IPRODIONE JMPR 1977 IDENTITY Iprodione is a recommended common name of APTOR and BSI and a proposed ISO Standard Common Name. Chemical name 3-(3,5-dichlorophenyl)-N-isopropyl-2,4-dioxoimidazolidine-1-carboxam ide Chemical abstracts 1-(1-methylethylaminocarbonyl)-3- (3,5-diohlorophenylimidazolidine)-2,4-dione i-isopropylcarbamoyl-3-(3,5-dichlorophenyl)hydantoin Synonyms Glycophene, promidione, 26019 RP, ROP, 500 F., NRR 910, LPA 2043 Rovral (R) Structural formulaOther Information on Identity and Properties a) Composition of the technical product The technical product contains 95% minimum of iprodione. The main impurities are phenyl hydantoins and bis-isopropyl-1,,3\-urea (referred to as 32870 R.P.). b) Physical and chemical properties Physical state: white, odourless, non-hygroscopic crystals. Molecular weight: 330.17 Melting point: 136°C Volatility: not volatile Vapour Pressure: 2 × 10-7mm. Hg at 20°C Solubility at 20°C: g/l water 0.013 ethanol 30 acetonitrile 150 toluene 150 benzene 200 acetone 300 methlyene chloride 500 Formulations Mainly wettable powder 500 g a.i./kg. Also suspension concentrate 500 g a.i./l and emulsifiable concentrate 200 g a.i./l. EVALUATION FOR ACCEPTABLE DAILY INTAKE BIOCHEMICAL ASPECTS Single oral doses of iprodione are rapidly eliminated by rats. Following a single application of an oral dose of 200 mg/kg, 26% of the administered dose was eliminated in the urine and 59% in the faeces within 24 hours after application. The major part of the dose excreted in the faeces is the parent compound, whereas only 3% of the administered dose is eliminated unchanged in the urine. Besides the principal urinary metabolites with a degraded isopropylcarbamoyl group (about 11% of the dose administered), there are metabolites with intact hydroxylated or non-hydroxylated aromatic rings. The isomer of the parent compound accounted for a small proportion of the metabolites. Residues in the principal organs and tissues did not exceed 1.5% of the administered dose in rats sacrificed 4 days after dosage (Laurent and Bays, 1974). In a similar study rats were dosed once with 100 mg/kg. of 14C-aromatic ring-labelled iprodione; 96 hours after administration 62% of the applied dose was eliminated via the urine and 36% via the faeces. About 16% was excreted as the parent compound in the faeces: the remaining radioactivity was mainly in urine in the form of the desisopropylated derivative (about 20% of the dose) and the N-(3,5-diachloro-4-hydroxyphenylbiuret) (approx. 13%). Tissues sampled 4 days after dosage contained about 1% of the administered dose. (Lourer, et al., 1976), Based on the identified metabolites the reactions that seem to occur during biotransformation are mainly hydroxylation, oxidation and desalyklation of the isopropylcarbamoyl group (-N1-CO-NH-CH(CH3)2->N1-CO-NH2->N1-H). TOXICOLOGICAL STUDIES Special studies on teratogenicity Groups of 25-30 rats were orally treated with 0, 100, 200 and 400 mg/kg on Restation days 5 to 15. Females at 400 mg/kg showed reduced fertility, reduced body weight gain and a dose-related reduction of food consumption especially during the treatment period. The number of implantations was also reduced at the highest dose level. There was no indication for an embryonyic or teratogenic effect of the test completed (Coquet, 1973a). Groups of 15-17 New Zealand White rabbits were intubated on gestation days 6-16 inclusive with 0, 100, 200 or 400 mg/kg. Body weight gain, over the period of treatment, was slightly reduced at 100 mg/kg, and a dose-related weight loss occurred at 200 and 400 mg/kg. Food intake was reduced at 200 mg/kg and above. At 400 mg/kg, 9 of 17 females died, and only one of the four remaining pregnant animals carried to term. Foetal loss was increased at 200 mg/kg, and foetal weight was reduced at 200 mg/kg and above. Multiple malformations occurred in 1 of 68 living foetuses at 200 mg/kg. Minor malformations were noted in all groups. Special studies on carcinogenicity See "Long term studies." Special study on reproduction Groups of 10 male and 20 female rats were maintained on a diet containing iprodione at concentrations of 0, 125, 250 and 1000 ppm for the first 5 weeks of each generation and 0, 250, 500 and 2000 ppm for the next 8 weeks of treatment. The diet was fed through three generations. The treatment did not affect the growth rate, food consumption, mortality or fertility of the parental animals. The number of living delivered pups of the females treated with 2000 ppm was slightly reduced and the post-natal growth of the pups was slightly retarded. There was also a tendency for growth reduction at 500 ppm. Autopsy findings and microscopic examination of the major organs performed in rate of the third generation did not reveal abnormalities. (Coquet, 1976) Special study on mutagenicity Groups of 25 male mice were fed 0, 1500 and 6000 ppm iprodione for 49 days. After termination of the feeding period the male mice were paired with 2 untreated females for 6 days, followed by a further 2 females for the 6-12 days post-treatment period. The treatment did not affect body weight, food consumption or fertility of the males. None of the examined parameters gave any indication of a mutagenic effect of iprodione (Hastings et al., 1974). Iprodione showed no mutagenic action in a rec-assay using two strains of Bacillus subtilis, reverse mutation tests with and without liner activation system using E. coli WP2 hcr- and five strains of Salmonella typhimurium TA and host-mediated assay with S. typimurium G 46 in mice (Shirasu et al., 1976). Acute Toxicity TABLE 1. Acute toxicity of iprodione Species Sex Route LD50 References mg/kg Rat M F Oral >2000 Pasquet & Mazuret, 1973 Rat M F Dermal >2500 ibid. Rat M i.p. 2400 Pasquet &. Mazuret, 1974 F i.p. 1200 ibid. Mouse M F Oral approx. 