HALOXYFOP First draft prepared by E. Bosshard Federal Office of Public Health, Food Science Division, Schwerzenbach, Switzerland Explanation Evaluation for acceptable daily intake Biochemical aspects Absorption, distribution, and excretion Biotransformation Toxicological studies Acute toxicity Short-term toxicity Long-term toxicity and carcinogenicity Reproductive toxicity Developmental toxicity Genotoxicity Special studies Dermal and ocular irritation and dermal sensitization Peroxisome proliferation Stereochemical inversion Comments Toxicological evaluation References Appendix: Expert report Explanation Haloxyfop is a substituted phenoxypropionic acid derivative which has been developed as a selective herbicide for the control of grass weeds in broad-leaf crops. In the first formulations produced, the active substance was either racemic haloxyfop ethoxy ethyl ester or the racemic methyl ester. When applied to plants, the ester is rapidly hydrolysed to the acid which has herbicidal activity. As it has been demonstrated that the R-isomer of haloxyfop is the herbicidally active compound, and essentially no activity is associated with the S-isomer, a resolved methyl ester has been developed which is approximately 98% R-isomer. Haloxyfop was evaluated for the first time by the present Meeting. Evaluation for acceptable daily intake 1. Biochemical aspects (a) Absorption, distribution, and excretion Several studies on the fate of haloxyfop and its esters were performed in rats, mice, dogs, monkeys, and also humans. All of the studies with radiolabelled material were conducted with haloxyfop acid or ester labelled with 14C in the phenyl ring. Male and female B6C3F1 mice were treated with a single oral dose of 5 mg/kg bw 14C-haloxyfop (acid), administered as the sodium salt, and its absorption, distribution, and elimination were investigated over 168 h. The absorption half-life was about 2 h, and the clearance half-lives in plasma, liver, kidney, and excreta were about two days in animals of each sex. At least 60% of the applied dose was excreted in the faeces and about 20% in the urine seven days after treatment. No sex difference in the excretion pattern of haloxyfop was observed. The bile was the major route of excretion in males and females (Smith et al., 1984). In a range-finding study, Fischer 344 rats were given single intravenous or oral doses of 0.5 or 50 mg/kg bw (males) or 10 mg/kg bw (females) of 14C-labelled haloxyfop (acid) as the sodium salt. Plasma was sampled and the excreta were collected for 120 h after treatment. The animals were then killed, and the organs were analysed for 14C activity. During a collection period of five days, the mean urinary excretion in male rats was about 14% of the applied dose and mean faecal excretion was 29%. No meaningful difference was found between the two routes of application or between doses. Three days after the oral dose of 10 mg/kg bw, the urine of female rats contained about 45% and faeces, 21%. After intravenous injection, urinary excretion in females was 57% and faecal excretion about 16%, indicating biliary excretion. The plasma half-life in males was about four days after intravenous administration of either dose, and a similar plasma half-life of about three days was found after oral treatment. In females, a plasma half-life of one day was observed, regardless of the route of administration. In the definitive study, male and female Fischer 344 rats were given a single oral dose of 0.1 mg/kg bw 14C haloxyfop (acid) applied as the sodium salt. Males excreted about 70% of the applied dose in faeces and about 19% in urine during a 28-day observation period; females excreted about 21% in faeces and 72% in urine during an observation period of 13 days. Most of the urinary radiolabel appeared within the first few days after treatment in females. The plasma half-lives were about six days for males and one day for females. The concentrations of radiolabel in selected tissues were highest in liver, with 0.6 ppm haloxyfop equivalents one day after treatment in males and 0.5 ppm in females. The average half-life in male tissues was six days and that in female tissues one day, corresponding to the plasma half-lives (Smith et al., 1982). Male and female Fischer 344 rats were given a single dose of 0.104 mg/kg bw 14C-haloxyfop methyl ester by gavage. The 14C activity was excreted primarily (60% of the applied dose) in the faeces of males and mainly (67%) in the urine of females; about 20% was excreted in the urine and faeces of males and females. The elimination half-lives in liver and kidney were consistent with the plasma half-lives: about five days in males and about one day in females. After oral administration of haloxyfop methyl ester, the plasma contained the highest 14C concentration, followed by liver, kidney, erythrocytes, and fat. The 14C concentration in fat varied between 0.009 and 0.067 ppm haloxyfop methyl ester equivalents- typically five to thirty times lower than the plasma concentration. Thus, the propensity for deposition and accumulation of the methyl ester in adipose tissue is low (Waechter et al., 1982). Male Fischer 344 rats, animals were given a single dose of 0.12 mg/kg bw of labelled haloxyfop ethoxy ethyl ester in corn oil by gavage, and the kinetic profiles in blood and tissues were determined over 10 days. The plasma concentration of radiolabel peaked about 4 h after treatment. The half-life for absorption was 2 h and that for elimination about four days. The administered label was excreted primarily in the faeces, to about 50% of the applied dose over 10 days; about 15% was excreted in the urine over the same period. The elimination half-lives in plasma, liver, kidney, and excreta were similar, averaging five days (Smith et al., 1983). Male beagle dogs received a single oral dose of 2.4 mg/kg bw 14C-haloxyfop (acid) as the sodium salt. The compound was rapidly absorbed, with a half-life of 9 min. Plasma elimination was bi-exponential; the half-life of the initial, rapid phase was about 1-2 h and that of the terminal phase about 34 h. Within eight days of treatment, about 77% of the dose had been eliminated in the faeces and about 10% in the urine. A high concentration of radiolabel was also found in bile (40 times the concentration in plasma), indicating biliary excretion (Nolan et al., 1987). In a range-finding study, unlabelled haloxyfop (acid) was administered as the sodium salt to male cynomolgus monkeys by nasogastric intubation, either as single oral doses of 40, 80, or 120 mg/kg bw or as multiple doses of 20, 40, or 60 mg/kg bw per day over five consecutive days. The doses of 80 and 120 mg/kg bw resulted in loss of appetite and decreased activity. Repeated administration of 40 mg/kg bw per day was associated with slight loss of appetite and weight: loss and the dose of 60 mg/kg bw per day with emesis and severe loss of appetite. On the basis of these results, doses of 5 and 20 mg/kg bw per day were selected for a four-week study of peroxisome stimulation, summarized in section ( g)(i) (Gerbig et al., 1985). One male monkey was given a nasogastric dose of 1 mg/kg bw unlabelled haloxyfop as the sodium salt, and blood, urine, and faeces were collected over 21 days. After a 10-week recovery, the monkey was given 1 mg/kg bw of 14C-haloxyfop, and blood and the excreta were analysed over six days. The compound was rapidly absorbed from the gastrointestinal tract, with a half-life of < 30 min, mainly in the urine (about 84% of the applied dose), with only 0.5% in the faeces. Plasma elimination was bi-exponential; the half-life of the initial, rapid phase was 2.5 h and that of the slower, terminal phase, three days (Gerbig et al., 1985). Laying hens were given 14C-haloxyfop (acid) in gelatin capsules for 11 days at a level equivalent to 12 ppm. The excreta contained 87% of the radiolabel, mainly as unchanged haloxyfop; 2 ppm was present in liver and 4 ppm in kidney, primarily as the parent haloxyfop and polar conjugates, while the residues in body fat and egg yolks consisted primarily of non-polar lipids, which in egg yolks were found to be incorporated into triacylglycerols (Yackovich & Miller, 1983a). Two lactating goats were given 14C haloxyfop (acid) twice daily in gelatin capsules for 10 days at a rate of 16 ppm. About 90% of the applied dose was excreted in urine as unchanged haloxyfop. The residues in tissues 12 h after the last dose were 0.4 ppm in liver, 1.3 ppm in kidney, and < 0.1 ppm in fat and other tissues. The residue levels in whole milk, primarily in triacylglycerols in fat, were about 0.3 ppm, corresponding to about 2-3% of the applied dose (Yackovich & Miller, 1983b). The pharmacokinetics of haloxyfop and its methyl ester was investigated in eight male volunteers, who received a single oral dose of 0.2 mg/kg bw haloxyfop as the sodium salt or a single dermal dose of 0.8 mg/kg bw haloxyfop methyl ester in xylene and surfactants. After oral administration, the compound was rapidly absorbed, with a half-life of 0.9 h, and excreted with a half-life of about six days. Urine was the principal route of elimination, containing about 79% of the applied dose. Slow skin absorption was observed after dermal application, with a half-life of 37 h. The urinary excretion indicated that only about 3% of the applied dose had been absorbed As the elimination half-life was also about six days, the elimination kinetics is independent of the route of administration. Moreover, the similarity of the excretion patterns of haloxyfop and its methyl ester suggest that the ester is rapidly hydrolysed to the parent acid in man as well (Nolan et al., 1985a). The experimental data indicated that these esters are rapidly hydrolysed in vivo to the acid form of haloxyfop (Smith et al., 1983) and that the toxicity of the esters and acid forms are equivalent on a molar basis (Herman et al., 1983b); however, the ester moiety may alter the rate and extent of percutaneous absorption -- an important factor with respect to the exposure of applicators. An additional study was therefore carried out in which a single dermal dose of a 12.5% haloxyfop EE-containing formulation, corresponding to 0.77 mg/kg bw of haloxyfop ethoxy ethyl ester, was applied topically to the forearms of three male volunteers. The clearance from plasma and the urinary excretion were similar to those seen in the study of haloxyfop methyl ester (Nolan et al., 1985a), indicating that the haloxyfop ethyl ester is also rapidly hydrolysed to the acid. The dermal absorption was estimated to be about 1% of the applied dose (Nolan et al., 1985b). (b) Biotransformation In male and female B6C3F1 mice treated with a single oral dose of 5 mg/kg bw 14C-haloxyfop (acid), as the sodium salt, unchanged parent compound was found in plasma, bile, and urine samples, and a glucuronide conjugate was identified (Smith et al., 1984). One male and one female rat were given a single oral dose of 2.5 mg/kg bw 14C-haloxyfop (acid) administered as the sodium salt or 14C-haloxyfop methyl ester in corn oil. More than 97% of the 14C activity in plasma, erythrocytes, and liver was identified as the parent acid. No peak was observed at the retention time of the methyl ester 48 h after treatment, suggesting that rapid hydrolysis of the ester had occurred in the gastrointestinal tract, probably before absorption. Haloxyfop acid and one major and two minor species were detected in the urine of male and female rats. The urine of males given haloxfop contained 75%, of the 14C activity, and that of males given the methyl ester contained 60%; the urine of females given haloxfop contained 94% and that of females given the methyl ester contained 89% of the radiolabel excreted in the form of the parent acid. Bile from both male and female rats also contained haloxyfop (parent acid), representing about 50% of the radiolabel found in bile plus a conjugate (Smith et al., 1982). Male and female Fischer 344 rats received a single oral dose of 2.5 mg/kg bw 14C haloxyfop methyl ester in corn oil, and analysis of plasma at various times showed the presence of haloxyfop (acid) at the levels that would be expected after administration of an equimolar dose of haloxyfop itself. Furthermore, as in the study conducted by Smith et al. (1982), no methyl ester was detected in blood 24 h after treatment (Waechter el al., 1982). Male Fischer 344 rats were given a single oral dose of 1.4 or 2.5 mg/kg bw 14C-haloxfop ethoxy ethyl ester in corn oil. No ester was seen in any blood sample extracted under either acidic or non-acidic conditions, and the ester appears to be rapidly hydrolysed, presumably in the gastrointestinal tract or at the latest in the blood. Analysis of non-acidified blood extracts from rats given the ethoxy ethyl ester by gavage showed that 80% of the 14C activity represented a conjugate of haloxyfop (acid) and about 20% corresponded to the parent acid (Smith et al., 1983). In male beagle dogs that received a single oral dose of 2.4 mg/kg bw 14C-haloxyfop (acid) as the sodium salt, virtually all of the radiolabel in the faeces but less than 25% of that in bile represented unchanged haloxyfop. It may therefore be assumed that the metabolites in the bile were conjugates that hydrolysed back to the parent acid in the gastrointestinal tract (Nolan et al., 1987). 