Synthesis and Structure–Activity Relationships of Miticidal 4,5-Dihydropyrazole-5-thiones

A series of novel 4,5-dihydropyrazole-5-thiones (DHPs) was synthesised by treating the corresponding dihydropyrazolones with ‘Lawesson’s reagent and evaluated for miticidal activity against two-spotted spider mites (Tetranychus urticae Koch). Of these, 3-(4-chlorophenyl)-4,4-dimethyl-1-phenyl-4,5-dihydropyrazole-5-thione, 3-(4-chlorophenyl)-4-ethyl-4-methyl-1-phenyl-4,5-dihydropyrazole-5-thione, 3-(4-chlorophenyl)-1-phenyl-4,5-dihydropyrazole-5-thione-4-spirocyclopentane and 4,4-dimethyl-1-phenyl-3-(4-trifluoromethyl-phenyl)-4,5-dihydropyrazole-5-thione were highly active (pEC₅₀>4·0) and were more effective than the miticide dicofol (pEC₅₀=3·879), which has traditionally been used for the control of phytophagous mites. Structure–activity relationship (SAR) studies were performed on each position of the pyrazole ring of DHPs. The results indicated that the unsubstituted phenyl, 4-substituted phenyl and thioxo groups on the 1-, 3- and 5-positions of DHPs respectively were required for activity. Quantitative SAR studies using physicochemical parameters of substituents and the capacity factor k′ as a hydrophobicity index suggested that: (a) the activities of all types of DHPs examined were mainly dominated by hydrophobicity, (b) the bulkiness of 4-substituents of the 3-phenyl ring favoured the activity and (c) the log k′ optimum for all DHPs was 1·675, equivalent to a log P_ow value of c. 5·0.     

Synthesis and biological evaluation of [1-(1H-1,2,4-triazol-1-yl)alkyl]-1-silacyclopentanes

A series of 1-aryl-1-(1H-1,2,4-triazol-1-yl)alkyl-1-silacyclopentanes has been synthesized by four-step reactions starting from 1-chloroalkyltrichlorosilane and tested for fungicidal activities in vitro for ten fungi and in vivo for four fungi occurring in rice, cucumber, tomato etc. Biological activities of the title compounds are strongly dependent upon the p-substituent on the phenyl group in the following order: F>Cl>Ph>OEt>H. Especially, 1-p-fluorophenyl-1-[1-(1H-1,2,4-triazol-1-yl)alkyl]-1-silacyclopentanes (alkyl=methyl or ethyl) showed significant fungicidal activity with a broad spectrum comparable to flusilazole in in-vivo assay. © 1998 SCI.     

Aerobic soil metabolism of flupyrazofos

To elucidate the fate of flupyrazofos [O,O-diethyl O-(1-phenyl-3-trifluoromethyl-5-pyrazoyl)phosphorothionate] in soil, an aerobic soil metabolism study was carried out for 60 days with [¹⁴C]flupyrazofos applied at a concentration of 0·38 μg g^-1 to a loamy soil. The material balance ranged from 103·5% to 86·9% and the half-life of [¹⁴C]flupyrazofos was calculated to be 13·6 days. The metabolites identified during the study were 1-phenyl-3-trifluoromethyl-5-hydroxypyrazole (PTMHP) and O,O-diethyl O-(1-phenyl-3-trifluoromethyl-5-pyrazoyl)phosphate (flupyrazofos oxon), with maximum levels of 9·8% and 1·6% of applied radiocarbon, respectively. Evolved [¹⁴C]carbon dioxide accounted for up to 5·3% of applied radiocarbon and no volatile products were detected during the study. Non-extractable ¹⁴C-residue reached 31·6% of applied material at 60 days after treatment and radiocarbon was distributed almost evenly in humin, humic acid and fulvic acid fraction. © 1998 Society of Chemical Industry     