4000 Pasquet A Mazuret, 1973 Dog M F Oral >2000 ibid. Rabbit M F Dermal >1000 ibid. The signs of toxicity were: loss of reflexes, muscular hypotonia, sedation and dyspena. Iprodione did not cause skin or eye-irritation in rabbits. In the anaesthetized dog iprodione administered at a dose of 300 mg/kg by the intraduodenal route did not affect the cardiovascular, respiratory or neurovegetative system (Detaille et al., 1973). TABLE 2. Acute toxicity of a 50% formulation of iprodione Species Sex Route LD50 References mg/kg Rat M F Oral 8000 Davies & Lowe, 1974 M F Dermal >2000 ibid. M F 4 h inhalation 13 mg/l air Pasquet & Mazuret, 1975a M F Oral 4100 ibid. Oral 4900 ibid. M F 4 h inhalation >13/l air Ibid. Rabbit M F Dermal >2000*) ibid. *) atoxic The formulation induced slight irritation in the rabbit eye but had no irritant effect on the intact or abraded skin of rabbits (Pasquet & Mazuret, 1975a). "In the sensitization test with guinea pigs, after 10 applications of 0-3 ml of a 50% iprodione solution, followed 2 weeks later by a challenge application, no evidence of dermal sensitization was observed" (Pasquet & Mazuret, 1975b). Short term studies Rat Groups of 15 male and 15 female caesarian originated, barrier sustained, rats were fed 0, 150, 500 or 1000 ppm iprodione in the diet for 5 months. No effects were observed on mortality, food consumption, haematology (as judged by haemoglobin, haematocrit, erythrocyte count, or total and differential leucocyte count) clinical chemistry (as judged by BSP, SGOT, SGPT or SAP) or urinalysis. Body weight gain was slightly reduced (especially in males) at 500 and 1000 ppm. Absolute (but not relative) heart weight was reduced in males at 500 and 1000 ppm, and absolute kidney weight was reduced at 1000 ppm. In females, absolute liver and kidney weights were significantly reduced at 500 ppm only. Gross and histopathology were normal at all dose levels. In a parallel study, dichlozoline, a structurally related compound, induced cataracts. No such effect was seen with (Ganter et al., 1973a). Dog Groups of 2 male and 2 female dogs were maintained on a diet containing iprodione at dose levels of 0, 800, 2400 and 7200 ppm for a period of 3 months. At the top dose level the method of administration was altered after 6 weeks, to gelatine capsules. The treatment did not affect mortality. The recorded values of haematological determinations and urinalyses were within normal limits. As judged by haemoglobin, haematocrit, reticulocyte erythrocyte count, total and differential leucocyte count and prothrombine time except for signs of mild anemia in 1 male and 1 female at 2 months and 1 male at 3 months at the top dose level. At 7200 ppm a reduction of food consumption was observed, accompanied by reduced body weight gain. The opththalmosopic examination of the animals did not reveal any pathological alteration (Canter and Girard, 1973b). The clinical chemistry determinations consisted of glucose, urea, cholesterol, bilirubiu, total proteins, protein electrophoresis, alkaline phosphatase, SGOT, SGPT, LDH, Na+, C, K+, Cl -, Ca++, P. At 2400 and 7200 ppm a slight increase of SLP was observed, also a transient increase of SGOT and SGPT after 1 and 2 months of treatment at 7200 ppm. In treated male rats a dose-dependent increase of relative liver weights was observed, in females at the dose levels of 2400 ppm and above. At 7200 ppm reduced relative weight of testes was found, but no histological indication of damage. The histopathological findings did not reveal any indication of treatment-related alterations of tissues (Coquet, 1973c). Long term studies Mouse Groups of 60 male and 60 female mice were maintained an a diet containing the test compound at 0, 200, 500 and 1250 PPM for 18 months. No treatment-related effect on body weight, food consumption or mortality was found. The recorded values of the haematological blood chemistry and urinalyses tests performed after 6, 12 and 18 months of the feeding period, were within the physiological range. Necropsy findings on mice that died during the last 6 months of the test and on those sacrificed at the termination date showed an increased number of enlarged lymph nodes in males at 200 ppm. Organ weight variations occurred sporadically in the various dose groups and are considered not to be treatment-related. The histopathological findings failed to reveal abnormal features. The distribution of neoplastic and non-neoplastic findings did not appear to demonstrate any significant dose-dependence. The most common tumours were lymphosarcoma involving the spleen, lymph nodes and thymus (Hastings and Hullman, 1975). Rat