2. Toxicological studies (a) Acute toxicity The results of studies of the acute toxicity of haloxyfop (acid) and its methyl and ethoxy ethyl esters are summarized in Table 1. Signs of acute toxicity consisted of rapid shallow breathing, prostration, and lethargy. The oral LD50 values for haloxyfop (acid) and its esters are similar in rats and mice, indicating that they have a common metabolic pathway. A comparison of the LD50 values after oral and intraperitoneal administration also reveals similar values, indicating extensive gastrointestinal absorption. These results are in good agreement with the findings of the various pharmacokinetic studies. The marked difference in the oral LD50 value for haloxyfop EE in rats reported by Carreon et al. (1982) (520 mg/kg bw) and Jones (1983a,b) (2870 mg/kg bw) may be due to greater gastrointestinal absorption when the test material is formulated in a 10% acetone-corn- oil solution instead of distilled water. (b) Short-term toxicity Mice Groups of 10 male and 10 female B6C3F1 mice (15 controls of each sex) were fed diets containing concentrations of haloxyfop (acid) (purity, 96%) corresponding to 0, 0.002, 0.02, 0.2, or 2 mg/kg bw per day for 13 weeks. Further groups of 10-12 mice of each sex were given doses of 0, 0.02, or 2 mg/kg bw per day for 36 weeks, with an interruption of one week between week 13 and 14. In the 13-week study, treatment-related effects were seen only at the highest dose. Reduced body weight was seen only in females. Males had slightly increased serum alkaline phosphatase activity. Haematological parameters were not influenced by treatment. At necropsy, alterations were observed grossly only in the liver, consisting of slight enlargement and darkening in animals of each sex, accompanied by increased liver weights. Histopathological changes were confined to the liver and again to the highest dose group; they consisted of hepatocellular enlargement and greater cytoplasmic homogeneity (lack of cytoplasmic microvesiculation) than in controls. In the 36-week study, treatment had no effect on behaviour, body-weight development, food consumption, or haematological parameters. In males at the highest dose, increased alkaline phosphatase activity was observed. In animals at this dose, the livers were slightly enlarged and darkened and their weights were increased, and the kidney weights of males were decreased. Histopathological alterations were observed in the livers of animals of each sex and in the kidneys of males. The changes in the liver consisted of hepatocellular enlargement, increased cytoplasmic homogeneity, and slightly increased eosinophilia. The kidneys of the males at the highest dose showed decreased cytoplasmic vacuolation of the proximal convoluted tubular cells in comparison with controls. The NOAELs were 0.2 mg/kg bw per day in the 13-week study and 0.02 mg/kg bw per day in the 36-week study Gorzinski et al., 1982a). Rats In a four-week study, groups of five CDF Fischer 344 rats of each sex (control group, 10 rats of each sex) received haloxyfop (acid) (purity, 99.99 or 99%) in the diet providing concentrations of 0, 0.01, 0.1, 1, and 10 mg/kg bw per day. The doses were selected on the basis of the results of a one-week palatability and a two-week dietary study (Tollett et al., 1981). Effects on the liver were indicated by an increase in serum alkaline phosphatase activity in males at the highest dose. An increase in liver weights at 1 and 10 mg/kg bw per day was most pronounced in males. Histopathological changes observed at > 1 mg/kg bw per day in animals of each sex consisted of hepatocellular swelling and increased eosinophilic staining of the cytoplasm. A slight decrease in mature sperm (spermatozoa) was seen in the testes and epididymides of some rats at 10 mg/kg bw per day. The NOAEL was 0.1 mg/kg bw per day, biased on biochemical, histological, and weight changes in the liver (Gorzinski et al., 1982b). Table 1. Acute toxicity of haloxyfop (acid) and its methyl and ethoxy ethyl esters Test materiala Species Sex Route LD50 or LC50 Purity Reference (mg/kg bw or (%) mg/litre air) Haloxyfop (acid) Rat Male Oral 340 NR Carreon et al. (1980) Female 550 Haloxyfop EEb Rat Male, female Oral 520 95 Carreon et al. (1982) Haloxyfop EE Rat Male Oral 700 94.7 Jones (1983a) Female 900 Haloxyfop EEc Rat Male, female Oral 2870 98.8 Jones (1983b) Haloxyfop ME Rat Male Oral 300 98.6 Mizell & Lomax (1989a) Female 620 Haloxyfop (acid) Rabbit Male, female Dermal > 5000 NR Carreon et al. (1980) Haloxyfop EE Rat Male, female Dermal > 5000 95 Carreon et al. (1982) Haloxyfop EE Rat Male, female Dermal > 2000 94.7 Jones (1982a) Haloxyfop EE Rat Male, female Dermal > 2000 98.8 Jones (1982b) Haloxyfop ME Rat Male, female Dermal > 2000 98.6 Mizell et al. (1989) Haloxyfop EEd Rat Male, female Intraperitoneal 670 96.5 Jones el al. (1986) Haloxyfop MEe Rat Male, female Intraperitoneal 220 98.6 Mizell et al. (1989) Haloxyfop EE Mouse Male, female Oral 610 97 Oda (1986) Haloxyfop ME Mouse Male, female Oral 710 98.6 Mizell & Lomax (1989b) NR, not reported a Haloxyfop EE, haloxyfop ethoxy ethyl ester; haloxyfop ME, haloxyfop methyl ester b Administered as a 10% solution in a 10% acetone-corn oil (1:9) solution c Formulated in distilled water d Formulated in arachis oil e Administered as a 25% solution in corn oil Groups of 80 male CDF Fischer 344 were fed diets providing doses of 0, 0.1, or 1 mg/kg bw per day for four weeks and were then allowed to recover for six weeks. Groups of 7-10 rats per dose were sacrificed at two-week intervals during both the treatment and the recovery period to study the onset and reversibility of hepatic changes. Treatment-related effects appeared at both doses, consisting of increased liver weights (transient at 0.1 mg/kg bw per day) accompanied by histopathological changes (hepatocellular enlargement and cytoplasmic eosinophilia) at the highest dose. After the recovery period, only the relative liver weights of animals at the high dose were still increased, but the histological changes remained. In animals sacrificed after four and six weeks of recovery, no changes were seen. The serum levels of haloxyfop were approximately proportional to the dose. The plasma clearance half-life of six days after a single oral dose was similar to the serum clearance half-lives of eight days for both doses after repeated oral administration (Herman et al., 1983a). Groups of 15 Fischer 344 rats of each sex received doses of 0, 0.002, 0.02, 0.2, or 2 mg/kg bw per day haloxyfop (acid) (purity, 96%) for 16 weeks, and groups of 12 received doses of 0, 0.02, or 2 mg/kg bw per day for 37 weeks. In the 16-week study, treatment had no effect on behaviour, body weight, food consumption, haematological parameters, or the results of urinalysis. As a viral infection (symptoms consistent with sialodacryoadenitis) was observed in animals in all groups a few days before the scheduled termination of the study, it was extended for an additional three weeks. Male rats at the highest dose showed a slight increase in alkaline phosphatase activity; a dose-related increase in liver weight was observed in males at 0.2 and 2 mg/kg bw, and testicular weights were slightly decreased at 2 mg/kg bw. In females, increased liver weights were observed only at the highest dose. At this dose, the kidneys of animals of each sex were darkened or greenish. Histopathological examinations of most organs revealed changes in the liver consisting of enlarged hepatocytes and a slightly increased degree of cytoplasmic homogeneity in males at 0.2 and 2 mg/kg bw and an increased degree of cytoplasmic homogeneity in females only at the highest dose. The darkened appearance of the kidney was not seen as differences in pigmentation of the renal tubular epithelial cells on microscopic examination. In the 37-week study, the same viral infection affected animals in all dose groups. No significant difference was observed in body weights between treated and untreated animals at termination of the study. The treatment did not change the results of haematology or urinalysis. Significant differences in clinical chemical parameters at the highest dose consisted of a slight increase in alkaline phosphatase activity, particularly in males, and an increase in serum alanine aminotransferase activity, particularly in females. Gross pathological changes observed in the liver and kidney of males at the highest dose consisted of slight liver enlargement and discolouration of the kidneys. The liver weights were increased at this dose in animals of each sex. Histopathological examination of the livers revealed hepatocellular enlargement and increased cytoplasmic homogeneity at the highest dose in males and females. In the kidneys, slight, chronic, progressive glomerulonephropathy occurred at a higher incidence in males at the highest dose than in controls. Variable accumulation of brown pigment in renal tubular epithelial cells was seen in all treated animals and was extensive in males at the highest dose. The pigment did not react with stains used to detect the presence of iron, calcium, phosphate, or bilirubin or lipofuscin pigment but probably represented a form of ceroid or lipofuscin pigments. No other histopathological alteration, including degenerative changes, was found in the kidneys. The NOAEL in the 16-week study was 0.02 mg/kg bw per day for males and 0.2 mg/kg bw per day for females, based on changes in liver weight and histopathology. The NOAEL in the 37-week study was 0.02 mg/kg bw per day, based on biochemical, macroscopic, and microscopic changes in the liver (Gorzinski et al., 1982c). Groups of 10 male Fischer 344 rats were fed diets containing haloxyfop ethoxy ethyl ester (purity, 99.3%) at concentrations providing daily doses of 0, 0.00028, 0.0028, or 0.028 mmol/kg bw per day, equivalent to 0, 0.1,1, and 10 mg/kg bw per day haloxyfop (acid). The treatment had no effect on body weight, food consumption, or the results of urinalysis. Clinical chemical examinations revealed a treatment-related increase in serum alkaline phosphatase activity, which was statistically significant only at the high dose, and dose-dependent decreases in cholesterol concentrations, which were statistically significant at the two higher doses; a slight but statistically significant increase in albumin