Phototransformation of Triadimefon on Glass and Soil Surfaces

Photodegradation of triadimefon has been studied on glass and soil surfaces. A number of photoproducts have been isolated and characterised by NMR, IR and MS. Photolysis resulted in considerable amounts of 1-(4-chlorophenoxymethyl)-1,2,4-triazole, 1-(4-chlorophenoxy)-2,2-dimethyl-1-(1,2,4-triazol-1-yl)propane, 1-(1,2,4-triazol-1-yl)-3,3-dimethylbutan-2-one and 1-(4-chlorophenoxy)-3,3-dimethyl-1-(1,2,4-triazol-1-yl)butan-2-ol. Rates of photodegradation on glass and soil surfaces under UV and sunlight followed first-order kinetics with a significant correlation coefficient. Photodegradation was greater on alluvial soil than on laterite soil.     

Photolysis of Diniconazole-M under Sunlight

The photodegradation of diniconazole-M [(E)-(R)-1-(2,4-dichlorophenyl)-4,4-dimethyl-2-(1,2,4-triazol-1-yl)-1-pentene-3-ol] was studied as thin film on glass surface under sunlight. Photoproducts were separated and identified by NMR, IR, UV and mass spectroscopy. They were characterised as the (Z)-isomer of diniconazole-M, a cyclic alcohol and its corresponding ketone and an isoquinoline derivative. © 1997 SCI.     

A novel series of O,O-diethyl O-(1,3-disubstituted-1,2,4-triazol-5-yl) phosphorothioates. Part II. Quantitative structure–activity relationships

The in-vivo toxicity data of 33 O,O-diethyl O-(1-alkyl-3-R″-1,2,4-triazol-5-yl) phosphorothioates, reported in Part I of this series, were subjected to multiregression analyses for the following organisms: Leptinotarsa decemlineata (larvae), Macrosiphum euphorbiae (aphids), Culex pipiens (adults), Spodoptera littoralis (larvae) and the rat. The activities were found to depend mainly on the steric parameters of R″, these being best expressed by the values L, B₁ and B₄ of the computer program STERIMOL. It was shown that there were different steric requirements for each species and these are discussed. The predictive values of the best equations were also estimated.     

Isolation of microsomal cytochrome-p450 isozymes from Ustilago maydis and their interaction with sterol demethylation inhibitors

A procedure for the isolation of microsomes containing cytochrome-P450 isozymes from Ustilago maydis is described. Yields of P450 amount to approximately 19(±+ 6) pmol mg^?1 of microsomal protein. The wavelength of maximum absorbance of the reduced carbon monoxide difference spectrum is 448-449 nm. The azole fungicides prochloraz, etaconazole, imazalil, triadimefon and 3-(2,4-dichlorophenyl)-2-(1H-1,2,4-triazol-1-yl)-4(3H)-quinazoline, which differ markedly in toxicity to U. maydis, all induce type II binding difference spectra at extremely low concentrations (10^?9-10^?8 M). The DMI concentrations which cause half saturation of type II binding difference spectra (IC₅₀) do not correlate with the fungicidal activities of the azoles. Binding of carbon monoxide to ferrous cytochrome-P450 was only slightly inhibited to different degrees by the DMIs tested. However, the inhibition of carbon monoxide binding also does not correlate with fungitoxicity of the DMIs. The results in this paper suggest that the spectrophotometric studies with this preparation are not useful for evaluating selective toxicity of DMIs to intact sporidia of U. maydis.     

The properties of RH 3866, a new triazole fungicide

2-Butyl-2-(4 chlorophenyl)-3-(1H-1,2,4-triazol-1-yl)propanenitrile, RH 3866, a new broad-spectrum fungicide was particularly effective against fungi in the subclass loculoascomycetidae and against powdery mildews and rusts. Some activity against fungi in the genera Fusarium, Monilinia and Rhizoctonia was also observed. The compound was translocated upwards when applied as a soil drench to control wheat-leaf rust caused by Puccinia recondita f.sp. tritici. Fenarimol-resistant Aspergillus nidulans was cross-resistant to RH 3866. Using a cell-free yeast enzyme extract RH 3866 strongly inhibited desmethyl sterol production.     