Groups of 60 male and 60 female rats were maintained on a diet containing 0, 125, 250 and 1000 ppm for 24 months. Slight reduction in body weight gain was observed at 1000 ppm. This was accompanied by some reduction in food intake. The treatment had no effect on food consumption, mortality or values of the hematologic, blood chemistry and urinalyses determinations. Necropsy findings did not reveal any drug-related gross alteration. Variations in organ weight did not show a group distribution and seemed not to be related to drug administration. Histopathology did not indicate a treatment relationship of neoplastic and non-neoplastic findings. AT 24 months the most common tumours observed were pituitary adenomas and adenocarcinoma and fibroadenoma of the mammary glands (Hastings et al., 1976). COMMENTS Iprodione is readily absorbed and rapidly excreted mainly as metabolites with intact hydantoin-moiety. The compound was not teratogenic. In a 3-generation study in rats, there was a slight but statistically significant reduction in postnatal growth at 2000 ppm. This effect was only marginal at the lower dose of 500 ppm which is regarded as a no-adverse-effect-level. In a short-term study in dogs no major effect occurred up to 2400 ppm. Likewise long-term studies in mice and rats revealed no effects up to 1250 ppm. No ocular alterations were found in any study. TOXICOLOGICAL EVALUATION Level causing no toxicological effect Mice: 1250 mg/kg in the diet, equivalent to 160 mg/kg bw Rat: 500 mg/kg in the diet, equivalent to 25 mg/kg bw ESTIMATE OF ACCEPTABLE DAILY INTAKE FOR HUMANS 0-0.3 mg/kg bw USE PATTERN Iprodione is used as a fungicide against a range of fungus diseases, including Botrytis in vines, black- and red currants, blackberries, raspberries and vegetables especially lettuce; Botrytis alii on onions; Rhizocotonia on seed potatoes; seed borne diseases on sugar beets (Phoma spp.) and cereals. It is also used against Botrytis and some other fungus diseases on ornamentals. The compound is used as a foliar spray on several crops, as a post- harvest dip for fruit, for dipping seed-potatoes and as a seed- treatment on sugar beet and cereals. The product is authorized for use on various crops in France, the Federal Republic of Germany, Greece, the Netherlands and the United Kingdom. In several other countries the compound is used or included in testing programmes and it is in course of registration in many countries including Australia, New Zealand, Japan, USA, Canada, Israel, and several European countries. Most of the recommended uses are summarized in Table 3. The information may not be complete since the use of the compound is expanding rapidly and more uses may be expected in the near future. RESIDUES RESULTING FROM SUPERVISED TRIALS Extensive data were obtained from supervised trials carried out in various countries on fruit and vegetables and on some agricultural crops; they are summarized in Tables 4 to 8 and 10. Pome and stone fruits (Tables 4 and 5; Rhône Poulenc, 1977a) Apples The residue at harvest from pre-harvest treatments at normal application rates (about 2.25 kg a.i./ha) is about 2 mg/kg. A combination of such treatments with post-harvest dipping gives rise to residues of about 6 mg/kg. After repeated applications at about twice the normal rate residues ranged from 2.9 - 6.5 mg/kg. The residue of the metabolite RB 30228 (see "Fate of residues") was below 0.15 mg/kg in these experiments. Pears Post-harvest dipping of pears against storage diseases gave rise to residues of 3.6 - 5 mg/kg. Peaches Residues at harvest following applications at the recommended rate varied between 0.9 and 6 mg/kg. A post-harvest dip adds about 4 mg/kg to these levels. Plums Residues arising from recommended applications varied between 0.6 and 6.8 mg/kg, depending on the pre-harvest intervals observed and the local conditions. The drying process increased the residue in the prunes by 0.6 - 1.6 mg/kg. TABLE 3. Use pattern and recommended pre-harvest intervals of iprodione Pre-harvest Crop Disease Application intervals No. of treatments Rate Country Days g a.i./ha Grapes Botrytis 4 750 Austria 28 " 4 750 France. 15 " 4-5 750 Fed. Rep. of 28 Germany " 3 3000 Japan 7 " 4 750 Portugal 15 " 4 750 Spain 15 " 4 750 Switzerland " 4 750 USSR " 4 750 Yugoslavia Strawberries Botrytis 4-5 1000 Belgium 15 3 1000 Fed. Rep. of 7 Germany 3 Japan 1 4-5 1000 The Netherlands 14 Pome and Stone fruit Apples Alternaria about 10 Japan 10 Peaches Monilia 3 Japan 1 Vegetables Chicory (witloof) (forcing) Botrytis 1 3 g/m2 Belgium Throughout Sclerotinia 1 4 g/m2 France the forcing applied on the top of period the roots at forcing TABLE 3. (Continued) Pre-harvest Crop Disease Application intervals No. of treatments Rate Country Days g a.i./ha Cucumbers Botrytis 4 Japan 1 Lettuce Botrytis Scleotinia 3 750 Belgium 10 (glasshouse) " 3-4 750 France " 3 750 Fed. Rep. 21 of Germany (glasshouse) 14 (outdoors) " 4 750 Japan 14 (also for endive) " 1x 1000-2000 The Netherlands 28 " 2xx 750 The Netherlands 28 Vegetables Onions Botrytis Sclerotinia 3 750 Japan 7 cepivorum Tomatoes Botrytis 4 Japan 1 Alternaria United Kingdom Agricultural Crops Beans Sclerotinia 3 Japan 21 Rice Pellicularia 3 Japan 21 TABLE 