and a slight decrease in globulin levels were also found at these doses. At the highest dose, minor decreases in packed cell volume, haemoglobin levels, and red blood cell count were observed. Organ weight changes consisted of an increase in liver weights at the two higher doses and a decrease in testicular weights at the highest dose. Treatment-related gross pathological alterations were limited to the livers of animals at the two highest doses and consisted of an increase in liver size. The enlarged livers and increased liver weights at the two higher doses, equivalent to 1 and 10 mg/kg bw haloxyfop (acid), respectively, were qualitatively and quantitatively similar to the results seen with haloxyfop (acid). The NOAEL was 0.00028 mmol/kg bw per day haloxyfop ethoxy ethyl ester, equivalent to 0.1 mg/kg bw per day haloxyfop (acid), based on a reduction in cholesterol concentration (Herman et al., 1983b). A sample of the optically-active R-enantiomer form of haloxyfop (purity, 99.4%) was given in the diet to groups of 10 male and 10 female Fischer 344 rats, at concentrations providing doses of 0, 0.065, 0.2, or 2 mg/kg bw per day, for 16 weeks. Two additional groups of 10 rats of each sex were kept on diets providing levels of 0 or 2 mg/kg bw per day for the same period and were then allowed to recover for four weeks. Females at the highest dose had slightly increased food consumption and body-weight gain. Males at the highest dose had small decreases in packed cell volume, haemoglobin, and erythrocyte count, which were minimal although statistically significant, after the recovery period. No further effects were seen on erythrocyte morphology or histopathological evaluation of the bone marrow. Alkaline phosphatase activity and potassium levels were increased in animals of each sex at the highest dose. Cholesterol levels were decreased in males at 0.2 and 2 mg/kg bw and in females at 2 mg/kg bw. All of these parameters returned to normal during the recovery period. Liver weights were increased in males and females at the highest dose, and relative liver weights were increased in males at 0.2 mg/kg bw, even after the recovery period. Testicular weight was decreased at the highest dose, and the decrease remained after the recovery period. Gross pathological examination reveal no alterations; microscopic alterations were confined to the livers of males at the highest dose and consisted of enlarged centrilobular hepatocytes and increased eosinophilic staining of hepatocytes. No such effects were observed at the end of the recovery period. The NOAEL was 0.065 mg/kg bw per day, based on the reduction in cholesterol levels (Barna-Lloyd et al., 1989). Dogs Groups of two beagle dogs of each sex were fed diets containing haloxyfop (acid) (purity, > 99%) for five weeks, at doses selected on the basis of the results of a range-finding and palatability study (Barna-Lloyd, 1983a) of 0, 5, 15, and 45 mg/kg bw per day. Bloody faeces were seen sporadically in both males and one female at the high dose. As a duodenal ulcer was also found in one male dog and as ulcerative lesions of the gastric and duodenal mucosa were found in the range-finding study, a causative relationship to the treatment cannot be excluded. Both males at the high dose showed clinical signs of illness towards the end of the study, resulting in a diagnosis of pneumonia; this effect was considered not to be a direct result of treatment but to be due to aspiration of feed particles. The treatment resulted in marked weight loss in both males and in one female at the high dose and in animals of each sex at the intermediate dose. Food consumption was reduced only at the high dose in animals of each sex. Alterations in haematological parameters were observed in these animals, consisting of decreases in packed cell volume, erythrocyte count, and haemoglobin values, particularly in males; the platelet count was markedly reduced in most animals at this dose. Alanine transaminase and serum alkaline phosphatase activities were markedly increased in animals of each sex at the high dose, and cholesterol concentrations were reduced in animals of each sex at 15 and 45 mg/kg bw. Bromsulphthalein retention in serum, determined as an indicator of the excretory function of the liver, was markedly increased in animals of each sex at the high dose. The relative liver and kidney weights were increased in males at the intermediate and high doses and in females at the high dose. The only pathological lesion probably attributable to treatment was the duodenal ulcer found in one male at the high dose; histopathological examination confirmed the presence of a focal, sharply demarcated ulcer. The NOAEL was 5 mg/kg bw per day, based on reduced body-weight gain, changes in biochemical parameters, and changes in liver and kidney weights (Barna-Lloyd et al., 1983b). Groups of four male and four female beagle dogs were fed diets providing doses of 0, 2, 5, or 20 mg/kg bw per day of haloxyfop (acid) (purity, 99.8%) for 13 weeks. Survival, food consumption and the results of urinalysis and ophthalmoscopy were not affected by the treatment. At the highest dose, decreased body-weight gain was found in animals of each sex, resulting in reduced overall body-weight gain only in males. Males and females at the highest dose had decreased erythrocyte counts, haemoglobin concentrations, haematocrit values, and platelet levels. A decrease in cholesterol concentration was observed at the intermediate and high doses. Slightly reduced levels of total and free triiodothyronine, and free thyroxin were also seen at these doses, accompanied by decreases in thyroid and parathyroid weights. At the highest dose, liver weights were increased in animals of each sex and kidney weights were increased, particularly in males. Histopathological examination revealed alterations in the liver, thyroid, and testis of animals at doses > 5 mg/kg bw. In the liver, slight hepatocellular enlargement was noted at the highest dose in animals of each sex and at the intermediate dose in females; this change appeared to be associated with glycogen deposition. The microscopic alterations in the thyroid glands consisted of a slight decrease in follicular size and hypertrophy of follicular epithelial cells at the two higher doses. The decreased amount of colloid in thyroid follicles seen at these doses suggests that the changes were an adaptive mechanism that may be associated with an increased rate of colloid turnover. Alterations in the testes observed at the two higher doses included a slight decrease in tubular size and more multi- nucleated spermitids in the tubular lumens. As these changes may reflect normal variation in maturation, a relationship with treatment is questionable. As significant increases in hepatic peroxisomal fatty acid ß-oxidation or peroxisomal volume density have been reported in animals fed dietary levels of haloxyfop as low as 0.5 mg/kg bw (rats) and 1 mg/kg bw (mice) (Stott et al., 1985a,b; see section ( g)(ii)), similar studies were conducted in these dogs. Electron microscopic examinations of hepatocytes of animals in the control and high-dose groups indicated no change in peroxisomal volume density or structural changes in peroxisomes or other organelles. Hepatic peroxisomal fatty acid ß-oxidation (substrate, palmitoyl-coenzyme A) was, however, induced in vitro at the intermediate and high doses. The NOAEL was 2 mg/kg bw per day, based on changes in biochemical parameters and organ weights and histopathological effects on the liver and thyroids (Dietz et al., 1987). Groups of six beagle dogs of each sex were fed diets containing targeted doses of 0, 0.05, 0.5, and 5 mg/kg bw per day of haloxyfop (acid) (purity, 99.9%) for 12 months. Treatment had no effect on general condition, body-weight development, food consumption, organ weights, or the results of urinalysis. Treatment-related effects occurred in animals of each sex only at the highest dose. Haematological examination revealed slightly decreased packed cell volume and haemoglobin in males at the intermediate and high doses, with no clear dose-response relationship; moreover, the packed cell volumes of concurrent controls were reported to be unusually high in comparison with those of historical controls, resulting in significant decreases of this parameter. The same explanation may be valid for the haemoglobin values. These haematological changes were therefore considered not to be biologically relevant. Changes in some clinical chemical parameters were inconsistent, except that serum cholesterol levels were decreased in animals of each sex at the highest dose. No gross pathological or histopathological lesions attributable to treatment were seen. The NOAEL was 0.5 mg/kg bw per day, based on reduced cholesterol levels (Barna-Lloyd et al., 1984). Monkeys Groups of four male and four female cynomolgus monkeys were given haloxyfop (acid) (purity, 99%) at doses of 0, 2, 10, or 30 mg/kg bw per day by nasogastric intubation for 13 weeks. The doses were selected on the basis of the results of a four-week study of liver peroxisome density (Gerbig et al., 1985; see section ( g)(ii)). Treatment had no effect on body weight, food consumption, or the results of ophthalmoscopy. Erythrocyte count, haemoglobin concentration, and haematocrit were slightly reduced in animals at the highest dose, the effects being less pronounced in females than in males; no effects were seen in bone marrow or peripheral blood. At this dose, the cholesterol concentration was decreased in animals of each sex. The changes in organ weights consisted of an increase in kidney weights at the two higher doses and increased liver and decreased thyroid weights at the highest dose. Microscopic examination revealed hepatocellular hypertrophy associated with an increased content of cytoplasmic lipid. Less severe hepatocyte enlargement was also noted in single animals at the intermediate dose. Electron microscopic examination of the hepatocytes confirmed a slightly higher cytoplasmic lipid volume density in monkeys at the highest dose. The thyroid glands of some animals in different dose groups were decreased in size, and the size and weight differences observed in females at the high dose were associated with a decrease in the size of thyroid follicles and an increase in the size of the epithelial cells lining the follicles (hypertrophy). These effects were not accompanied by cell necrosis and were probably due to a physiological increase in colloid turnover. The incidence of microscopic changes in the thyroids of males at the high dose was not different from that in the controls or other treatment groups. Quantitative ultrastructural evaluation of centrilobular hepatocytes from male and female monkeys given 0 and 30 mg/kg bw revealed no difference in peroxisomal volume density but indicated a slight increase in smooth endoplasmic reticulum in those treated with the high dose. There was no significant difference in hepatic peroxisomal activity between control and treated monkeys. The NOAEL was 2 mg/kg bw per day, based on organ weight changes and histopathological alterations in the liver (Yano et al., 1987). (c) Long-term toxicity and carcinogenicity Mice Groups of 70 male and 70 female B6C3F1 mice were maintained on diets providing haloxyfop (acid) (purity, 99.6%) at doses of 0, 0.03, 0.065, or 0.6 mg/kg bw per day. Ten mice of each sex per group were sacrificed at six and 12 months, and the remaining 50 animals of each sex were killed after 24 months. Treatment had no effect on behaviour, mortality, body-weight development, food consumption, or haemato- logical or clinical chemical parameters. The liver weights of males at the highest dose were slightly increased after six and 12 months of treatment, and histopathological examination showed