1988). Long-term/carcinogenicity studies Mice Groups of male and female C57/BL/10JfCD-1/Alpk mice (50/sex/group) were fed diets containing 0, 0', 5, 40 or 200 ppm hexaconazole (purity 90%) for 2 years. Two concurrent control groups of 50 male and 50 female mice were kept. Observations included clinical signs, body weight, food consumption, haematology, macroscopy, liver and testes weight, and histopathology. A slightly increased incidence of the loss of coat color (black to grey) was observed in male mice at 200 ppm during the second year of the study. At the highest dose, body weight gain and food efficiency were significantly reduced in males and food consumption was significantly reduced in females. At termination Hb, Ht and RBC values were significantly increased in both sexes and MCV, platelet count and WBC count in females only at the highest dose. Relative liver weight was significantly increased in high dose males and females accompanied by an increased incidence of minimal to moderate centrilobular fatty changes in the liver. Tumour incidences were not increased. The NOAEL in this study was 40 ppm (equal to 4.7 mg/kg bw/day for male mice and 5.9 mg/kg bw/day for females) (Pigott, 1988). Rats Groups of male and female ALpk:APfSD rats (64/sex/group) were fed diets containing 0, 10, 100 or 1000 ppm hexaconazole (purity 89.8%). Twelve rats/sex from each group were used for interim sacrifice after 52 weeks and the remaining 52 rats/sex/group were continued to terminal sacrifice after 105 weeks. Observations included clinical signs, body weight, food consumption, ophthalmoscopy, haematology, clinical chemistry, APDM-activity in liver, macroscopy, organ weights (gonads, adrenals, kidneys, liver and brain), and histopathology. In order to provide information on adrenocortical function, blood samples of 12 male and 12 female rats of each group were taken at week 52/53 and week 78/79 and analyzed for corticosterone. Urinary sodium and potassium levels (as an indirect method of assessing aldosterone levels) were determined in 13/rats/sex/group at week 52. No treatment-related effects were seen on mortality, haematology, corticosterone, urinary sodium and potassium levels or ophthalmoscopy. A dose-related decrease in body weight gain was seen in females at 100 ppm and in both sexes at 1000 ppm. Food consumption was lower for high dose males and females. At 1000 ppm plasma triglyceride levels were reduced in males and in females. Cholesterol levels were significantly increased in high dose female rats and urea levels decreased during the first year. Increases in ALAT and ASAT activities were observed in male rats at 1000 ppm. Urinary protein excretion was significantly increased in high dose males up to week 25 which was reflected in lower pH values. There was a marked increase in hepatic amino-pyrine-N-demethylase activity in both males and females receiving 1000 ppm; a smaller but still significant increase was observed in males at 100 ppm. Relative liver weight was significantly increased at the highest dose (at interim sacrifice females at 100 ppm also showed an increased relative liver weight). Relative adrenal and kidney weights were increased in females at 100 and 1000 ppm after 52 weeks only. Livers of high dose rats showed an accentuation of lobular pattern, with or without swollen or enlarged lobes and pale spots at the interim sacrifice as well as at termination. Microscopy revealed a dose-related increased incidence of fatty changes, primarily centrilobular in pattern in the liver of males at 1000 and 100 ppm and in females at 1000 ppm. High dose rats also showed an increase in the incidence of hepatocyte hypertrophy, with a slight dose-related increase in microcystic degeneration of the liver in males at 1000 ppm and a slight increase at 100 ppm. An increased incidence of cortical vacuolation