3. (Continued) Seed and tuber treatments Cereal seed Pre-harvest Crop Disease Application intervals No. of treatments Rate Country Days g a.i./ha Barley Helminthosporium 1 60 g a.i./100 kg seed Wheat Tilletia caries 1 60 g a.i./100 kg seed Garlic Sclerotinia cepivorum 1 300 g a.i./100 France kg seed Potatoes Rhizoctonia solani 1 100-150 g/ France 1000 kg tubers spraying on tubers immediately before storage dipping in spring before planting 400 g/100 l Sugar-beet Phoma spp 1 150 g a.i./kg France. seed enveloped seed x= one application at planting. xx= two applications, the first about a week after planting and a second within two weeks after planting Berry fruits and currents (Table 6; Rhône-Poulenc, 1977b) The residue levels at harvest after treatments at normal rates and observing recommended pre-harvest intervals (10-21 days) were generally at or below 5 mg/kg on blackcurrants, 2 mg/kg on raspberries and 6 mg/kg on strawberries. Grapes The maximum residues of iprodione on grapes at harvest following treatment according to good agricultural practice (about 750 g a.i./ha) were in general not higher than 10 mg/kg. The highest levels in the unfermented must and the win were 4.4 and 6.4 mg/l respectively. Some results are shown in Table 10 (Rhône-Poulenc, 1977c). See "Fate of residues", "In storage and processing". Vegetables (Table 7; Rhône-Poulenc, 1977d) Chicory (witloof) The residues in the edible sprouts after a normal period of forcing and one treatment at the recommended rate did not exceed 1 mg/kg. The residues in the roots were much higher, with a maximum of about 10 mg/kg. The roots are often used as animal feed. Cucumbers Residues on cucumbers treated with 3 kg a.i./ha (twice the normal rate) were between 0.3 and 2.2 mg/kg. Lettuce Residues arising from recommended applications on outdoor lettuce (750 g a.i./ha) varied between 1.7 and 2.5 mg/kg after pro-harvest intervals of 14-21 days. The residues on glasshouse-grown lettuce are in general much higher. Three applications of the recommended dosage gave rise to residues of 6.7 mg/kg after a pre-harvest interval of 39 days, and in other experiments maximum levels of 7.2 mg/kg were found 14 days after the last application. Residue levels of the metabolite RP 30228 were slightly about the limit of determination; other metabolites were below it. (Metabolites are identified in the section "Fate of residues." Onions The residues on onions 1 day after application did not exceed 0.2 mg/kg. TABLE 4. Supervised trials of iprodione. Residues in pome and stone fruit (pre-harvest application) Application Residues (mg/kg) at intervals (days) often application Crop Country Year No Rate Formulation* 0-2 3-6 7-10 13-14 30-35 40 50 g/100 1 kg/ha (20-22) Apples Japan 1975 1 100 5 WP 50% 2.15 1.75 1975 1 100 5 " 2.9 2.25 1975 1 100 5 " 0.38 1975 10 100 5 " 6.5 1975 10 100 5 " (5.75) 1975 10 100 5 " 3.75 1975 10 100 5 " 3.4 1975 10 100 " (1.95) 1975 10 100 5 " 1.7 U.K. 1975 10 100 2.25 " (2.0) Cherries Moss Australia 1975 4 1.4 " 8.0 Peaches Katharine Australia 1976 7 50 1.4 " 5.4 Anne Truly 1976 3 50 0.5 " 1.7 Goldmine 1976 5 50 1.4 " 5.8 Redhaven Canada 1974 4 50 1.0 " 6.5 4.6 4.9 1974 4 50 1.0 " 1.45 Babygold Canada 1974 7 50 1.0 " 2.3 2.0 1.3 1974 6 50 1.0 " 1.8 0.9 Earlired 1974 5 1.0 " 2.5 1.9 2.2 2.2 Redhaven 1974 5 1.0 " 6.1 4.1 3.4 2.9 1.6 Sunhaven 5 1.0 " 7.6 9.0 10.0 8.5 Gifu Japan 1975 7 100 4.0 3.7 2.1 1975 3 100 4.0 " 4.6 2.9 Okayama 1975 2 100 3.0 " 6.3 4.8 1975 3 100 3.0 " 6.8 5.8 TABLE 4. (Continued) Application Residues (mg/kg) at intervals (days) often application Crop Country Year No Rate Formulation* 0-2 3-6 7-10 13-14 30-35 40 50 g/100 1 kg/ha (20-22) Plums October Australia 1976 4 1.4 " 2.2 purple Inra 711 France 1973 4 0.5 SC 0.25 0.26 4 1.0 SC 1.4 0.9 1974 0.5 4.15 3 1.0 6.8 2 0.5 0.2 2 1.0 0.6 * SC = Suspension concentrate WP = Wettable powder TABLE 5. Supervised trials of iprodione. Residues in pome and stone fruit (post-harvest application) Application Rate Crop Country Year No. g a.i./100 Formulation Residues (mg/kg) after storage period of (days) dip 1-2 7 11 85 95 Apples Cox's U.K. 1973 - - 2.0 1 200 5.8 1 200 4.4 Pears Conference U.K. 1973 1 200 SC 5.0 1973 1 200 4.8 1973 1 200 3.6 1973 1 200 4.7 1973 1 200 1973 1 200 4.0 Peaches Australia - WP50% 1.7 1 50 WP50% 5.3 1 50 WP50% 5.0 TABLE 6. Supervised trials of iprodione. Residues in berry fruits and currants Application Residues (mg/kg) at intervals (days) after application Crop Country Year No. Rate Formulation 0-1 3-4 7-10 13-17 18-23 28-30 33-36 g/100 1 kg/ha Raspberries France 1974 3 0.8 WP 50% 1.1 Heyton 0.5 0.85 Malling jewel U.K. 1974 5 1.1 " " 1.55 3 1.1 " " 2.0 4 1.1 " " 7.9 5.0 2.8 2.1 Strawberries Belgium 1974 5 0.75 " " 4.9 Sivetta 5 1.0 " " 6.0 Domunil 5 0.75 " " 1.9 5 1.0 " " 2.5 Redcoat Canada 1974 4 1. " " 3.1 1.8 1.4 0.85 Vista 4 1.1 " " 3.5 2.4 1.4 1.0 Redcoat 4 3.45 2.1 1.6 1.0 Redcoat 3 0.9 0.8 0.2 Red Gauntlet France 1973 4 0.5 " " 0.22 0.75 " " 0.44 1.0 " " 0.66 Immigrante 1974 4 0.75 " " 1.75 4 1.0 " " 2.2 Gorella 1974 4 0.75 " " 0.35 4 1.0 0.44 3 0.75 " " 0.5 3 1.0 " " 1.1 Suprême d'Halles 4 0.5 " " 1.2 4 0.75 " " 1.9 4 1.0 " " 2.75 4 0.5 " " 2.5 4 0.75 " " 3.2 4 1 5.6 Senga Segana Fed. Rep. 1974 3 0.9 " " 5.3 