slightly altered cytoplasmic tinctorial properties of centrilobular hepatocytes and a decrease in cytoplasmic vacuolization in male and female mice at this dose. The liver weights were not increased at termination of the study. Gross pathological examination showed an increased number of treated mice with one or more liver masses or nodules, with incidences in males of 22, 30, 32, and 34% and in females of 12, 14, 26, and 26% at 0, 0.03, 0.065, and 0.6 mg/kg bw per day, respectively. Histological examination revealed an increase in the incidence of hepatic foci in males at 0.03 and 0.6 mg/kg bw in comparison with concurrent controls, with incidences of 14, 24,10, and 24%, respectively. Dose-dependent increases in the incidences of hepatocellular tumours were seen in male and female mice at 0.065 and 0.6 mg/kg bw, which were statistically significant in males at the highest dose: The incidences of primary hepatocellular tumours (benign or malignant) were 26, 30, 40, and 54% in males and 14, 18, 26, and 30% in females, respectively. The incidence of benign hepatocellular adenoma in males at the highest dose was 38%, and the incidence of malignant, non-metastatic hepatocellular tumours in females was 16%; these incidences were significantly increased in comparison with controls. The ranges of incidence of primary hepatocellular neoplasms in historical control mice of this strain were reported to be 23-60% in males and 9-32% in females; the ranges of incidence were 12-52% and 7-24% for adenoma and 5-24% and 0-10% for carcinoma (adapted from Billington, 1995). The NOAEL was 0.03 mg/kg bw per day, based on a dose-related increase in the incidence of hepatocellular tumours in animals of each sex at 0.065 and 0.6 mg/kg bw per day (Tollett et al., 1985) A review of the carcinogenicity of haloxyfop in mice was also available (Swenberg, 1994; see Appendix). Rats Groups of 50 male and 50 female Fischer 344 rats were fed diets containing haloxyfop (acid) (purity, 99.7%) at targeted doses of 0, 0.01, 0.03, 0.065, and 0.1 mg/kg bw per day for males and 0, 0.01, 0.03, 0.065, and 1 mg/kg bw per day for females, for two years. Groups of 20 rats of each sex per dose were sacrificed at six and 12 months of treatment. At these times, treatment-related effects were seen in the liver and kidney at doses > 0.065 mg/kg bw. The only change in clinical chemical parameters was a slight increase in serum alanine aminotransferase activity in males fed the two highest doses and sacrificed after one year. Increased liver weights were observed at doses > 0.065 mg/kg bw at both interim sacrifices. After six months, slightly increased relative liver weights were found in females at 0.065 mg/kg bw and in males at 0.1 mg/kg bw, whereas females at the highest dose had increased absolute and relative liver weights. At the one-year interim sacrifice, females at this dose had increased relative liver weights. At both interim sacrifices, the livers of males and females at the highest dose showed an increase in hepatocyte size and eosinophilic staining of the cytoplasm in the centrilobular region. Changes in the kidney consisted of slight dark discolouration of the renal cortex in animals at the highest dose at both interim sacrifices and at doses > 0.065 mg/kg bw after one year. The discolouration appeared to be due to an increased quantity of pigment granules in the proximal convoluted tubules, which stained for iron and in the periodic acid-Schiff reaction (Tollett et al., 1983). At the time of terminal sacrifice, no effects had been seen on mortality, body weight, food consumption, organ weights (including liver weights), or the results of haematological and clinical chemical tests, urinalysis, or histopathology, so that the alterations seen at interim sacrifice were not confirmed. Histopathological changes in the kidney included an increased quantity of renal pigment in the proximal convoluted tubules of females at the high dose, accompanied by a slight decrease in kidney weights. The pigmentation was similar to that found at the interim sacrifices. A single male at 0.1 mg/kg bw and two females at 1 mg/kg bw had focal accumulation of hepatocytes of normal appearance in the pancreas. Although the biological significance of these findings is questionable, this alteration has been identified as a treatment-related effect in rats (Reddy et al., 1984). There was no increase in the incidence of neoplasia. The NOAEL was 0.065 mg/kg bw per day, based on transient changes in liver weights and histopathological alterations in the liver and kidney at higher doses (Yano et al., 1984). (d) Reproductive toxicity Rats Groups of 30 male and 30 female Fischer 344 rats were maintained on diets providing haloxyfop (acid) (purity, 99.6%) at doses of 0, 0.005, 0.05, or 1 mg/kg bw per day over three generations. The F0 animals were maintained on the test diet for 102 days and were then mated to produce the F1a and F1b litters. The F1 rats were maintained on the test diet for 137 days and then mated to produce the F2a, F2b, and F2c litters. The F2 generation was fed the diet for 64 days before being mated to produce the F3a and F3b generations. The F2c rats were maintained on the test diet for 61 days and were then cross-mated with untreated stock males and females to further investigate the reduced fertility observed in previous matings. Treatment had no influence on the behaviour, appearance, or mortality of the animals. In some generations, the dose of 1 mg/kg bw resulted in reduced body weights in comparison with controls during various periods: the body weights of pups in the F1b litters were reduced, and the body weights of F1 adults, particularly females (chosen from F1b litters), were slightly lower throughout the pre-breeding period; reduced mean body weights were also observed tor F2a pups throughout lactation and for F2b adults of each sex during treatment. Males at 0.05 mg/kg bw also had lowered mean body weights towards the end of treatment. The reduced body-weight gain was usually accompanied by reduced food consumption. Fertility (the number of pregnant females in relation to the number of females mated) was reduced in treated F1 adults producing the F2b and F2c litters in comparison with the controls, but no clear dose-response relationship was observed and the fertility indices in the controls varied markedly (by 53-90%.) The lowest fertility index was 40% in the F1 adults producing the F2b litter, which is lower than the range in the controls. In the absence of a dose-response relationship and of a consistent pattern over the generations, these effects may not be related to treatment. To further investigate this question, rats of the F2c generation were cross-mated with untreated males and females. No effect on fertility was seen, as the fertility indices were 80-93%. Microphthalmia and/or anophthalmia were observed in control and treated animals. The incidence in the controls was 0-1%. The highest incidences occurred in F2a pups, with 0.6% in controls, 2% at 0.005 mg/kg bw, 1.4% at 0.05 mg/kg bw, and 1.4% at 1 mg/kg bw. As there was no dose-response relationship and no consistent pattern over the generations, the increased incidences are not considered to be related to treatment. The range of incidence of this lesion in fetuses of historical controls was reported to be 0-4%. Liver weights (absolute and/or relative) were increased and kidney weights decreased in most generations at the highest dose, particularly in adults. Histopathological examination of F1b weanlings revealed no treatment-related alterations. F1 adult males at the highest dose had enlarged hepatocytes, often with altered tinctorial properties. The convoluted tubules of animals at the highest dose had increased pigmentation, suggested to be due to a form of lipofuscin (Tollett et al., 1983). No gross or histopathological changes were found in reproductive organs that would explain the reduced fertility observed in F1 adults. The NOAEL for reproductive toxicity was 1 mg/kg bw per day, based on reduced fertility indices in some instances. The NOAEL for body-weight gain depression was 0.05 mg/kg bw per day, based on reduced body-weight gain in the F2b generation (Jeffries et al., 1985). Groups of 30 male and 30 female Sprague-Dawley rats were maintained on diets providing haloxyfop (acid) (purity, 99.4%) at doses of 0, 0.01, 0.065, or 1 mg/kg bw per day for eight (F0 generation) or 11 weeks (F1 generation). The F0 males and females were mated twice to produce the F1a and F1b litters and F1 males and females to produce the F2a and F2b litters. Feeding of the two highest doses resulted in a dose-related reduction in the body weight and body-weight gain in 14- and 21-day-old F1a and F1b neonates; the differences in the F1b litters were statistically significant, whereas a significant reduction was observed in the F1b litters only at the highest dose. The reduction in pup weight may be explained by the slightly larger F1a litters at 0.065 mg/kg bw. The weights of F2a neonates at 21 days were also decreased after treatment at the highest dose. Neither food consumption nor reproductive parameters were affected by treatment. Gross pathological examination of F0 and F1 adults revealed enlarged livers in some F0 males and females at the highest dose. The NOAEL was 0.065 mg/kg bw per day, based on neonatal body-weight changes at 1 mg/kg bw per day (Nitschke et al., 1985). (e) Developmental toxicity Rats Groups of 30 female Fischer 344 rats received 0, 0.1, 1.0, or 7.5 mg/kg bw per day haloxyfop (sodium salt) by gavage on days 6-15 of gestation. Maternal toxicity, evidenced by slightly reduced body-weight gain and reduced food consumption, was seen in animals at the highest dose early in gestation (days 6-8). The incidence of malformations was not increased. Variations included a significant increase in the incidence of delayed ossification in vertebrae (thoracic centra) and a slight increase in the incidence of unfused thoracic centra at the highest dose. The delay in skeletal development may indicate an embryotoxic effect, probably consequent to maternal toxicity. The NOAEL was 1 mg/kg bw per day, based on maternal and embryotoxicity at the higher dose (Hayes et al., 1983). Groups of female Wistar rats were fed diets containing haloxyfop ethoxy ethyl ester (purity, 98.2%) by gavage at doses of 0, 5, 10, or 50 mg/kg bw per day on days 6-16 of gestation No signs of maternal toxicity were observed. The two higher doses resulted in an increased number of resorptions and fewer live fetuses per litter; vaginal haemorrhage was also observed at these doses. Mean fetal weight was reduced at the highest dose. Examination of external and soft tissues revealed a dose-dependent increase in the incidence of cachectic fetuses and an increased incidence of ureterohydronephrosis in all treated groups. The effects at the lowest dose were less pronounced and sometimes not significantly different from the control. Retardation of ossification was observed at the two higher doses (Machera, 1993). Rabbits Groups of 30 female New Zealand white rabbits received 0, 1.0, 7.5, or 20 mg/kg bw per day haloxyfop (sodium salt) by gavage on days 6-18 of gestation. Five animals at the high dose, one animal at the intermediate dose, and one animal at the low dose died. No other effects on general appearance or body-weight development were observed that indicated maternal toxicity. At the highest dose, there was an increased incidence of resorptions. Some fetal alterations were more frequent in treated than in control groups. The incidences of severe forelimb flexure were 1% at the intermediate dose, 2% at the high dose, and 0% in controls; the incidence of forelimb flexure in historical controls was reported to be 3%. Microphthalmia was not observed in any control fetus, but occurred at incidences of 0.5% at the intermediate dose and 1% at the high dose; this lesion was not found in historical controls in the 10 studies considered. A significant increase in the incidence of crooked hyoid bone (considered to be a minor skeletal variant) was observed at the highest dose. The absence of major external malformations in the concurrent control group is unusual in view of the means of about 4% of fetuses (range, 1-7%) and 21% of litters (range, 7-42%) reported in historical controls. The incidences of total major malformations in this study were reported to be 0, 17, 16 and 24% of litters at 0, 1, 7.5, and 20 mg/kg bw, respectively, in good agreement with the mean value of 20% (Hayes et al., 1983). A further study was conducted to determine whether the small increase in the incidence of malformations-in particular microphthalmia-observed in the previous study could be confirmed. Groups of 25-30 female rabbits received haloxyfop (sodium salt) (purity, 99.6%) by gavage at doses of 0, 3.0. 