was observed in the adrenal glands of mid and high dose males. A slight increase was seen in cortical cysts in females at 1000 ppm. In the testes of rats at 1000 and 100 ppm, a treatment-related increased incidence was seen in benign Leydig cell tumours. The incidence was 2/52, 2/52, 4/52, 8/52 at 0, 10, 100 and 1000 ppm, respectively. Historical control values for this finding are 0-14.4%. The NOAEL in this study was 10 ppm (equal to 0.47 mg/kg bw/day in males and 0.61 mg/kg bw/day in females) (Hext, 1988a; 1988b). Reproduction study Rats Groups of 15 male and 15 female ALpk:APfSD rats received hexaconazole (purity 90.0%) in the diet at 0, 20, 100 or 1000 ppm. After 12 weeks of treatment animals were mated to start a 2-generation (2 litters/generation) study. F1 parents selected from F1a offspring were mated after 11 weeks. At 1000 ppm body weight gain and food consumption were decreased in F0 and F1 parents. A trend for a decreased body weight gain was observed in F0 males at 100 ppm. At the highest dose birth weight and weight gain to day 36 of F1a litter offspring were significantly reduced. In both F2a and F2b litters total litter weight was markedly reduced and F2b pup weight was also reduced. Absolute as well as relative liver weights were increased at 1000 ppm for F0 and F1 parents and F1a, F2a and F2b pups. Histopathology revealed evidence of fatty changes in the liver with or without hepatocyte hypertrophy in male and female parents and pups at 1000 ppm. At 100 ppm there was evidence of a similar but less marked effect on the histopathology of the liver in both parents and offspring. Cortical cell vacuolation of the adrenal gland was observed in both male and female parents and offspring at 1000 ppm and to a much lesser extent this was also found at 100 ppm. No adverse effects were observed on reproduction parameters such as fertility indices, length of gestation, pre-coital interval, litter size and number of live and dead fetuses. The NOAEL in this study was 20 ppm (equivalent to 1 mg/kg bw/day) (Middleton, 1988). Special studies on embryo/fetotoxicity Rats Groups of 24 pregnant Wistar Alpk/AP rats were orally dosed by gavage at 0, 2.5, 25 or 250 mg/kg bw/day hexaconazole (purity 92.3%) in corn oil from day 7 to day 16 of gestation. Clinical signs, mortality, body weight and food consumption were recorded. At day 22 of gestation animals were sacrificed and the fetuses were delivered by cesarean section. The number and positions of implantations and corpora lutea were determined. The fetuses were counted, sexed and weighed and examined for external, visceral and skeletal malformations. At 250 mg/kg bw/day, maternal body weight gain and food consumption were significantly decreased. Post-implantation loss was significantly increased. The mean number of live fetuses was slightly reduced and pup weight was significantly lower at the highest dose. The number of fetuses with minor defects only was significantly increased at 25 and 250 mg/kg bw/day. The incidence of fetuses with extra 14th thoracic ribs was significantly increased at 25 and 250 mg/kg bw/day. At 250 mg/kg bw/day the proportion of fetuses with unossified calcanea and partially ossified 5th sternebrae was significantly increased and the mean manus and pes scores were also significantly increased in this group. In this study fetotoxic effects were observed at 250 and to a lesser extant at 25 mg/kg bw/day, but there were no indications for structural malformations being associated with compound administration. The NOAEL for fetotoxicity in this study was 2.5 mg/kg bw/day (Killick et al., 1984a). Rabbits Groups of 18 pregnant New Zealand white rabbits were orally dosed by gavage with 0, 2.5, 12.5 or 50 mg hexaconazole (purity 92.3%)/kg bw in corn oil from days 7-19 of gestation. At day 30 of gestation animals were sacrificed and the fetuses