2.7 2.3 1.0 0.4 of Gemany 3 1.25 " " 9.1 3.6 3.4 1.9 0.7 TABLE 6. (Continued) Application Residues (mg/kg) at intervals (days) after application Crop Country Year No. Rate Formulation 0-1 3-4 7-10 13-17 18-23 28-30 33-36 g/100 1 kg/ha Senga Segana Netherlands 1974 4 0.75 " " 1.1 1974 5 0.75 " " 26.4 14.2 0.67 Red Gauntlet Switzerland 1974 1 0.75 " " 1.0 0.86 0.2 0.1 0.1 Wädenswill 1974 3 0.75 " " 0.2 1974 3 0.75 " " 0.15 Royal Sovereign U.K. 1974 4 1.1 " " 1.2 1.6 1.3 Strawberries Cambridge Favourite (g) 1974 4 1.1 WP 50% 8.0 6.9 4.5 4.7 Cambridge Favourite (g) 1974 3 1.1 " " 1.7 Cambridge Favourite 1974 3 1.0 " " 0.7 Cambridge Favourite 1976 3 1.6 1.1 Cambridge Favourite 1976 3 0.75 0.9 0.6 Red Gauntlet 1976 1 0.75 0.6 Red Gauntlet 1976 1 1.0 0.9 Red Gauntlet 1974 3 2.2 1.7 Cambridge Favourite 1974 3 2.2 0.55 Royal Sovereign 1974 2 1.0 0.3 TABLE 6. (Continued) Application Residues (mg/kg) at intervals (days) after application Crop Country Year No. Rate Formulation 0-1 3-4 7-10 13-17 18-23 28-30 33-36 g/100 1 kg/ha Black currants Wellington Tr. UK 1974 4 1.1 WP 50% 3.9 62 days Baldwin UK 1974 4 1.1 " " 4.6 62 days (g) = glasshouse TABLE 7. Supervised trials of iprodione. Residues in vegetables Application Residues (mg/kg) at interval (days) after application Rate Crop Country Year No. 1kg/ha Formulation 0-1 3-4 5-7 10-14 21-22 28-30 31-35 g/100 Bean without pod Japan 1975 1 1 WP 50% 0.05 0.05 0.05 Cucumbers(g) Japan 1975 3 1 0.05 0.05 1975 1 3 WP 50% 1.7 1.0 0.36 1975 3 3 " " 1.6 0.9 0.7 1975 4 3 " " 2.2 1.4 1.2 1975 1 2.5 " " 1.2 1.0 0.24 1975 3 2.5 " " 1.9 1.4 0.3 1975 4 2.5 " " 1.8 1.0 1.0 Lettuce Val.d'Orge France 1974 6 0.5 " " 0.03 6 0.75 " " 0.03 6 1.0 " " 0.03 6 0.5 EC 200g/l <0.02 6 0.75 " " <0.02 6 1.0 " " 0.04 5 0.5 WP 50% 2.5 5 0.75 " " 1.3 Murkönig Fed. Rep. 3 0.75 " " 15.7 1.8 0.6 0.05 0.05 0.05 Kares of Germany 1976 4 0.75 " " 24.5 9.1 1.7 Reskia 1976 3 0.25 " " 2.6 0.8 0.2 3 0.75 " " 13.2 3.0 1.1 Susan 1976 3 0.5 " " 4.6 1.2 0.4 3 0.75 " " 28 4.3 4.2 Murkönig(g) Fed. Rep. 1976 3 0.25 " " 24 6.9 2.9 of Germany 3 0.75 " " 46 10.5 7.2 TABLE 7. (Continued) Application Residues (mg/kg) at interval (days) after application Rate Crop Country Year No. 1kg/ha Formulation 0-1 3-4 5-7 10-14 21-22 28-30 31-35 g/100 Ravel(g) 1976 3 0.25 " " 26 5.4 2.7 0.75 " " 22 4.8 3.6 Kurume Br.(g) Japan 1975 2 3 " " 4.6 0.28 0.05 3 3 " " 10.8 0.27 0.1 4 3 " " 7.4 0.3 0.1 Kumamoto(g) Japan 1975 2 1.5 " " 0.48 1.05 0.4 3 1.5 " " 1.9 0.6 1.2 4 1.5 " " 2.25 0.78 1.7 Déciminor(g) Netherlands 1975 2 0.75 " " 8.2 4.9 Vera(g) 1975 2 0.75 " " 9.15 0.05 0.05 Ostinata(g) UK 1974 4 0.56 " " 19 18 14 (24 days) Val d'Orge 1974 3 0.56 " " 8.8 4 0.56 " " 59 40 41 21 Onions S. Africa 1977 7 50 WP 50% 0.14 0.15 100 " " 0.15 0.24 Sweet Peppers(g) U.K. 1975 6 4.3 TABLE 7. (Continued) Application Residues (mg/kg) at interval (days) after application Rate Crop Country Year No. 1kg/ha Formulation 0-1 3-4 5-7 10-14 21-22 28-30 31-35 g/100 Tomatoes Koibuchi (g) Japan 1975 1 2.5 " " 1.25 1.4 1.2 0.8 Koibuchi (g) 1975 3 2.5 " " 5.3 3.4 3.0 2.4 Koibuchi (g) 1975 4 2.5 " " 5.6 5.4 4.3 3.5 1975 3 3.0 " " 2.1 3.3 1.8 2.9 4 3.0 " " 4.6 3.6 4.1 2.8 5 3.0 " " 4.4 4.0 3.8 3.7 Eurocross(g) U.K. 1974 5 50 " " 2.7 6 50 " " 3.8 7 50 " " 4.9 8 50 " " 4.2 2.3 Sonato(g) U.K. 1974 4 50 " " 1.65 5 50 " " 2.3 6 50 " " 2.8 7 50 " " 3.7 8 50 " " 4.2 5.8 5 50 " " 3.1 2.5 2.7 1 1 " " 0.64 (18 days) TABLE 7. (Continued) Application Residues (mg/kg) at interval (days) after application Rate Crop Country Year No. a.i. Formulation 30-40 40 44-48 59 70 93-104 162 g/m2 S R S R S R S R S R S R S R Chicory Belgium 1975 1 3 " " 0.41 1.49 1 6 " " 0.36 3.10 3 " " 0.09 2.7 6 " " 0.32 4.4 3 " " 0.77 6.2 6 " " 0.59 10.0 3 " " 0.55 2.7 6 1.0 3.7 France 1974 1 4 " " 0.6 8 " " 1.0 0.07 4 " " 0.25 8 " " TABLE 7B Crop Country Year No. Rate Formulation 30-40 40 44-48 59 70 93-104 162 g/100 1g/1000 dip kg S R S R S R S R S R S R S R Potatoes pre-plant France 1976 1 200 WP 50% n.d. treatment 300 " " n.d. 50 " " 0.01 100 " " 0.01 150 " " 0.02 200 " " 3.0 5.0 50 " " 25 25 100 " " 58 67 150 " " 120 140 foliar spray S. Africa 1976 5 50 " " <0.02 5 100 " " <0.02 3 50 " " <0.02 3 100 <0.02 WP = wettable povider; EC = emulsion concentrate; (g) = glasshouse; R = roots (chicory) or tubers (potato); S=sprouts Peppers and tomatoes Following applications at normal rates (50 g a.i./100 l) residues of 4.5 - 5 mg/kg were found at harvest after pre-harvest intervals of 3.6 days. Beans (dry) After treatment at a dosage rate of 1 kg/a.i./ha, residues in the dry beans were very low (0.05 - 0.2 mg/kg). Cereal crops (Table 8; Rhône-Poulenc, 1977e) Wheat Two applications at normal rates (1 kg a.i./ha) with a pre-harvest interval of 73 days did not give rise to measurable residues in the kernels. Rice After treatment during the growing season with relatively high dosages (1.2 kg a.i./ha), residues of 0.1 - 2.1 mg/kg were found de-husked, unpolished rise 21 days after the last treatment. FATE OF RESIDUES In plants The fate of iprodione in plants and soil was studied with unlabelled and 14C-phenyl-labelled products. It was found that when applied to the leaf surface, iprodione does not appreciably penetrate through the skin. The residues on the skin had a half-life of 30-60 days, being slowly converted to 1-(3,5-dichlorophenylcarbamoyl)-3-isopropylhydentoin, RP 30228), which represented up to 35% of the remaining residue. 