7.5, or 15 mg/kg bw per day on days 6-18 of gestation. Four dams at the highest dose died: two died due to an intubation error, and two others were found dead on days 25 and 28 of gestation having shown no previous signs of toxicity. No other signs of maternal toxicity were observed, and no treatment-related signs of embryo- or fetotoxicity were noted. The incidences of malformations were 2, 3, 2, and 2% of fetuses at 0, 3.0, 7.5, and 15 mg/kg bw group, respectively; the mean percentage of major malformations in historical controls was 4% of fetuses (range, 1-7%). The malformations were mainly skeletal changes, such as fused and forked ribs, and vertebral and soft tissue changes, such as single hydrocephalus or coarctation of the pulmonary artery. No microphthalmia was observed (Hanley et al., 1985). The NOAEL in these two studies was 7.5 mg/kg bw per day with respect to maternal toxicity and 15 mg/kg bw per day for embryo- and fetotoxicity. (f) Genotoxicity The results of studies of the genotoxicity of haloxyfop are shown in Table 2. (g) Special studies (i) Dermal and ocular irritation and dermal sensitization Studies on the irritating and sensitizing potential of haloxfop and its esters are summarized in Table 3. Table 2. Results of tests for the genotoxicity of haloxyfop and its R enantiomer End-point Test system Concentration Purity Results Reference or dose (%) Haloxyfop (acid) In vitro Reverse mutation S. typhimurium TA98, 2-2000 mg/platea 99 Negative Domoradzki (1981) TA100, TA1535, TA1537, TA1538 Forward mutation, Chinese hamster ovary 25-2000 mg/mlb NR Negative Myhr (1982) hprt locus cells Chromosomal aberration Human lymphocytes 100-1000 mg/mla 99.4 Negative Bootman et al. (1986) Unscheduled DNA Rat hepatocytes 0.3 × 10-9-0.3 × 99 Negative Domoradzki (1980) 10-3 mol/litre In vivo Micronucleus formation Rat bone marrow Single oral dose of 99.6 Negative Bhaskar Gollapudi et al. 0, 30, 100, or 300 (1982) mg/kg bw R-Enantiomer Reverse mutation S. typhimurium TA98, 5-1580 mg/plate 99.4 Negative Bhaskar Gollapudi & TA100, TA1535, TA1537 Samson (1989) Table 2. (cont'd). End-point Test system Concentration Purity Results Reference or dose (%) Chromosomal aberration Rat lymphocytes 50-500 mg/mlc 99.4 Negativee Bhaskar Gollapudi & 166.7 - 1667 mg/mld Linscombe (1989) Unscheduled DNA Rat hepatocytes 5-500 mg/ml 99.4 Negative McClintock & Bhaskar Gollapudi (1989) NR, not reported a Toxic at highest doses b Sharp increase in toxicity at 600-2000 mg/ml c With metabolic activation: no mitotic activity at doses > 1667 mg/ml d Without metabolic activation; no mitotic activity at 5000 mg/ml e Positive response at 1667 mg/ml not confirmed in an experiment conducted at concentrations of 750-1667 mg/ml (ii) Peroxisome proliferation Haloxyfop (acid) (purity, > 99%) was administered in the food to groups of 21-25 Fischer 344 rats and B6C3F1 mice of each sex at doses of 0, 0.1, 0.5, 1.0, or 10 mg/kg bw per day for a four-week challenge period. At the end of the challenge period, three animals of each sex were examined by electron microscopy and eight of each sex in anenzyme assay; the remainder were kept on normal diet for a study of recovery. In the enzyme assays, the activities of hepatic peroxisomal enzymes were determined in vitro, including those involved in the ß oxidation of fatty acids, hepatic carnitine acetyltransferase, glycerophosphate dehydrogenase, and catalase. The treatment had no effect on behaviour or general condition in either species. Body weight and food consumption were reduced in male rats at 10 mg/kg bw, and a dose-related increase in the liver weights of rats of each sex was observed at this dose and also in males at 1 mg/kg bw; in females, only the relative liver weights were increased at 10 mg/kg bw. In mice, marked liver weight increases were seen at 10 mg/kg bw in animals of each sex, and the protein content of livers of mice at the high dose was increased. Microscopic changes were observed in the livers of rats and mice at 0.5, 1.0, or 10 mg/kg bw, consisting of hepatocellular enlargement and/or alteration in cytoplasmic staining (increased eosinophilia). These changes affected the entire hepatic lobule in male rats at 10 mg/kg bw, whereas in the other groups the changes were found only in the centrilobular region. The microscopic changes in mice of each sex were similar to those in male rats. A few rats and mice at 10 mg/kg bw also showed a slight increase in the presence of mitotic figures and necrosis of individual hepatocytes. Quantitative evaluation of electron micrographs of hepatocytes from mice and rats showed increased peroxisome volume densities in animals of each sex at 10 mg/kg bw, which were 12 times higher than in controls in male rats, eight times higher in male mice, three times higher in female rats, and 14 times higher in female mice. Less pronounced increases were also found at 1.0 mg/kg bw in male mice and male and female rats and at 0.5 mg/kg bw in male rats. Other changes seen in hepatocytes from rats at the high dose included irregular peroxisomal shape and the occurrence of filamentous nucleoids. Various increases were observed in the activities of the enzymes related to peroxisomal fatty acid catabolism. Palmitoyl-CoA was used as the substrate in the assay for fatty acid ß-oxidase. The specific activity of this enzyme, which generates a major portion of peroxisomal hydrogen peroxide in vitro, was induced in mice and rats of each sex at 10 mg/kg bw. The degree of induction in male rats was greater (393% of controls) than that in females (109% of controls). Dose-related increases in fatty acid ß-oxidase activity were also seen in male rats at 0.5 and 1 mg/kg bw, attaining activities corresponding to 160 and 294% of that of controls, respectively. In mice, induction of fatty acid ß-oxidase resulted in activities of 337% in male and Table 3. Dermal and ocular irritation and sensitization due to haloxyfop (acid) and its methyl and ethoxy ethyl esters Test materiala Species Sex Route Result Purity (%) Reference Haloxyfop (acid) Rabbit Male, female Skin No irritation NR Carreon et al. (1980) Eye Irritationa Haloxyfop EE Rabbit Female Skin No irritation 95 Carreon et al. (1982) Male, female Eye Irritationb Haloxyfop EE Rabbitf Female Skin No irritation 94.7 Jones (1982c) Haloxyfop EE Rabbit Female Skin Irritation 98.8 Jones (1982d) Haloxyfop ME Rabbit Male, female Skin No irritation 98.6 Mizell (1989a) Haloxyfop ME Rabbit Male, female Eye Irritationc 98.6 Mizell (1989b) Haloxyfop EE Guinea-pig Male, female Various No sensitization 95 Carreon et al. (1982); (up to 100% Jones (1982e, 1983c) concentration) Haloxyfop ME Guinea-pig Male Bühler test No sensitization 98.6 Mizell (1989c) (modified) (up to 100% concentration) Table 3. (cont'd). Test materiala Species Sex Route Result Purity (%) Reference Haloxyfop ME Guinea-pig NR Magnusson/ No sensitization Technical Jones (1994) Kligman (up to 100% maximization concentration) test NR, not reported; EE, ethoxy ethyl; ME, methoxy ethyl a In unwashed eyes, conjunctival redness, swelling, discharge, reddening of the iris, and opacity covering up to 100% of the cornea in most animals; effects lasting < 21 days. In washed eyes, similar signs but reversible by 10 days after exposure. b In unwashed eyes, conjunctival redness and swelling, discharge, and transient reddening of the iris in single animals; all signs disappeared within three days after exposure. c Conjuctival redness and discharge; effects reversible within 24 h after treatment; all eyes unwashed 257% in female mice at 10 mg/kg bw in comparison with controls, whereas at lower doses no induction was observed. The specific activity of catalase, the peroxisomal enzyme responsible for the destruction of hydrogen peroxide, was induced in both rats and mice but to a lesser extent. Catalase activity, measured as the hydrolysis of hydrogen peroxide substrate, was 145% and 174% of the control activity in male rats ingesting 1 and 10 mg/kg bw, respectively, whereas in females at 10 mg/kg bw the catalase activity was only 134% of controls. In mice at 10 mg/kg bw, catalase activity was about 206% of the control value in animals of each sex. An increase in the capacity to transfer fatty acid ß-oxidase-generated acyl-coenzyme A groups out of the peroxisomes into mitochondria was indicated by increases in hepatic carnitine acetyltransferase activities. These dose-related increases in male rats at 0.5, 1.0, and 10 mg/kg bw resulted in values 2-22-fold higher than those of the controls. In females, only a fourfold increase was found at the high dose. The hepatic carnitine acetyltransferase activity in mice of each sex at 1 and 10 mg/kg bw was increased by about two- and 14-fold in comparison with controls, respectively. At 0.5 mg/kg bw, the activity was slightly increased in female mice only. Weak increases in glycerophosphate dehydrogenase activity were observed at 10 mg/kg bw in male rats and in mice of each sex, attaining statistical significance only in male rats at the high dose (Stott et al., 1985a). The NOAEL was 0.1 mg/kg bw per day with respect to changes in biochemical parameters and histological changes in the liver indicative of peroxisomal proliferation. In a subsequent study, the reversibility of the effects observed in the previous study was determined after a two- to four-week recovery period. After the two-week recovery, male rats and mice of each sex at the high dose had increased liver weights, altered hepatic morphology (enlarged hepatocytes, altered tinctorial properties), and elevated fatty acid ß-oxidase, hepatic carnitine acetyltransferase, and glycerophosphate dehydrogenase (male rats) activities. The magnitude of these changes was, however, lower than at the end of treatment. The liver weights of male rats at the high dose were still greater than those of the controls after either recovery period. In mice, the liver weights were still increased after two weeks' recovery in males and females at 10 mg/kg bw and in females at 1 mg/kg bw. The histopathological changes were similar to those found immediately after treatment, consisting of increased hepatocyte size and/or alterations in hepatocellular cytoplasmic staining in some groups. Microscopic changes were found in male rats at 1 and 10 mg/kg bw after two weeks' recovery, whereas only males treated with 10 mg/kg bw still had slight changes after four weeks' recovery. A similar pattern of reversibility was found in mice, in which the histopathological changes were present after two weeks' recovery in males and females at 10 mg/kg bw; none were seen after the four-week recovery period. The activities of fatty acid ß-oxidase, hepatic carnitine acetyltrans- ferase, and catalase were also reversed; however, the activity of fatty acid ß-oxidase was still elevated