were delivered by Cesarean section. No dose-related maternal toxicity was observed. The number, growth, and survival of the fetuses were not affected by treatment. After examination of the fetuses for external, visceral and skeletal malformations, a slight increase (not significant) in partially ossified 5th sternebrae was seen at 50 mg/kg bw only. The NOAEL in this study was 12.5 mg/kg bw/day (Killick et al., 1984b). Special studies on genotoxicity A number of genotoxicity tests have been carried out with hexaconazole. The results are summarized in Table 2 (in vitro) and Table 3 (in vivo). Special studies on pharmacological effects In vivo studies In a rat behavioural study, a pull-up test for evaluating muscle relaxation and a Halothane sleeping time test, central nervous system (CNS) depression was observed at high doses (>500 mg/kg bw) hexaconazole (purity 89.8%). The NOAEL for CNS depression in these studies was 250 mg/kg bw/day. Hexaconazole had no effect on the cardiovascular system as determined by blood pressure measurements, heart rate or respiration rate and gastrointestinal motility (Allen, 1988). In vitro studies At high concentrations a non-competitive antagonism of both acetylcholine and histamine in guinea-pig ileum was observed. Complete haemolysis of rabbit erythrocytes was induced by 0.03% and 0.1% hexaconazole. No effects were observed on (alpha)1, (alpha)2 or œ-adrenoceptors, nicotinic acetylcholine receptors or on smooth muscle (Allen, 1988). Special studies on skin and eye irritation and sensitization A dose of 500 mg hexaconazole (purity not given) moistened with 0.5 ml of deionised water, was applied under occlusive conditions to the shaven intact back skin of 6 male New Zealand white albino rabbits for 4 hours. No skin irritation up to 72 hours after application occurred (Southwood, 1984b). Table 2. Results of in vitro genotoxicity assays on hexaconazole Test system Test object Concentration Purity Results Reference Ames test1 S. typhimurium 1.6-5000 µg/ plate, 92.3% negative Callander, 1984 TA98, TA100, 2 tests TA1535, TA1537, TA1538 Ames test1 E. coli WP2 uvrA 1.6-5000 µg/pla 89.8% negative Callander, 1988 pKM101 2 tests2 Cytogenetics assay human lymphocytes 15-250 µg/ml, 92.3% negative Sheldon, et al., 1984a >200 toxic3 20-250 µg/ml4 Lymphoma forward mouse L5178Y cells 7.8-125 µg/ml 92.3% negative Cross, 1986 mutation assay >70 µg:toxic5 Unscheduled DNA rat hepatocytes 10-4, 10-5, 90.0% negative Trueman, 1988 synthesis test 10-6 or 10-7 M6 1 Both with and without rat liver S9 fraction. 2 2-Aminoanthracene and N-methyl-N1-nitro-N-nitrosoguanidine were used as positive controls. 3 Without metabolic activation, mitomycin C was used as positive control. 4 With metabolic activation, cyclophosphamide was used as a positive control. 5 Dimethylsulfoxide was used as negative control and benzo (alpha)pyrene and ethylmethanesulfonate were used as positive controls with and without metabolic activation, respectively. 6 6-p-dimethylaminophenylazobenzthiazole was used as a positive control. Table 3. Results of in vivo genotoxicity assays on hexaconazole Test system Test object Concentration Purity Results Reference Micronucleus test C57/BL/6J mice 75 and 120 mg/kg 92.3% negative Sheldon, et al., (m+F) bone i.p.* 1984b marrow cells Dominant lethal test CD-1 male mice 10, 30 or 100 92.3% negative Wickramaratne, mg/kg bw for 5 et al., 1984 cons. days* * Cyclophosphamide was used as a positive control. Nine New Zealand white albino rabbits were given doses of 100 mg of undiluted hexaconazole (purity not stated) into the conjunctival sac of the left eye. The eyes of 3/9 rabbits were washed. All animals showed conjunctival redness, chemosis and discharge at 1 hour after application reversible within 3 days except for slight discharge that was still seen in 1/6 rabbits (unwashed) after 7 days (Southwood, 1984b). Hexaconazole was tested for skin sensitization in 20 Dunkin Hartley guinea pigs in a Magnusson Kligman test. The intradermal and topical induction concentrations were a 0.5% solution of hexaconazole (purity not given) in 4.5% dimethylformamide/corn oil and a 75% suspension in dimethylformamide, respectively. After a challenge with a 10% solution, 1/20 animals showed scattered mild redness; following challenge with a 25% solution 12/20 animals showed scattered mild redness. Following a re-challenge with a 25% solution 6/20 guinea pigs gave a positive response (Southwood, 1984c). Special study on steroid metabolism Isolated Leydig cells, prepared from the testes of adult Alpk:APfSD rats, were incubated with varying concentrations of either hexaconazole (0.1-30µm) or ketoconazole (0.l-10µm) for a period up to 24 hours. After the incubation period testosterone, progesterone and 17-OH progesterone were analyzed using specific radio immunoassays. The experiments were repeated in the presence of a maximally stimulating dose of HCG (human chorionic gonadotropin). A dose- related decrease in testosterone production, accompanied by an increase in the production of progesterone and 17-OH progesterone was observed after treatment with hexaconazole and hezaconazole in the presence of hCG. Incubation with ketoconazole showed the same effects, but ketaconazole is about 70-100 times more active than hexaconazole (Foster, 1990). The inhibition of testosterone production by ketoconazole was also reported in several in vivo as well as in vitro studies in humans, mice and rats (English et al., 1986; Pont et al., 1982; Santen et al., 1983; Lambert et al., 1986) Observations in humans No information was available. COMMENTS Following oral administration to rats, hexaconazole was rapidly and almost completely excreted via the urine and the faeces. The total radioactivity excreted was equal for both males and females, but females excreted a higher proportion of the dose in urine than in faeces. The highest tissue residues were found in the liver, intestinal contents and the adrenal cortex. Biliary excretion was extensive, accounting for about 80% and 40% of the total radioactivity in males and females respectively. About 50% of the radioactivity excreted in the bile was reabsorbed by enterohepatic circulation. Hexaconazole was metabolized via oxidation of the n-butyl chain by two pathways. The more important pathway was conversion of hexaconazole to 5-hydroxy-hexaconazole and 5-keto-hexaconazole; a minor pathway involved two-stage oxidation of the terminal methyl group to "hexaconazole acid" via 6-hydroxy-hexaconazole. Free triazole was also formed by cleavage of hexaconazole or its metabolites. The compound showed slight to moderate acute oral toxicity in rats and mice. WHO has classified hexaconazole as slightly hazardous based on acute toxicity and has concluded that it is "unlikely to present acute hazard in normal use" (WHO, 1990). From acute as well as from short-term studies it appeared that male rats were more sensitive than female rats. Short-term studies with mice, rats and dogs indicated that the liver is the primary target organ. Lipid accumulation in hepatic parenchymal cells was observed, with associated disturbances in lipid metabolism and blood chemistry. Elevated levels of aminopyrine-N-demethylase (rat) suggest an adaptive response in the liver. In a one-year study in dogs (capsule administration) the NOAEL was 2 mg/kg bw/day. However, a 90-day dog study (capsule administration) indicated a NOAEL of 5 mg/kg bw/day. Since the next highest dose in the one-year dog study was 10 mg/kg bw/day, the Meeting concluded that the appropriate NOAEL for dogs was probably 5 mg/kg bw/day. In the rat, cortical parenchymal vacuolation in the adrenal glands was observed. In a short-term feeding study in