2-5% of this residue consisted of minor degradation products, including 1-carbamoyl-3-(3.5- dichlorophenyl) hydantoin (RD 32490) (Rhône-Poulenc, 1973). Wheat and strawberry plants grown on soil treated with iprodione (Rhône-Poulenc, 1977f) took up small amounts of the compound (in wheat 0.7-1.3% of the amount applied to the soil surface), which was mainly found in the leaves and stems (95-99% of the extractable residue). Within the plant the parent compound was converted to RP 30228, small amounts of RP 32490 and some more polar unidentified products. The organosoluble residue in strawberry plants 32 days after a foliar application at a rate equivalent to 1 kg a.i./ha consisted of 61% unchanged parent compound and 16% RP 30228. 55 days after foliar treatment at 2 kg a.i./ha 69% of the residue was iprodione, 7% RP 30228 and 5% RP 32490. TABLE 8. Supervised trials of iprodione. Residues in cereal crops. Application Residues (mg/kg) at intervals (days) after application Rate Crop Country Year No. Formulation 14-15 21-22 28-30 73 81 g/100 1 kg/ha Rice Japan 1975 1 100 1.2 WP 50% grain 0.1 0.1 0.1 straw 16 15 10.3 1975 1 100 1.2 WP 50% grain 0.3 0.4 0.3 straw 32 12.5 10.5 3 100 1.2 WP 50% grain 2.1 straw 45 3 100 1.2 WP 50% grain 1.4 straw 32 3 100 1.2 grain 0.8 straw 49 4 100 1.2 1.8 grain 43 straw Wheat Maris Nimrod UK 1 34 1.0 <0.05 2 34 1.0 <0.05 Jos Cumbier 1 34 1.0 <0.05 2 34 1.0 <0.05 TABLE 9. Nature and Distribution of radio-activity in wheat grown in soil treated with 10 kg/ha. 14C-iprodione % of total 14C in each plant part as Unidentified Total 14C Days after Organo- Water expressed as treatment Plant part Iprodione RP 30228 RP 32490 soluble soluble Bound iprodione mg/kg 16 roots 49 14 n.d. 21 0 17 20 leaves and 66 6.4 4.4 21 1.5 1.7 20 stem 44 roots 16 15 n.d. 13 1.1 55 31 leaves and 48 9.5 18 20 0.95 4.2 20 stem 89 roots 2.9 8.1 0.8 9.2 0 79 238 leaves and 26 17 14 32 0.22 11 36.7 stem ears 9.1 3.1 0.1 24 0 56 32 kernels n.d. n. d. n.d. 72 0 28 2.5 Wheat plants were grown on soil treated with excessive dosages of 14C-labelled iprodione and the distribution of the residue in the plant was studied after 16, 44 and 89 days. The nature and distribution of the recovered radio-activity is shown in Table 9 (Rhône-Poulenc, 1977f). The plant and soil metabolites of iprodione have been identified by various methods including TLC, GLC, and colorimetric analysis and the degradation pathway shown in Figure 1 deduced. In soil The degradation of residues in soil follows a similar pattern. The half-life at initial levels of 2 and 5 mg/kg is about 30 days. After 12 months incubation under aerobic conditions at 23-25°C, no more than 3% of the remaining radio-activity was in the form of unchanged iprodione. Conversion to metabolite RP 30228 proceeded rapidly. The concentration of RP 30228 reached a maximum (45-55% of the radio-activity still present) after 80-100 days and then decreased (Rhône-Poulenc, 1976). In leaching experiments with radio-labelled iprodione it was shown that the parent compound was only slightly mobile, remaining in the 0-15 cm layer. The metabolite RP 30228 is less soluble in water than the parent compound (0.5 mg/l compared to 13 mg/l) and virtually all remained in the 0-5 cm layer (Rhône-Poulenc 1973, 1976). In storage and processing Extensive data were obtained from various countries on the fate of residues of iprodione during wine making and on the effect of residues on the fermentation. When grapes containing about 5 mg/kg were used for wine making, no influence on the fermentation process was found. This was confirmed in laboratory experiments in which CO2 evolution and the proportion of viable cells (those susceptible to actidione) were measured. In a trial in which the grapes contained 2-10 mg/kg iprodione, the fermentation process was slightly retarded. It is unlikely that this effect would be observed under practical conditions of wine making. During the wine making, iprodione remains fairly stable, but a considerable part of the residue will be eliminated with the solids (mavc) during clarification. The residues in wine are generally about 15-25% of those in the grapes. No residues of iprodione were found in alcohol obtained after distilling wine (Rhône-Poulenc, 1977c; Barre et al., 1976). Some results are shown in Table 10. TABLE 10. Residues of iprodione at various stages of vinification Iprodione, mg/kg in Country Year Grapes Must Wine Finished Unfermented Fermented Racked Clarified Wine France 1974 4.9 2.7 0.98 0.75 3.0 1.7 1.0 0.71-0.84 1975 6.1 2.75 0.8 7.5 4.4 1.45 1975 2.2 1.5 0.34 5.4 0.6 South 1976 1.0 1.3 0.9 Africa 2.6 0.5 1.5 Switzerland 2.3 1.9 0.7 1973 1.7 1.4 0.5 2.9 1.9 0.4