A novel series of O,O-diethyl O-(1,3-disubstituted-1,2,4-triazol-5-yl) phosphorothioates. Part I. Synthesis and laboratory evaluation

A novel series of O,O-diethyl O-(1-R′-3-R″-1,2,4-triazol-5-yl) phosphorothioates, in in which R″ was an alkyl group and R″ was a radical characterised by the presence of a conjugated multiple bond, generally of a vinyl nature, has been synthesised and tested in the search for new insecticides. Several of the compounds showed a broad spectrum of activity, covering important species of Orthoptera, Hemiptera, Lepidoptera, Coleoptera, Diptera and mites. At the same time they were characterised by a relatively low oral toxicity to rats.     

Aerobic Metabolism of Flupropacil in Sandy Loam Soil

The aerobic soil metabolism of [¹⁴C]flupropacil (isopropyl 2-chloro-5-(1,2,3,6-tetrahydro-3-methyl-2,6-dioxo-4-trifluoromethylpyrimidin-1-yl)benzoate) was determined in microbially active, sieved (2-mm) sandy loam soil with a soil moisture content of 75% at 1/3 bar. The soil was treated with [¹⁴C]flupropacil at 0·5 mg kg⁻¹ (twice the field use rate) and placed in incubation flasks connected to a series of traps (50 g litre⁻¹ NaOH, 0·5M H₂SO₄, ethylene glycol) and incubated at 25(±1)°C. Soil was sampled at 0, 3, 9, 20, 30, 48, 76, 120, 181 and 238 days of aerobic incubation. Volatiles were collected once every two weeks and on the day of soil sampling. Flupropacil metabolized with a half-life of 79 days under aerobic conditions. The major metabolite was flupropacil acid which accounted for up to 69·1% of the initially applied radioactivity at Day 238. Each of the two minor metabolites detected at the end of the study accounted for less than 0·5%. One of the minor metabolites was identified as C4242 acid (2-chloro-5-(1,2,3,6-tetrahydro-2,6-dioxo-4-trifluoromethylpyrimidin-1-yl)benzoic acid). Only a negligible portion (less than 0·3%) of the applied flupropacil was mineralized to [¹⁴C]carbon dioxide. Extractable radioactivity ranged from 78·9% to 95·5%, with bound residues accounting for 3·2%–23·4%. The material balance ranged from 91·6% to 104·4%.     

1-取代苯胺基- 4,4-二甲基-2-(1H-1,2,4-三唑-1-基)-1-戊烯-3-酮的合成及其生物活性

为寻找高活性的烯基三唑类杀菌剂,利用1-二甲氨基-4,4-二甲基-2-(1H-1,2,4-三唑-1-基)-1-戊烯-3-酮与取代苯胺进行亲核取代反应,合成了一系列新型1-取代苯胺基-4,4-二甲基-2-(1H-1,2,4-三唑-1-基)-1-戊烯-3-酮化合物,其结构经元素分析、核磁共振氢谱确认。由1H NMR分析结果推测该类化合物E式构型为优势产物。初步生物活性测试结果表明,化合物 1n (取代基R=3-OCH3)在50 μg/mL浓度下对葡萄白腐菌Coniothyrium diplodiella、黄瓜黑星菌Cladosporium cucumerinum等的抑制率均达到100%;在10 μg/mL浓度下对促进黄瓜子叶生根的活性达到155.2%。     

Quantitative bioassays for determining residues and availability to plants of sulphonylurea herbicides