mice, effects on the male and female reproductive organs and on the adrenals were observed. From in vitro studies it can be concluded that hexaconazole inhibits testosterone production. In a long-term feeding study in mice (highest dose level 200 ppm) observed effects were reduced body weight gain, increased erythrocyte, haemoglobin and haematocrit values and, in the liver, increased weight and centrilobular fatty changes. The tumour incidence was not enhanced. The NOAEL in this study was 40 ppm, equal to 4.7 mg/kg bw/day for males and 5.9 mg/kg bw/day for females. In a long-term feeding study in rats, the same effects as in the short-term study were observed. In the testes, the incidence of benign Leydig cell tumours was slightly increased. The NOAEL in this study was 10 ppm, equal to 0.47 mg/kg bw/day in males and 0.6l mg/kg bw/day in females. After reviewing the available in vitro and in vivo short-term genotoxicity tests, it was concluded that there was no evidence of genotoxicity. Embryotoxicity/fetotoxicity was observed in a teratogenicity study in rats. No effects were observed at 2.5 mg/kg bw/day. Delayed ossification was observed in a rabbit teratogenicity study at the highest dose of 50 mg/kg bw/day; the NOAEL was 12.5 mg/kg bw/day. In a two-generation reproduction study in rats, reproductive performance was not affected. Parental body weight gain, food consumption and pup weight were decreased. Histopathological examination revealed fatty changes in the liver, either with or without hepatocytic hypertrophy, and cortical vacuolation of the adrenal gland in both parents and pups. The NOAEL in this study was 2.5 mg/kg bw/day. An ADI was allocated based upon the NOAEL from the rat long-term study (0.5 mg/kg bw/day), using a safety factor of 100. TOXICOLOGICAL EVALUATION Level causing no toxicological effect Mouse: 40 ppm in the diet, equal to 5.0 mg/kg bw/day Rat: 10 ppm in the diet, equal to 0.5 mg/kg bw/day Dog: 5 mg/kg bw/day Estimate of acceptable daily intake 0-0.005 mg/kg bw Studies which will provide information valuable in the continued evaluation of the compound Observations in humans. REFERENCES Allen, S.A. (1988) Hexaconazole: pharmacological evaluation. Unpublished report no.: CTL/P/1970 from ICI Central Toxicology Laboratory, Alderley Park, Macclesfield, Cheshire UK. Submitted to WHO by ICI Agrochemicals, Surrey, UK. Callander, R.D. (1984) PP523: An evaluation in the salmonella mutagenicity assay. Unpublished report no.: CTL/P/977 from ICI Central Toxicology Laboratory, Alderley Park, Macclesfield, Cheshire UK. Submitted to WHO by ICI Agrochemicals, Surrey, UK. Callander, R.D. (1988) Hexaconazole - an evaluation of mutagenic potential using E.coli. Unpublished report no.: CTL/P/2143 from ICI Central Toxicology Laboratory, Alderley Park, Macclesfield, Cheshire UK. Submitted to WHO by ICI Agrochemicals, Surrey, UK. Cross, M.F. (1986) PP523: Assessment of mutagenic potential using L5178Y Mouse Lymphoma Cells. Unpublished report no.: CTL/P/1298 from ICI Central Toxicology Laboratory, Alderley Park, Macclesfield, Cheshire UK. Submitted to WHO by ICI Agrochemicals, Surrey, UK. Davison, V.M. (1988) Hexaconazole: Acute oral toxicity to the rat. Unpublished report no.: CTL/P/2231 from ICI Central Toxicology Laboratory, Alderley Park, Macclesfield, Cheshire UK. Submitted to WHO by ICI Agrochemicals, Surrey, UK. English, H.F., Santner, S.J., Levine, H.B. and Santen, R.J. (1986) Inhibition of testosterone production with ketoconazole alone and in combination with a gonadotropin releasing hormone analogue in the rat. Cancer Res. 46, 38-42. Forbes, D. (1988) Hexaconazole: 29-day feeding study in mice. Unpublished report no. CTL/P/2204 from ICI Central Toxicology Laboratory. Submitted to WHO by ICI Agrochemicals, Surrey, UK. Foster, P.M.D. (1990) Effects of hexaconazole (ICIA523) on the steroidogenic