METHODS OF RESIDUE ANALYSIS Gas-chromatographic methods using electron capture detectors have been developed for the analysis of residues in several fruits and vegetables. These are suitable or can be adapted for regulatory purposes. They have been adapted for residue analysis In must and wine. The limit of determination on most fruits and vegetables is about 0.01-0.02 mg/kg. Some commodities of plant origin, e.g. prunes and mare, require a more elaborate clean-up owing to the higher proportion of interfering plant constituents. The limit of determination in these commodities is about 0.05-0.1 mg/kg. No loss of residues was found during storage for more than 1 year at temperatures of -18°C.(Rhône-Poulenc, 1975a,b). NATIONAL TOLERANCES REPORTED TO THE MEETING The following maximum residue limits were reported to the Meeting as established or under consideration. They refer to iprodione, excluding metabolites. Country Commodity Maximum residue limit, mg/kg Australia Apricots, cherries, plumes peaches 10 France Grapes 10 Fed. Rep. of Germany Grapes 10 The Netherlands Lettuce 5 Strawberries 2 New Zealand Apricots, berry fruits, cherries, grapes, peaches, plums 10 Switzerland Grapes 7 APPRAISAL Iprodione is used against a relatively broad range of fungus diseases, on a wide range of fruits and vegetables. Its use is authorized, or is in course of registration, for various crops in a number of countries. It is marketed in the form of a wettable powder, a suspension concentrate and an emulsifiable concentrate. The products are mainly used as a spray on the aerial parts of growing crops, for post-harvest dipping of fruit as a dip for seed potatoes and as a seed treatment. Application rates vary according to the crop/disease situation and regional conditions. Residue data were obtained from supervised trials carried out in various countries with different climatic conditions. Studies with unlabelled and 14C-phenyl-labelled products showed that iprodione does not appreciably penetrate through the plant cuticle. The residue on the surface of the plants had a half-life of about 30-60 days. It was converted into 1-(3,5-dichlorophenyloarbamoyl)-3-isopropyl-2,4-dioxoimida-zolidine, 1-(3,5-dichlorophenylcarbamoyl)-3-isopropylhydantoin, RP 30228, which represented up to 35% of the remaining residue. 2-5% of this residue consisted of minor degradation products, including 1-carbamoyl-3-(3,5-dichlorophenyl)hyclantoin (RP 32490). Wheat and strawberry plants grown on soil treated with iprodione took up small amounts of the compound (equivalent to 0.7-1.3% of the total applied to the soil surface). Within the plant the parent compound was converted into metabolite RP 30228, Small amounts of RP 32490 and some more polar unidentified products. The degradation of residues in soil follows the same pattern. The half-life at initial levels of 2 and 5 mg/kg is about 30 days. After 12 months incubation under aerobic conditions at 23-25°C no more than 3% of the remaining residue is in the form of unchanged iprodione. The parent compound is only slightly mobile, remaining mainly in the upper 0-15 cm layer. The metabolits RP 30228 is less soluble in water than the parent compound (0.5 mg/l compared to 13 mg/l) and virtually all remained in the 0-5 cm layer. Residues in wine were approximately 15-25% of those on the harvested grapes. Gas-chromatographic methods using electron capture detectors have been developed for the analysis of residues in several fruits and vegetables, must and wine, which are suitable or can be adapted for regulatory purposes. The limit of determination is generally about 0.01-0.02 mg/kg. No loss of residue was found over more than 1 year at -18°C. RECOMMENDATIONS The following maximum residue limits for iprodione on various fruits and vegetables are recommended. They refer to iprodione, excluding any metabolites. Commodity Limit, mg/kg pre-harvest interval on which recommendations are based post-harvest treatment Apples, pears 10 10-14 + Grapes 10 14-21 Lettuce 10 14-21(281) Peaches 10 10-14 + Plums 7 14 Strawberries 7 14 Blackcurrants 5 10-21 Cucumbers 5 3-6 Sweet peppers 5 3-6 Commodity Limit, mg/kg pre-harvest interval on which recommendations are based post-harvest treatment Raspberries 5 10-21 Tomatoes 5 3-7 Rice (hulled, unpolished) 3 21 Chicory (witloof) sprouts 1 throughout forcing Beans, dry 0.2 14-21 Garlic, onions 0.1 1 1 Glasshouse use. FURTHER WORK OR INFORMATION DESIRABLE 1. Information on the fate of iprodione residues in milk, meat and eggs when food wastes containing iprodione residues are used as components of animal feeds. 2. Residue data on grain and straw from supervised trials on cereal crops treated according to good agricultural practice. 3. Further information about the effects of processing and cooking on iprodione residues in a range of commodities. REFERENCES Barre, P., R. Cordonnier, A. Dugal, L. Lacroixy M. Laurent et M. Buys (1976) Etude, dens le raisin et le vin, des résidus d'un fongicide antibotrytis, le 26019 R.P. et leur effects our la fermentation alcoholique. Progrés Agricole et Viticole 93 (11) 2-8. Coquet, B. (1973a) Recherche du pouvoir teratogéne chez le rat OFA par voie orals du produit 26019 R.P. Unpublished report from Centre de Recherche et d'Elevage des Onoins, No. 731016. Coquet, B. (1973b) Recherche du pouvoir teratogéne chez le lapin pax voie orale du produit 26019 R.P. Unpublished report from Centre de Recherches et essais biologiques, Les Onoins, No. 730925. Coquet, B. (1977c) Essai de toxocité chronique (3 mois) chez le chien par voie orals du produit 26019 R.P. Unpublished report from Centre