A bioassay procedure for quantitative determination of sulphonylurea herbicides is described. Turnips (Brassica rapa) were found very suitable as test plants and gave results within 10 days. Six sulphonylurea compounds were investigated for their activity in three widely differing soils. The potential availability to plants was calculated from the dose-response curves of vermiculite (non-sorptive substrate) and the corresponding ED₅₀-values of the soils. The dose-response relationship (logistic curve) was described by a computer model by a position parameter, the slope of the curve and the minimum and maximum fresh weights of plants. The limit of quantitative detection in the range of ED₃₀ in vermiculite was 0·06 μg 1^?1 for sulfometuron and 1·03 μg 1^?1 for DPX-L5300, methy12-([4-methoxy-6-methyl-1,3,5-triazin-2-yl (methyl)carbamoyl]-sulphamoyl) benzoate. Results with turnips showed that sulfometuron was the most active compound in all substrates (ED₅₀ in vermiculite 0·12 μg 1^?1) followed by chlorsulfuron, metsulfuron-methyl, triasulfuron, DPX-M6316, methyl 3-([(4-methoxy-6-methyl-1,3,5-triazin-2-yl)aminocarbamoyl]-aminosulphaphamoyl)-2-thiophenecarboxylate, and DPX-L5300 which had ED₅₀ or 1·98 μg 1^?1, The Horotiu sandy loam soil showed the highest ED₅₀-values and the lowest plant availability for all compounds compared to the other soils. Probit and logistic evaluation methods for deriving dose-response relationships are compared and their applicability is discussed.     

Effects of fluazifop-butyl on shoot growth and rhizome buds of Elymus repens (L.) Gould

A series of glasshouse experiments was conducted to evaluate the activity of fluazifop-butyl, butyl 2-[4-(5-trifluoromethyl-2-pyridyloxy)phenoxy] propionate, against Elymus repens. Foliar applications of doses 0·25–1·0 kg ha^?1 consistently gave better control than did soil applications. The most obvious phytotoxic symptoms were chlorosis and necrosis, beginning with the youngest leaves 5–6 days after spraying, which spread to all leaves within 2 weeks. Translocation was measured by defoliating plants at different times after spraying and assessing regrowth and by evaluating rhizome-bud viability. At low doses (0·125 and 0·25 kg ha^?1) translocation to rhizomes occurred mainly between 6 and 48 h. When fluazifop-butyl was sprayed at a dose range of 0·125–1·0 kg ha^?1, at least 90% of the rhizome buds had accumulated a lethal dose within 72 h of spraying. In another experiment, with a dose of 0·25 kg ha^?1, 31, 72 and 92% of rhizome buds were found to be non-viable when sampled 2, 24 and 48 h respectively after spraying. At 1·0 kg ha^?1 all the buds had accumulated sufficient herbicide to prevent sprouting 48 h after spraying.     

Optimal application timing of simeconazole granules for control of rice kernel smut and false smut

We investigated the optimal timing of simeconazole (RS-2-(4-fluorophenyl)-1-(1H-1,2,4-triazol-1-yl)-3-trimethylsilylpropan-2-ol) application for controlling rice kernel smut in field trials in Miyagi Prefecture, Japan, using formulations of simeconazole (1.5% granules). The field tests revealed that a submerged application of simeconazole granules (450–600 g ai/ha) at 1–5 weeks before heading was highly effective against kernel smut, with treatments 1–2 weeks before heading being the most effective. Submerged application of the fungicide at 2–5 weeks before heading was also highly effective against false smut, with treatment 3 weeks before heading being the most effective. These periods overlap the timing for optimal application of simeconazole to control rice sheath blight and ear blight. Consequently, we concluded that treatment with simeconazole 2–3 weeks before heading can be a useful tool for controlling all four diseases.     