function of isolated rat Leydig cells, Unpublished report no.: CTL/R/1035 from ICI Central Toxicology Laboratory, Alderley Park, Macclesfield, Cheshire UK. Submitted to WHO by ICI Agrochemicals, Surrey, UK. Hext, P.M. (1987) PP523: 4-hour acute inhalation toxicity study in the rat. Unpublished report no.: CTL/P/1731 from ICI PLC, Alderley Park, Macclesfield, Cheshire, UK. Submitted to WHO by ICI Agrochemicals, Surrey, UK. Hext, P.M. (1988a) Hexaconazole: two year feeding study in rats. Unpublished report no.: CTL/P/1920 from ICI Central Toxicology Laboratory, Macclesfield, Cheshire UK. Submitted to WHO by ICI Agrochemicals, Surrey, UK. Hext, P.M. (1988b) Second supplement to hexaconazole: two year feeding study in rats measurement of plasma corticosterone levels. Unpublished report no.: CTL/P/1920 from ICI Central Toxicology Laboratory, Macclesfield, Cheshire, UK. Submitted to WHO by ICI Agrochemicals, Surrey, UK. Jones, B.K., Galvin, G. Rhodes, S.J. and Soames, A.R. (1984) PP523: Excretion and tissue retention of a single dose (1 mg/kg) in the rat. Unpublished report no.: CTL/P/1148 from ICI Central Toxicology Laboratory, Alderley park, Macclesfield, Cheshire, UK. Submitted to WHO by ICI Agrochemicals, Surrey, UK. Jones, B.K. (1988a) Hexaconazole: repeat dose study (1mg/kg) in the rat. Unpublished report no.: CTL/P/2089 from ICI Central Toxicology Laboratory, Alderley Park, Macclesfield, Cheshire, UK. Submitted to WHO by ICI Agrochemicals, Surrey, UK. Jones, B.K. (1988b) Hexaconazole: whole body autoradiography study in the rat following 14 daily oral doses of 1 mg 14C-labelled hexaconazole/kg. Unpublished report no.: CTL/P/2052 from ICI Central Toxicology Laboratory, Alderley Park, Macclesfield, Cheshire, UK. Submitted to WHO by ICI Agrochemicals, Surrey, UK. Jones, B.K. (1989a) Hexaconazole: tissue distribution and elimination following a single oral dose (1 mg/kg) in the rat. Unpublished report no.: CTL/P/2389 from ICI Central Toxicology Laboratory, Alderley Park, Macclesfield, Cheshire, UK. Submitted to WHO by ICI Agrochemicals, Surrey, UK. Jones, B.K. (1989b) Hexaconazole: tissue distribution and elimination following a single oral dose (200 mg/kg) in the rat. Unpublished report no.: CTL/P/2390 from ICI Central Toxicology Laboratory, Alderley Park, Macclesfield, Cheshire, UK. Submitted to WHO by ICI Agrochemicals, Surrey, UK. Jones, B.K. (1989c) Hexaconazole: biotranformation in the rat with first amendment. Unpublished report no.: CTL/P/1848 from ICI Central Toxicology Laboratory, Alderley Park, Macclesfield, Cheshire, UK. Submitted to WHO by ICI Agrochemicals, Surrey, UK. Killick, M.E., Wickramaratne, G.A., Banham, P.B. and Thomas, M.R. (1984a) PP523: Teratogenicity study in the rat. Unpublished report no.: CTL/P/1127 from ICI Central Toxicology Laboratory, Alderley park, Macclesfield, Cheshire, UK. Submitted to WHO by ICI Agrochemicals, Surrey, UK. Killick, M.E., Wickramaratne, G.A., Banham, P.B. and Thomas, M.R. (1984b) PP523: Teratogenicity study in the rat. Unpublished report no.: CTL/P/1131 from ICI Central Toxicology Laboratory, Alderley park, Macclesfield, Cheshire, UK. Submitted to WHO by ICI Agrochemicals, Surrey, UK. Kinsey, D.L., Hollis, K.J., Chart, I.S., Gore, C.W., Godley, M.J. Pigott, G.H., Stonard, M.D. and Chalmers, D.T. (1984) PP523: 90-day feeding study in rats. Unpublished report no.: CTL/P/1073 from ICI Central Toxicology Laboratory, Alderley Park, Macclesfield, Cheshire, UK. Submitted to WHO by ICI Agrochemicals, Surrey, UK. Lambert, A., Mitchell, R., and Robertson, W.R. (1986) The effect of ketoconazole on adrenal and testicular steroidogenesis in vitro. Biochem. Pharmacol., 25(22), 3999-4004. Leah, A.M. (1989) Hexaconazole: acute oral toxicity to the mouse, including the first amendment to the report. Unpublished report no. CTL/P/2234 from ICI Central Toxicology