de Recherche et d'Elevage des Onions, No. 731008 Coquet B. (1976) Influence du produit 26019 R.P. sur la reproduction du rat (Essai sur 3 générations). Unpublished report from Institut Franc. de Recherche et Essais Biologique, No. 760435 submitted by Rhône-Poulenc. Davies, V.A. and Lowe C.Y. (1974) Fungicides: Formulation LPA 2043: Acute Oral and Dermal Toxicity in the Rat. Unpublished report from May and Baker Ltd., England, No. RG 2037. Detaille, J.Y., Pasquet, J., Mazuret, A. and Mondot, S. (1973) Antifongique 26019 RJ., Phaxmacologie générale chez le chien anesthésié au pento barbital. Unpublished report des Laboratoires do Recherches de la Société des Usines Chimiques Rhône-Poulenc, subm. by Rhône-Poulenc. Ganter, P., Julou, L., Pascal, S., Pasquet, J., Populaire, P., Delesque, M., LeBail, R. and Myan, J. (1973a) Produit No. 26019 R.P. - Toxicété à terms (5 mois) chez le rat par voie orale, on comparaison avec la dichlozoline (Selex, N.D. Sumitomo = 23319 R.P.). Unpublished report from Laboratoires do Recherches de la Société des Usines Chimiques Rhône-Poulenc, No. D.S.Ph. No. 171249 submitted by Rhône-Poulenc. Ganter, P. and Girard, P. (1973b) Produit 26019 R.P. - Examen histologique de la toxicité oculaire du 26019 R.P. chez le chien aprés un traitement do 3 mois. Unpublished report from Laboratoires de Recherches de la Société des Usines Chimiques Rhône-Poulenc, No. D.S.Ph. No. 17131, submitted by Rhône-Poulenc. Hastings, S.E., Huffmann, K.W and Gallo, M.A. (1974) Dominant Lethal Mutagenicity in Mice. Unpublished report from Boss and Clark, Division of Rhodia Inc., No. SEH 74:69. Hastings, S.E., Huffman, K.W. (1975) Chronic Toxicologic and Carcinogenic Study with R.P. 26019 in Mice. Unpublished report from Rhodia, Inc., Hess and Clark Division, No. SEH 75:113, submitted by Rhône-Poulenc. Hastings, S.E., Winbigler, J.C. and Kiggins, E.M. (1976) Chronic Toxicologic and Carcinogenic Study with R.P. 26019 in Rats. Unpublished report from Rhodia, Inc., Hess and Clerk Division, No. 76:57, submitted by Rhône-Poulenc. Laurent, M. and Buys, M. (1974) Etude du métabolisme chez le rat. Unpublished report from Société des Usines chimiques Rhône-Poulenc. Laurent, M., Brunie, B., Buys, M., Heusse, D. and Chabassol, Y. (1976) Etude du métabolism chez le rat á l'aide du produit marqué au 14C. Unpublished report from Rhône-Poulenc, Direction des Recherches et du Développement, Centre de Recherches Nicolas Grillet, Vitry-sur-Seine, C.N.G. -An No. 18548, submitted by Rhône-Poulenc. Pasquet, J. and Mazuret, A. (1974) Product 26019 R.P. Toxicité aigue chez le rat par voie intrapéritonéale. Unpublished report from Laboratoires de Recherches de la Socété des Usines Chimiques Rhône-Poulenc, No. 174621 submitted by Rhône-Poulenc. Pasquet J. and Nazuret, A. (1975a) Glycophene (26019 R.P.) - Formulation LFA 2043 (wettable powder at 50% of glyoophene) Acute toxicity and Dermal and Ocular tolerance. Unpublished report from Rhône-Poulenc. No. 18182 submitted by Rhône-Poulenc. Pasquet J. and Mazuret, A. (1975b) Glycophene (26019 R.P.). Etude de l'action sensibilisante outanée chez le cobaye. Unpublished report from Centre Nicolas Grillet, France, No. 18081, submitted by Rhône-Poulenc. Pasquet, J., Shirasu, Y., Moriya, M. and Katto, K. (1976) Mutagenicity Testing on Glycophene in Microbial Systems. Unpublished report from Institute of Environmental Toxicology, Toxicology Division, submitted by Rhône-Poulenc. Rhône-Poulenc (1977a) Dosages de residue dans les fruits a noyau (prune, Pêche, cerise) at a pepins (poire, pomme). Unpublished report R.P./R.D./C.N.G. No. 19 157. Rhône-Poulenc (1977b) Dosage de residue dans les petits fruits (fraises - framboises - cassis). Unpublished report R.P/R.D./C.N.G. No. 19 193. Rhône-Poulenc (1977c) 26019 R.P. Residus dans les raisins, ls mout, le vin et l'alcohol. Unpublished report R.P./R.D./C.N.G. No. 19 177. Rhône-Poulenc (1977d) Rovral-26019 RP. Dosages de residue dans les legumes. Unpublished report R.P./R.D./C.N.G. No. 19 191. Rhône-Poulenc (1977e) Rovral-26019 RP. Dosages de residue dans les cereales (blé et riz). Unpublished report R.P/R.D./C.N.G. No. 19 170. Rhône-Poulenc (1975a) 26019 Methods de dosage des residue dans les vegetaux et derives. Unpublished report R.P./R.D/C.N.G. -An. No. 2736. Rhône-Poulenc (1975b) 26019, Discussion at évaluation des performances de la méthode de dosage des résidus. Unpublished report R.P./R.D./C.N.G. -An No. 2658. Rhône-Poulenc (1973) Produit No. 26019 R.P. Metabolisms dans les vegetaux et dans le sol. Unpublished report S.W. C.R.P. -D.S.Ph.D.S. An Nord No. 17 374. Rhône-Poulenc (1977f) Dégradation du 26019 R.P. absorbé par les racines ou déposé sur les feuilles des vegetaux (fraisiers et blé) a l'aide de 26019 R.P. marqué au 14C. Unpublished report R.P./R.D./C.N.G. et C.N.G. An No. 19201. Rhône-Poulenc (1976) Degradation of RP 26019 in the soil. Treatments with 2 and 5 ppm 14C labelled product. Unpublished report R.P./R.D./C.N.G. No. 18785.
See Also: Toxicological Abbreviations Iprodione (Pesticide residues in food: 1980 evaluations) Iprodione (Pesticide residues in food: 1992 evaluations Part II Toxicology) Iprodione (Pesticide residues in food: 1995 evaluations Part II Toxicological & Environmental)