Structural studies in azolylmethanes

The crystal structures of a number of fungicidal azolylmethanes are compared. In the benzyl compounds [1-aryl-4,4-dimethyl-2-(1,2,4-triazol-1-yl)pentan-3-ones, the corresponding pentan-3-ols, and 1-(4-chlorophenyl)-3-(2-fluorophenyl)-2-(1,2,4-triazol-1-yl)propan-1-one], the benzyl and tert-butyl groups (or 4-chlorophenyl group) are trans, whereas in the analogous phenoxy compounds [1-(4-chlorophenoxy)-3,3-dimethyl-1-(1,2,4-triazol-1-yl)butan-2-one and the corresponding butan-2-ol], the tert-butyl groups are trans to the triazole and gauche to the phenoxy group. Coupling constants, determined by nuclear magnetic resonance (n.m.r.) spectroscopy, suggest that for some compounds there is one dominant solution conformation. Intramolecular hydrogen bonding, observed by infrared spectroscopy in two of the compounds, supports the findings by n.m.r. For some compounds, the crystal and solution conformations appear to be very similar, whereas in others they are quite different. Published data on the relative activity of the enantiomers of the benzyl- and phenoxy-compounds are discussed, but differences in the relative activity of enantiomers in the two series cannot be readily rationalised. It is concluded that different enantiomers may have different modes of binding at the active site.     

Synthesis,spectral properties and insecticidal,acaricidal and ovicidal activities of some O-(1,5-disubstituted- 6-oxo-12H-pyridazin-4-yl) phosphorothioates

A synthesis of O,O-dialkyl, O-alkyl O-2-chloroethyl (or O-2-ethoxyethyl) O-(1,5-disubstituted-6-oxo-1H-pyridazin-4-yl) phosphorothioates is described. Infrared, Raman and ultraviolet spectra of the compounds prepared are interpreted. The wave-numbers of the v(C? C) bands were correlated with substituent constants. Good linear correlations of v(C? O) with σ, σ^F, σ_I and σ_R were observed for compounds containing various substituents in the neighbourhood of the keto group of the pyridazinone ring. The insecticidal, acaricidal and ovicidal activities of O-(ethyl or isopropyl), O-(alkyl, 2-chloroethyl, or 2-ethoxyethyl) O-(5-methoxy-1-methyl-6-oxo-1H- pyridazin-4-yl) phosphorothioates, O-ethyl O-isopropyl O-(5-methoxy-1-substituted-6-oxo-1H-pyridazin-4-yl) phosphorothioates and O-ethyl O-isopropyl O-(1-methyl-5-substitutedd-oxo-1H-pyridazin-4-yl) phosphorothioates are reported together with the toxicity of some of these compounds to rats.     

Light-induced transformations of tribenuron-methyl in aqueous solution

Tribenuron-methyl a sulfonylurea herbicide, readily photodegraded in aqueous solution under sunlight and UV light. The photoproducts identified were N-methyl-4-methoxy-6-methyl-1,3,5-triazine-2-amine, methyl 2-(aminosulfonyl) benzoate, o-benzoic sulfimide, N-(4-methoxy-6-methyl1,3,5-triazin-2-yl)-N-methyl urea and N-(2-carbomethoxyphenyl)-N-(4-methoxy-6-methyl-1,3,5triazin-2-yl)-N′-methyl urea. The rate of photodegradation of tribenuron-methyl in different types of water followed first-order kinetics with significant correlation coefficient, increased with increase in pH and was also dependent upon the dissolved impurities. © 1999 Society of Chemical Industry     

Measurement and simulation of the movement of thiazafluron, clopyralid and metamitron in soil columns

Adsorption and leaching of the herbicides thiazafluron (1,3-dimethyl-1(5-trifluoromethyl-1,3,4-thiadiazol-2-yl)urea), metamitron (4-amino-4,5-dihydro-3-methyl-6-phenyl-1,2,4-tri azin-5-one) and clopyralid (3,6-dichloropicolinic acid) were studied in one sandy and two silty-clay soils. Equilibrium adsorption coefficients (K_d) were measured using a batch equilibration procedure, and mobility was studied in repacked columns of the soils under fluctuating saturated/unsaturated flow conditions. Breakthrough curves (BTCs) were consistent with an inverse relationship between leaching and adsorption with greater mobility of the weakly-adsorbed clopyralid than the more strongly adsorbed thiazafluron or metamitron. The BTC data were used to evaluate the LEACHP simulation model. Following model calibration with respect to hydrological parameters and some of the herbicide degradation rates, the best fits between predicted and observed data were with the less adsorptive and highly mobile clopyralid. In general, the model gave acceptable predictions of the timing of the concentration maxima and the shapes of the BTCs, although earlier breakthrough than that observed was predicted with the less mobile herbicides, thiazafluron and metamitron, in the silty-clay soils. For metamitron, the total amounts leached were not predicted accurately, suggesting more rapid degradation of the herbicide in the soil columns than in the kinetic studies performed in a 1:1 soil:solution ratio shaken system.     