in male rats at the high dose (168% of control) after the four-week recovery period. The increased liver protein concentrations observed in mice after treatment were not seen after two weeks' recovery. No data are available on the reversibility of these effects after long-term exposure (Stott et al., 1985b). Haloxyfop (acid) (purity, 99.6%) as the sodium salt was given to groups of two male cynomolgus monkeys by nasogastric intubation at doses of 0, 5, or 20 mg/kg bw for four weeks. Two additional monkeys were given 20 mg/kg bw per day over four weeks and then maintained on normal diet for at least four weeks. There was no apparent effect on the behaviour, general appearance, activity, body weight, food consumption, or haematological parameters. A reduction in serum cholesterol concentrations was observed at the high dose but the values had returned to normal by the end of the four-week recovery period. There were no changes in organ weights and no histopatho- logical alterations. Electron microscopy of the livers of the controls and animals at the high dose revealed no treatment-related differences in the peroxisomes or other intracellular components of the liver in the treated monkeys (Gerbig et al., 1985). In a study of possible species differences in sensitivity to hepatic peroxisomal induction by haloxyfop, the results of studies in which peroxisomal induction had been investigated in rats, mice, dogs, and monkeys were reviewed, and liver weights, light microscopy findings in liver, hepatic peroxisomal volume density, and serum cholesterol levels were compared (Barnard et al., 1986). Samples of liver were collected for electron microscopy from three dogs of each sex per group in the 12-month dietary study in beagle dogs at doses of 0, 0.05, 0.5, and 5 mg/kg bw per day for 12 months (Barna-Lloyd et al., 1984; see short-term studies); and from two male monkeys at each dose in the four-week study at oral doses of 0, 5, and 20 mg/kg bw per day (Gerbig et al., 1985, see short-term studies). Electron microscopic and morphometric point-counting techniques were used to quantify peroxisomal volume density, and the results were expressed as percent of hepatocellular cytoplasm occupied by peroxisomes. Examination of liver sections from controls, from dogs at 5 mg/kg bw, and from monkeys at 20 mg/kg bw showed that haloxyfop at these doses had no effect. The results of these studies are in good agreement with the lack of organ weight changes and histopathological alterations and indicate that the livers of dogs and monkeys are less sensitive than those of mice and rats to the inducing effects of haloxyfop. (iii) Stereochemical inversion Groups of four Fischer 344 rats of each sex were given an oral dose of 11 mg/kg bw 14C-haloxyfop (racemic material), and urine and faecal samples were collected at 24-h intervals for 10 days. The elimination half-life in female rats was estimated to be about 16.3 h, and most of the dose that was excreted in the urine was present as the parent compound; > 98% of the haloxyfop present in the urine and faeces of female rats corresponded to the R-enantiomer. In male rats, the elimination half-life was about 70 h, and most of the dose was excreted in faeces. Again, most of the excreted haloxyfop in urinary and faecal samples was the R-enantiomer. Thus, stereochemical inversion is rapid and nearly complete in the rat (Bartels & Smith 1988, 1989). Comments After oral administration of the racemic mixture to rats, 98% of the parent compound was in the form of the R-isomer, indicating rapid conversion of the S-enantiomer in vivo. Various studies on the fate of haloxyfop (acid) and its esters have been conducted in mice, rats, dogs, monkeys, and humans. Haloxyfop is rapidly absorbed and eliminated primarily as the unchanged parent compound after oral administration. A marked sex difference in the excretion pattern was noted in rats, the principal route of excretion being the faeces in males and the urine in females. The major route of elimination was also faecal in mice and dogs (only males studied), whereas in monkeys (only males studied) the main elimination route was the urine. The plasma elimination half-lives were lowest in female rats (one day) and longest in male rats (six days). Comparative pharmacokinetic investigations with haloxyfop (acid) and its esters in rats showed very similar patterns of absorption and excretion. The esters were rapidly converted to the parent acid. Pharmacokinetic studies in man after oral administration revealed rapid absorption. The plasma elimination half-life was about six days. Urine was the main excretory route; dermal absorption was estimated to be about 3% of an applied dose. After a single oral dose to rats, haloxyfop and its esters showed similar, moderate toxicity. The LD50 was about 300 mg/kg bw for the acid and its methyl ester and about 500 mg/kg bw for the ethoxyethyl ester. The WHO has classified haloxyfop as 'moderately hazardous'. Two short-term studies were conducted in mice. In one study, the diet provided doses of 0, 0.002, 0.02, 0.2, or 2 mg/kg bw haloxyfop per day over 13 weeks; in the other study, the doses were 0, 0.02, or 2 mg/kg bw per day over 36 weeks. At 2 mg/kg bw per day in both studies, effects in the liver consisted of increases in serum alkaline phosphatase activity (in males), increased liver weights, hepatocellular enlargement, and increased eosinophilia. In addition, in the 36-week study, the kidneys of high-dose males showed a decrease in cytoplasmic vacuolation. The NOAELs were 0.2 mg/kg bw per day in the 13-week study and 0.02 mg/kg in the 36-week study. Two short-term dietary studies were conducted in rats. In the 16- and 37-week studies, the doses were 0, 0.002, 0.02, 0.2, or 2 mg/kg bw per day and 0, 0.02, or 2 mg/kg bw per day, respectively. At 2 mg/kg bw per day in both studies, changes including an increase in serum alkaline phosphatase activity, liver enlargement, an increase in liver weight, a slight decrease in testicular weights, and histopathological changes in the liver (hepatocellular enlargement and increased cytoplasmic homogeneity) were observed. In male rats, treatment- related effects on the liver were observed at 0.2 mg/kg bw per day in the 16-week study. The NOAEL was therefore 0.02 mg/kg bw per day in both studies. In a 13-week study in dogs, doses of 0, 2, 5, or 20 mg/kg bw per day haloxyfop were given in the diet. At 5 mg/kg bw per day and above, changes in biochemical parameters (reduced thyroid hormone levels, decreased cholesterol concentration), decreased thyroid and parathyroid weights, and histopathological changes in the liver (hepatocellular enlargement) and thyroid gland (decrease in follicular size, hypertrophy of follicular epithelial cells) were observed. At 20 mg/kg bw per day, decreased body-weight gain, reductions in various haematological parameters and increases in liver and kidney weights were found. The NOAEL was 2 mg/kg bw per day. In a 12-month dietary study in dogs at doses of 0, 0.05, 0.5, or 5 mg/kg bw haloxyfop per day, a decrease in the serum cholesterol concentration was found in animals of each sex at 5 mg/kg bw per day. The NOAEL was 0.5 mg/kg bw per day. In a 13-week study in monkeys at doses of 0, 2, 10, or 30 mg/kg bw haloxyfop per day, oral administration of 30 mg/kg bw per day resulted in a decrease in the cholesterol concentration, an increase in liver and kidney weights, a decrease of thyroid weights, hepatocellular hypertrophy, increased content of cytoplasmic lipid, and, in females, a decrease in the size of the thyroid follicles and hypertrophy of the follicular epithelial cells. At 10 mg/kg bw, increased kidney weights and slight hepatocellular enlargement were observed. The NOAEL was 2 mg/kg bw per day. A two-year dietary study of carcinogenicity in mice at doses of 0, 0.03, 0.065, or 0.6 mg/kg bw haloxyfop per day resulted in a dose-dependent increase in the incidence of hepatocellular tumours at 0.065 and 0.6 mg/kg bw per day in animals of each sex. Statistically significant increases in the incidence of adenomas in males and carcinomas in females were observed at 0.6 mg/kg bw per day. Other histopathological effects on the liver, including altered cytoplasmic staining properties of centrilobular hepatocytes and a decrease in cytoplasmic vacuolization, were observed at 0.6 mg/kg bw per day. The NOAEL was 0.03 mg/kg bw per day on the basis of an increased incidence of liver tumours at higher doses. In a two-year study of carcinogenicity, rats were given diets providing doses of 0, 0.01, 0.03, 0.065, or 0.1 mg/kg bw per day for males and 0, 0.001, 0.03, 0.065, or 1 mg/kg bw per day for females. Treatment-related effects on the liver at 0.1 mg/kg bw per day and above included transient organ weight increases, hepatocellular enlargement and increased eosinophilia. There was no evidence of carcinogenic potential. The NOAEL was 0.065 mg/kg bw per day. In a study of developmental toxicity in rats at oral doses of 0, 0.1, 1, or 7.5 mg/kg bw haloxyfop (sodium salt) per day, maternal toxicity was observed at 7.5 mg/kg bw per day, as evidenced by reduced body-weight gain and reduced food consumption. In the fetus, ossification was delayed at 7.5 mg/kg bw per day. No evidence for teratogenicity was observed. The NOAEL for maternal toxicity and embryotoxicity was 1 mg/kg bw per day. In two studies of developmental toxicity in rabbits at doses of 0, 1, 7.5, or 20 mg/kg bw per day and 0, 3, 7.5, or 15 mg/kg bw per day, maternal deaths occurred at 15 mg/kg bw per day and above. Embryotoxicity was seen at 20 mg/kg bw per day, as indicated by an increased incidence of resorptions. The results gave no evidence of teratogenic potential. The NOAEL was 7.5 mg/kg bw per day for maternal toxicity and 15 mg/kg bw per day for embryotoxicity. In a two-generation study, rats were treated with diets providing doses of 0, 0.01, 0.065, or 1 mg/kg bw haloxyfop per day. Reductions in body-weight gains were observed in weanlings of the F1 and F2 generations at 1 mg/kg bw per day. Reproduction was not affected by the treatment. The NOAEL was 1 mg/kg bw per day for reproduction and 0.065 mg/kg bw per day for body-weight changes in neonates. Haloxyfop has been adequately tested for genotoxicity in a range of tests in vivo and in vitro. The Meeting concluded that it is not genotoxic. In order to study the mechanism of hepatocarcinogenesis in mice, several short-term studies were conducted to investigate the effect of haloxyfop on hepatocellular peroxisomes. Peroxisome induction was evidenced by histopathological and electron microscopic changes and increased activities of enzymes involved in the ß-oxidation of fatty acids and of hepatic carnitine acetyltransferase in mice at a dose of 1 mg/kg bw per day and in rats at 0.5 mg/kg bw per day. The increase in liver tumour incidence observed at 0.065 mg/kg bw per day in the long-term study of carcinogenicity in mice indicates that peroxisome proliferation is not an important part of the mechanism by which this non-genotoxic compound is carcinogenic. An ADI of 0-0.0003 mg/kg bw was established on the basis of the NOAEL of 0.03 mg/kg bw per day in the two two-year studies in mice, using a safety factor of 100. Toxicological evaluation Levels that cause no toxic effect Mouse: 0.03 mg/kg bw per day (two-year study of toxicity and carcinogenicity) Rat: 0.065 mg/kg bw per day (two-year study of toxicity and carcinogenicity and study of reproductive toxicity) 1 mg/kg bw per day (maternal, embryo-, and fetotoxicity in study of developmental toxicity) Rabbit: 7.5 mg/kg bw per day (maternal toxicity in study of developmental toxicity) Dog: 0.5 mg/kg bw per day (12-month study of toxicity) Monkey: 2 mg/kg bw per day (13-week study of toxicity) Estimate of acceptable daily intake for humans 0-0.0003 mg/kg bw Toxicological criteria for setting guidance values for dietary and non-dietary exposure to haloxyfop Exposure Route, study type species Result, Remarks Short-term (1- 7 days) Skin, irritation, rabbit Irritating Eye, irritation, rabbit Irritating Skin, sensitization, guinea-pig (Buehler No sensitization and Magnusson/Kligman) Oral, toxicity, rat LD50 = 340-550 mg/kg bw per day Dermal, toxicity, fat, rabbit LD50 > 2000 mg/kg bw per day Medium-term (1-26 weeks) Repeated dietary, one month, dog NOAEL = 5 mg/kg bw per day, reduced body-weight gain, reduced cholesterol and increased liver and kidney weights Repeated dietary, 16 weeks, rat NOAEL = 0.02 mg/kg bw per day, increase in liver weights and histopathological changes in liver Oral, developmental toxicity, rat NOAEL = 1 mg/kg bw per day, reduction in maternal body-weight gain, delayed ossification Dietary, reproductive toxicity rat NOAEL = 0.065 mg/kg bw per day, reduced neonatal body-weight gain Long-term (> oneyear) Repeated dietary, two years, toxicity and NOAEL = 0.03 mg/kg bw per day; carcinogenicity, mouse increased incidence of liver tumours References Ashby, J. et al. (1994) Mechanistically-based human hazard assessment of peroxisome proliferator-induced hepatocarcinogenesis. Hum. Exp. Toxicol., 13, Suppl. 