Laboratory, Alderley Park, Macclesfield, Cheshire, UK. Submitted to WHO by ICI Agrochemicals, Surrey, UK. Middleton, M.C. (1988) Hexaconazole: two generation reproduction study in the rat. Unpublished report no.: CTL/P/1598 from ICI Central Toxicology Laboratory, Alderley Park, Macclesfield, Cheshire, UK. Submitted to WHO by ICI Agrochemicals, Surrey, UK. Pigott, G.H. (1988) Hexaconazole: two year feed study in mice. Unpublished report no. CTL/P/1929 from ICI Central Toxicology Laboratory, Alderley Park, Macclesfield, Cheshire, UK. Submitted to WHO by ICI Agrochemicals, Surrey, UK Pont, A., Williams, P.L., Azhar, S., Reitz, R.E., Bochra, C., Smith, E.R. and Stevens, D.A. (1982) Ketoconazole blocks testosterone synthesis. Arch. Intern. Med. 142, 2137-2140. Santen, R.J., Van den Bossche, H., Symoens, J., Brugmans, J. and DeCoster, R. (1983) Site of action of low dose ketoconazole on androgen biosynthesis in men. J. Clinical Endocrin. Metab. 57(4), 732- 736. Sheldon, T., Howard, A.C. and Richardson, C.R. (1984a) PP523: A cytogenetic study in human lymphocytes in vitro. Unpublished report no. CTL/P/1186 from ICI Central Toxicology Laboratory, Alderley Park, Macclesfield, Cheshire, UK. Submitted to WHO by ICI Agrochemicals, Surrey, UK. Sheldon, T., Richardson, C.R., Shaw, J. and Barber, G. (1984b) An evaluation of PP523 in the mouse micronucleus test. Unpublished report no. CTL/P/1136 from ICI Central Toxicology Laboratory, Alderley Park, Macclesfield, Cheshire, UK. Submitted to WHO by ICI Agrochemicals, Surrey, UK. Southwood, J. (1984a) PP523: Acute oral and acute dermal toxicity studies. Unpublished report no. CTL/P/1113 from ICI Central Toxicology Laboratory, Alderley Park, Macclesfield, Cheshire, UK. Submitted to WHO by ICI Agrochemicals, Surrey, UK. Southwood, J. (1984b) PP523: Skin and eye irritation studies. Unpublished report no. CTL/P/1043 from ICI Central Toxicology Laboratory, Alderley Park, Macclesfield, Cheshire, UK. Submitted to WHO by ICI Agrochemicals, Surrey, UK. Southwood, J. (1984c) PP523: Skin sensitisation study. Unpublished report no. CTL/P/1049 from ICI Central Toxicology Laboratory, Alderley Park, Macclesfield, Cheshire, UK. Submitted to WHO by ICI Agrochemicals, Surrey, UK. Stonard, M.D. (1989) PP523: 90-day oral dosing study in dogs and first amendment. Unpublished report no. CTL/P/1137 from ICI Central Toxicology Laboratory, Alderley Park, Macclesfield, Cheshire, UK. Submitted to WHO by ICI Agrochemicals, Surrey, UK. Stonard, M.D. (1988) Hexaconazole: 1 year oral dosing study in dogs. Unpublished report no. CTL/P/1942 from ICI Central Toxicology Laboratory, Alderley Park, Macclesfield, Cheshire, UK. Submitted to WHO by ICI Agrochemicals, Surrey, UK. Trivedi, S., Jones, B.K. and Soames, A.R. (1986) PP523: Excretion and tissue retention of a single oral dose (200 mg/kg) in the rat. Unpublished report no. CTL/P/1431 from ICI Central Toxicology Laboratory, Alderley park, Macclesfield, Cheshire, UK. Submitted to WHO by ICI Agrochemicals, Surrey, UK. Trueman, R.W. (1988) Hexaconazole: Assessment for the induction of unscheduled DNA synthesis in primary rat hepatocyte cultures. Unpublished report no. CTL/P/1887 from ICI Central Toxicology Laboratory, Alderley Park, Macclesfield, Cheshire, UK. Submitted to WHO by ICI Agrochemicals, Surrey, UK. Wickramaratne, G.A., Bramley, J.R., Banham, P.B. and Godley, M.J. (1984) PP523: Dominant lethal study in the mouse. Unpublished report no. CTL/P/1110 from ICI Central Toxicology Laboratory, Alderley Park, Macclesfield, Cheshire, UK. Submitted to WHO by ICI Agrochemicals, Surrey, UK. WHO (1990). The WHO recommended classification of pesticides by hazard and guidelines to classification 1990-1991 (WHO/PCS/90.1). Available from the International Programme on Chemical Safety, World Health Organization, Geneva, Switzerland.
See Also: Toxicological Abbreviations