The current status of insecticide resistance in Musca domestica in England and Wales and the implications for housefly control in intensive animal units

Following the 1984–85 housefly (Musca domestica L.) resistance survey, a similar survey was carried out between January 1990 and April 1992 in order to monitor changes in UK housefly resistance. Samples of fly populations were collected from 35 farms throughout England and Wales. Dose-response data were obtained by topical application and feeding test methods. For both methods the knockdown (KD) after 48 h was used for all the dose-response comparisons. The ranges of resistance factors for the topical application method were for methomyl, 1·6–20·0 at KD₅₀ and 4·5–34·4 at KD₉₅; for azamethiphos, 2·5–58·5 at KD₅₀ and 5·0–2604 at KD₉₅; for pyrethrins+piperonyl butoxide, 1·2–9·6 at KD₅₀ and 1·6–14·7 at KD₉₅; and for permethrin, 2·2–118·8 at KD₅₀ and 4·3–200·0 at KD₉₅. The ranges of the resistance factors for the feeding tests were for methomyl, 1·2–56·1 at KD₅₀ and 3·1–80·0 at KD₉₅, and for azamethiphos, 3·9–125·0 at KD₅₀ and 4·4–380·0 at KD₉₅. The means of resistance factors for all of the insecticides showed increases over those obtained in a previous survey carried out in 1984–85. The significance of the results for housefly control in intensive animal units in the UK is discussed.     

Physicochemical factors affecting the uptake by roots and translocation to shoots of amine bases in barley

The uptake by barley roots from nutrient solution and subsequent transport to shoots of two series of amine bases were measured over 6 to 72 h. The compounds were chosen to span systematically ranges of lipophilicity (assessed using 1-octanol/water partition coefficients, K_ow) and pKa that would include commercial pesticide amines. In a series of six substituted phenethyl amines, strong bases with pKa∽9·5, all the compounds were strongly taken up by roots from solutions of pH 8·0; uptake declined substantially as the pH was lowered to 5·0, especially for the compounds of intermediate lipophilicity (log K_ow 2 to 3). This uptake could be ascribed to three processes: (i) accumulation of the cation inside the root cells due to the negative charge on the plasmalemma, as given by the Nernst equation and important only for the polar compounds which have low permeation rates through membranes; (ii) accumulation into the vacuole by ion-trapping, which was the dominant process at high pH for all compounds and at all pH values for the compounds of intermediate lipophilicity; (iii) partitioning on to the root solids, substantial only for the most lipophilic compounds. Translocation to shoots was proportional to uptake by roots, this ratio being independent of external pH for each compound and being optimal for the compounds of intermediate lipophilicity. Such proportionality was also observed in a series of three weaker bases of intermediate lipophilicity, in which compounds of pKa 7·4 to 8·0 were also well taken up and translocated whereas the very weak base 4-ethylaniline (pKa 5·03) was much less so. Tests with quaternised pyridines confirmed that organic cations move only slowly through membranes. The observed behaviour of the amines could be modelled reasonably well assuming that transport within the plant was dominated by movement across membranes of the non-ionised species, and this appeared to be true even for the most lipophilic phenethylamine (log K_ow 4·67) studied, though its long-distance movement would be as the protonated species. © 1998 Society of Chemical Industry