2. Barna-Lloyd, T., Taylor, H.W., Swaim, L.D., Maresh, C.L., McDermott, M.C,. Duke, R.L. & Grandjean, M. (1983a) DOWCO 453 Herbicide: Results of a dog dietary range-finding and palatability probe study. Study-No. TXT: K 131381-(11). Unpublished report prepared by Dow Chemical, Lake Jackson, Texas, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Barna-Lloyd, T., Taylor, H.W., Swaim, L.D., Maresh, C.L., McDermott, M.C. & Grandjean, M. (1983b) 453 Herbicide: Results of a one-month dietary toxicity study in beagle dogs. Study No. TXT: K 131381-(15). Unpublished report prepared by Dow Chemical, Lake Jackson, Texas, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Barna-Lloyd, T., Taylor, H.W., Davis, N.L., Swaim, L.D., Hinze, C.A. & Wilkerson, J.E. (1984) DOWCO 453 Herbicide: Results of a 12-month dietary toxicity study in beagle dogs. Study No. TXT: K 131381-(17). Unpublished Report Prepared by Dow Chemical, Lake Jackson, Texas, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Barna-Lloyd, T., Szabo, J.R. & Davis, N.L.(1989) XRD-535 Herbicide: Subchronic rat dietary toxicity and recovery study. Study No. TXT: DR-0298-5651-001. Unpublished report prepared by Dow Chemical, Lake Jackson, Texas, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Barnard, S.D., Yano, B.L. & Franson, L.E. (1986) Induction of hepatic peroxisome proliferation by haloxyfop-Species sensitivity; dogs and monkeys-Study No. HET K 131381-047. Unpublished report Pprepared by Dow Chemical, Midland, Michigan, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Bartels, M.J. & Smith, F.A. (1988) Haloxyfop: Investigation of stereochemical inversion in the Fischer 344 rat. Study No. HET K 131381-065. Unpublished report prepared by Dow Chemical, Midland, Michigan, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Bartels, M.J. & Smith F.A. (1989) Stereochemical inversion of haloxyfop in the Fischer 344 rat. Drug Metab. Dispos. Biol. Fate Chem., 17, 286-291. Bhaskar Gollapudi, B. & Linscombe, V.A. (1989) Evaluation of XRD-535 in an in vitro chromosomal aberration assay utilizing rat lymphocytes. Study No. TXT: DR-0298-5651-005. Unpublished report prepared by Dow Chemical Lake Jackson Research Center Freeport, Texas, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Bhaskar Gollapudi, B. & Samson, Y. (1989) Evaluation of XRD-535 in the Ames Salmonella mammalian-microsome bacterial mutagenicity assay. Study No. TXT: DR-0298-5651-003. Unpublished report prepared by Dow Chemical Company, Midland, Michigan, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Bhaskar Gollapudi, B., Linscombe, V.A. & Sinha, AK. (1982) Evaluation of DOWCO 453 Herbicide in the rat bone marow micronucleus test. Study No. TXT: K-131381-(2/). Unpublished report prepared by Lake Jackson Research Center, Dow Chemical, Freeport, Texas, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Billington, R. (1995) Haloxyfop; evaluation of mammalian toxicity. Unpublished report prepared by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Bootman, J., Hodson-Walter, G. & Dance, C.A. (1986) In vitro assessment of the clastogenic activity of DOWCO 453 in cultured human lymphocytes. Study No. (6/DCS 006/515; Dow Report No. DET 821). Unpublished report prepared by Life Science Research Ltd, Eye, Suffolk, United Kingdom. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Carreon, R. E., Young, J. T. & New, M.A. (1980) DOWCO 453: Acute toxicological properties. Unpublished report prepared by Dow Chemical, Midland, Michigan, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Carreon, R.E., Quast, J.F. & Wall, J.M. (1982) DOWCO 453 Ethoxy Ethyl Ester: Acute toxicological properties and industrial handling hazards Unpublished report prepared by Dow Chemical, Midland, Michigan, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Dietz, F.K., Quast, J.F., Yano, B.L., Firchart, H.M., Landenberger, B.D., Stott, W.T., Campbell, R.A. & Williams, D.M. (1987) DOWCO 453 Herbicide. 13-Week dietary toxicity study in beagle dogs. Study No K 131381-056. Unpublished report prepared by Dow Chemical, Midland, Michigan, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Domoradzki, J.Y. 1980) The evaluation of DOWCO 453 Herbicide in the rat hepatocyte unscheduled DNA synthesis assay. Study No. HET K 131381-(7). Unpublished report prepared by Dow Chemical, Midland, Michigan, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Domoradzki, J.Y. (1981) Evaluation of DOWCO 453 Herbicide in the Ames Salmonella/mammalian microsome mutagenicity assay. Study No. HET K 131381-(6). Unpublished report prepared by Dow Chemical, Midland, Michigan, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Gerbig, C.G., Barnard, S.D., Molello, J.A., Nolan, R.J., Campbell, R.A., Sorrells, R.M., Starrett, M.G. & Fassnacht, D.M. (1985) Haloxyfop: Liver peroxisome evaluation and metabolism studies following oral treatment of male cynomolgus monkeys. Study No. NBX-664. Unpublished report prepared by Merrell Dow Pharmaceuticals, Indianapolis, Indiana, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Gorzinski, S.J., Tollett, J.T., Johnson, K.A., Schnetz, D.J. & Dittenber, D.A. (1982a) DOWCO 453: Results of 13 and 36-week dietary toxicity studies in B6C3F1 mice. Study No. HET K 131381-(3). Unpublished report prepared by Dow Chemical, Midland, Michigan, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Gorzinski, S.J., Herman, J.R. & Yano, B.L. (1982b) DOWCO 453 purified and technical grade acid: A 4-week dietary probe study in CDF Fischer 344 rats. Study No. HET T2.2-189-(4). Unpublished report prepared by Dow Chemical, Midland, Michigan, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Gorzinski, S.J., Burek, J.D., Keyes, D.G. & Campbell, R.A. (1982c) DOWCO 453: Results of 16 and 37-week dietary toxicity studies in Fischer 344 rats. Study No. HET K 131381-(4). Unpublished report prepared by Dow Chemical, Midland, Michigan, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Hayes, W.C., Hanley, T.R. & Yano, B.L. (1983) DOWCO 453 Sodium Salt: Oral teratology study in rats and rabbits. Study No. HET K 131381-(28). Unpublished report prepared by Dow Chemical, Midland, Michigan, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Hanley, T.K., Yano, B.L., Berdasco, N.M., Kirk, H.D. & Scortichini, B.H. (1985) Haloxyfop: Oral teratology study in rabbits (repeat study). Study No. HET K 131381-(042). Unpublished report prepared by Dow Chemical, Midland, Michigan, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Herman, J.R., Tollett, J.T. & Yano, B. L. (1983a) DOWCO 453 EE Ester: Results of a 4-week dietary probe study in male CDF Fischer 344 rats. Study No. HET DR- 0210-0416-003. Unpublished report prepared by Dow Chemical, Midland, Michigan, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Herman, J.R., Tollett, J.T., Yano, B.L. & Campbell, R.A. (1983b) DOWCO 453: Results of a recovery study in male CDF Fischer 344 rats. Study No. HET K 131381-034. Unpublished report prepared by Dow Chemical, Midland, Michigan, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Jeffries, T.K., Yano, B.L. & Rao, K.S. (1985) DOWCO 453: Three-generation dietary reproduction study in Fischer 344 rats. Study No. HET K 131381-012. Unpublished report prepared by Dow Chemical, Midland, Michigan, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Jones, J.R. (1982a) DOWCO 453 EE Tech Lot NP2: Acute dermal median lethal dose (LD50) in the rat. Report No. 3234-50/135. Unpublished report prepared by Hazleton Laboratories Europe Ltd, North Yorkshire, United Kingdom. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Jones, J.R. (1982b) DOWCO 453 EE Tech Lot OP2: Acute dermal median lethal dose (LD50) in the rat. Report No. 3237-50/127. Unpublished report prepared by Hazleton Laboratories Europe Ltd, North Yorkshire, United Kingdom. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Jones, J.R. (1982c) DOWCO 453 EE Tech Lot NP2: A primary skin irritation and corrosivity study in the rabbit. Report No 3230-50/136. Unpublished report prepared by Hazleton Laboratories Europe Ltd, North Yorkshire, United Kingdom. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Jones, J.R. (1982d) DOWCO 453 EE Tech Lot OP2: A primary skin irritation and corrosivity study in the rabbit. Report No. 3228-50/128. Unpublished report prepared by Hazleton Laboratories Europe Ltd, North Yorkshire, United Kingdom Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom Jones, J.R (1982e) DOWCO 456 EE: Delayed contact hypersensitivity study in the guinea pig. Report No. 2977-50/107. Unpublished report prepared by Hazleton Laboratories Europe Ltd, Harrogate, United Kingdom. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Jones, J.R. (1983a) DOWCO 453 EE Tech Lot NP2: Acute oral toxicity study (LD50) in the rat. Report No. 3263-50/134. Unpublished report prepared by Hazleton Laboratories Europe Ltd, North Yorkshire, United Kingdom. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Jones, J.R. (1983b) DOWCO 453 EE Tech Lot OP2: Acute oral toxicity study (LD50) in the rat. Report No. 3372-50/126. Unpublished report prepared by Hazleton Laboratories Europe Ltd, North Yorkshire, United Kingdom. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Jones, J.R. (1983c) DOWCO 453 EE Tech. Lot NP2: Delayed contact hypersensitivity study in the guinea pig (Buehler test). Report No. 3394-50/143. Unpublished report prepared by Hazelton Laboratories Europe Ltd, Harrogate, United Kingdom. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Jones, J.R. (1994) Haloxyfop-R Methyl Ester Technical: Magnusson/Kligman maximisation study in the guinea pig. Study No 291/52. Unpublished report prepared by Safepharm Laboratories, Derby, United Kingdom. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Jones, J.R., Blackwell, M.P. & Collier, T.A. (1986) DOWCO 453 EE Ester: Acute parenteral (intraperitoneal) toxicity test in the rat. Project No. 44/85. Unpublished report prepared by Safepharm Laboratories, Ltd, Derby, United Kingdom. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Machera, K. (1993) Developmental toxicity of haloxyfop ethoxyethyl ester in the rat. Bull. Environ. Contain. Toxicol., 51, 625-632 McClintock, M.L. & Bhaskar Gollapudi, B. (1989) Evaluation of XRD-535 in the rat hepatocyte unscheduled DNA synthesis (UDS) assay. Study No. TXT: DR-0298-5651-004. Unpublished report prepared by Dow Chemical Lake Jackson Research Center, Freeport, Texas, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Mizell, M.J. (1989a) XRD-535 Methyl Ester: Primary dermal irritation study in New Zealand white rabbits. Study No. DR-0217-5704-001 B Unpublished report prepared by Dow Chemical Company, Midland, Michigan, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Mizell, M.J. (1989b) XRD-535 Methyl Ester: Primary eye irritation study in New Zealand white rabbits. Study No. DR-0217-5704-001C. Unpublished report prepared by Dow Chemical, Midland, Michigan, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Mizell, M.J. (1989c) XRD-535 Methyl Ester: Dermal sensitization potential in the Hartley albino guinea pig. Study No. DR-0217-5704-001 E; M-005152-001E. Unpublished report prepared by Dow Chemical Company, Midland, Michigan, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Mizell, M.J. & Lomax, L.G. (1989a) XRD-535 Methyl Ester: Acute oral toxicity study in Fischer 344 rats. Study No. DR-0217-5704-001A. Unpublished report prepared by Dow Chemical, Midland, Michigan, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Mizell, M.J. & Lomax, L.G. (1989b) XRD-535 Methyl Ester: Acute oral toxicity study in B6C3F1 mice. Study No. DR-0217-5704-001G. Unpublished report prepared by Dow Chemical, Midland, Michigan, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Mizell, M.J., Schuetz, D.J. & Johnson, K.A. (1989a) XRD-535 Methyl Ester: Acute dermal toxicity study in Fischer 344 rats. Study No. DR- 0217-5704-001D. Unpublished report prepared by Dow Chemical, Midland, Michigan, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Mizell, M.J., Eisenbrandt, D.L. & Battjes, J.E. (1989b) XRD-535 Methyl Ester: Acute intraperitoneal toxicity study in Fischer 344 rats. Study No. DR- 0217-5704-001F. Unpublished report prepared by Dow Chemical Company, Midland, Michigan, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Mylar, B.C. (1982) Mutagenicity evaluation of XRD0453 in the CHO HGPRT forward mutation assay. Study No. 20989; Dow Report No. HET K 131381-(21). Unpublished report prepared by Litton Bionetics, Inc., Kensington, Maryland, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Nitschke, K.D., Hayes, W.C., Berdasco, N.M., Yano, B.L. & Rao, K.S. (1985) DOWCO 453) two-generation dietary reproduction study in Sprague-Dawley rats. Study No. HET K 131381-039. Unpublished report prepared by Dow Chemical, Midland, Michigan, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Nolan, R.J., Campbell, J.T., Tollett, J.T. & Saunders, J.H. (1985a) DOWCO 453: Pharmacokinetics in human volunteers following a single oral or dermal dose. Study No. HET K 131381-037. Unpublished report prepared by Dow Chemical, Midland, Michigan, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Nolan, R.J., Campbell, R.A. & Venable, J.R. (1985b) DOWCO 453: Pharmacokinetics of the ethoxy ethyl ester of DOWCO 453 in human volunteers following a single dermal dose. Study No. HET DR-0210-0416-007. Unpublished report prepared by Dow Chemical, Midland, Michigan, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Nolan, R.J., Dryzga, M.D., Yano, B.L. & Bartels, M.J. (1987) Haloxyfop: Pharmacokinetics following oral administration to male beagle dogs. Study No. HET K 131381-061. Unpublished report prepared by Dow Chemical, Midland, Michigan, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Oda, S. (1986) Acute oral toxicity study of DOWCO 453 EE in mice. Study No. B-862. Unpublished report prepared by K Research Center Inc, Tokyo, Japan. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom Reddy, J.K., Rao, M.S., Qureshi, S.A., Reddy, M.K., Scarpelli, D.G. & Lalwani, N.D. (1984) Induction and origin of hepatocytes in rat pancreas. J. Cell Biol., 98, 2082-2090. Smith, F.A., Hermann, E.A., Dryzga, M.D. & Ramsey, J.C (1982) The pharmacokinetics of 14C-DOWCO 453 in Fischer 344 rats. Study No. HET K 131381-(26). Unpublished report prepared by Dow Chemical, Midland, Michigan, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Smith, F.A., Veenstra, G.E., Freshour, N.L. & Hermann, E.A. (1983) DOWCO 453 Ethoxy Ethyl Ester: Pharmacokinetics in Fischer 344 rats following oral administration. Study No. HET DR-0210- 0416-004. Unpublished report prepared by Dow Chemical, Midland, Michigan, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Smith, F.A., Kropscott, B.E. & Kastl, P.E. (1984) The pharmacokinetics of DOWCO 453 in the B6C3F1 mouse. Study No. HET K 131381-036. Unpublished report prepared by Dow Chemical, Midland, Michigan, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Stott, W.T., Yano, B.L., Barnard, D. Williams, D.M., Hannah, M.A., Cieszlak, F.S., Albee, R. & Smith, K. (1985a) The proliferation of hepatocellular peroxisomes in rats and mice ingesting haloxyfop. Study No. HET K 131381-44/K 131381-46. Unpublished report prepared by Dow Chemical, Midland, Michigan, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Stott, W.T., Yano, B.L., Hannah, M.A., Battjes, I.E. & Cieszlak, F.S. (1985b) The proliferation of hepatocellular peroxisomes in rats and mice ingesting haloxyfop: 2- and 4-Week recovery. Study No. HET K 131381-046B. Unpublished report prepared by Dow Chemical, Midland, Michigan, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Swenberg, J.A. (1994) Expert report: on the toxicity mid carcinogenicity of haloxyfop. Unpublished report dated 27 September 1994. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Tollett, J.T., Blogg, C.D., Wade, C.E., Morden, M.C, Schütz, D.J., Dittenberger, D.A., Hermann, E.A & Gorzinski, S.J. (1981) DOWCO 453: Results of a 1-week palatability study and a 2-week probe study in feed in CDF Fischer 344 rats. Study No. HET K-131381-(2). Unpublished report prepared by Dow Chemical, Midland, Michigan, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Tollett, J.T., Yano, B.L., Campbell, R.A. & Herman, J.K. (1983) DOWCO 453 Acid: Results of a 6-month and 1-year interim sacrifice of a 2-year dietary toxicity-oncogenicity study in CDF Fischer 344 rats. Study No. HET K-1313181(18a). Unpublished report prepared by Dow Chemical, Midland, Michigan, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Tollett, J.T., Yano, B.L., Cieszlak, F.S. & Battjes, J.E. (1985) DOWCO 453: Two-year dietary chronic toxicity-oncogenicity study in B6C3F1 mice. Study No. HET K 131381(22). Unpublished report prepared by Dow Chemical, Midland, Michigan, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Yano, B.L., Campbell, R.A. & Tollett, J.T. (1984) DOWCO 453: Two-year chronic toxicity-oncogenicity study in CDF Fischer 344 rats. Study No. HET K 131381(18B). Unpublished report prepared by Dow Chemical, Midland, Michigan, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Yano, B.L., Marler, R.J., Sorrells, R.M., Hannah, M.A., Stott W.T., Landenberger, B.D., Williams, D.M. Weiss, S.K. (1987) Haloxyfop: 13-Week oral toxicity study in cynomolgus monkeys. Study No. 131381-058 (T-1242). Unpublished report prepared by Dow Chemical, Midland, Michigan, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Yackovich, P.R. & Miller, J.H. (1983a) Fate of DOWCO 453 fed to laying hens. Study No. GH-C1635. Unpublished report prepared by Dow Chemical, Midland, Michigan, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Yackovich, P.R. & Miller, J.H. (1983b) The fate of DOWCO 453 fed to lactating goats. Study No. GH-C1624. Unpublished report prepared by Dow Chemical, Midland, Michigan, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Waechter, J.M., Campbell, R.A., Dryzga, M.D. & Ramsey, J.C. (1982) DOWCO 453 Methyl Ester: Pharmacokinetics in Fischer 344 rats following oral administration. Study No. HET K 132986-003. Unpublished report prepared by Dow Chemical, Midland, Michigan, USA. Submitted to WHO by Dow Elanco Europe, Wantage, Oxon, United Kingdom. Appendix: Expert report An additional evaluation of the long-term carcinogenicity was made, including a re-evaluation of the slides from liver tumours, further quantitative data, particularly with respect to historical controls, and the results of numerous statistical analyses (Swenberg, 1994). The conclusions are summarized here. In addition to transient changes in liver weights, the non-neoplastic histopathological changes included altered tinctorial properties in hepatocytes at 0.6 mg/kg bw and an increased incidence of foci of cellular alteration in livers of male mice at 0.03 and 0.6 mg/kg. bw. No increase was found at the intermediate dose of 0.065 mg/kg bw. The incidence at 0.03 and 0.6 mg/kg bw was 24%, in comparison with 14% in the concurrent control group; the range of the incidence of hepatocellular foci in male historical controls is 0-20% (11 studies). Thus, the incidence seen in the carcinogenicity studies slightly exceeded the historical control range. Swenberg concluded that the incidence of liver foci is similar to that of historical controls from the laboratory and that it is not affected by exposure to haloxyfop. The absence of a dose-response relationship supports that conclusion. With respect to neoplastic findings, numerous statistical analyses were conducted, with particular attention to the increases in tumour incidence in comparison with concurrent and historical controls; possible increases in tumour multiplicity and decreases in tumour latency were also considered in the evaluation. Using both the original statistical methods and an improved method for tumours with a high background incidence, the incidence of hepatocellular adenomas and adenomas or carcinomas significantly increased in males at 0.6 mg/kg bw, and a significant increase in the incidence of hepatocellular carcinomas was identified in females. A statistically significant linear trend was identified for the same end-points. When the trend test was conducted excluding the data for the high dose, no significant trend was seen for any type or combination of hepatic tumours. Statistical comparisons with historical control groups from 11 studies were also conducted. Only the incidence of hepatocellular carcinomas in females at 0.6 mg/kg bw was statistically significantly increased when the original statistical methods were used, and there was a trend for this group. When the additional statistical methods were used, no significant increase was seen. Moreover, the incidence of liver rumours (adenomas and carcinomas combined) in the concurrent male controls was found to be unusually low, as 5/11 of the historical control groups had statistically higher incidences. A further statistical analysis included a comparison of the data on liver tumours in each dose group with each of the 11 historical control groups. This analysis showed a significant increase in the incidence of adenomas in males at the high dose in 2/11 comparisons and an increased incidence of adenomas or carcinomas in 3/11. The incidence of adenomas was significantly increased in females at the high dose in 1/11 comparisons, that of carcinomas in 6/11, and that of adenomas or carcinomas in 2/11. Comparisons for males at the low and intermediate doses revealed both increases and decreases, with no consistent pattern. Females at the low dose ha d a significantly increased incidence of carcinomas in 1/11 comparisons. Comparisons for females at the intermediate dose showed a significantly increased incidence of adenomas in 1/11 comparisons and an increased incidence of adenomas or carcinomas in 2/11 comparisons. Swenberg concluded that the data are equivocal with regard to a carcinogenic effect in males at the highest dose, while there appears to be a carcinogenic effect for females at this dose. No carcinogenic response was found at the intermediate dose in this analysis. A small increase in tumour multiplicity was also seen in females at the high dose, with 1.6 tumours per animal, in comparison with 1.0 tumour per animal in the control group. The treatment had no effect on the lifespan of animals bearing hepatic tumours.
See Also: Toxicological Abbreviations