Inhibition of ergosterol biosynthesis in Ustilago maydis by the fungicide 1-[2-(2, 4-dichlorophenyl)-4-ethyl-1, 3-dioxolan-2-ylmethyl]-1H-1, 2, 4-triazole

Inhibition of sporidial multiplication in cultures of Ustilago maydis by 1-[2-(2, 4-dichlorophenyl)-4-ethyl-1, 3-dioxolan-2-ylmethyl]-1H-1, 2, 4-triazole^a (CGA-64251), at concentrations of 0.1, 1.0 and 5.0 μg ml^?1, increased from about 15% during the first 4 h, to 58–70% during the subsequent 4 to 12-h period. Sporidia became swollen and highly branched in the presence of the fungicide. Total lipid content as a percentage of the dry weight was not affected after exposure of the sporidia to the fungicide at 0.1 or 5 μg ml^?1 for 4 h, but synthesis of ergosterol and other demethyl-sterols was inhibited by 87–92%. Large quantities of methyl-sterol precursors of ergosterol and of free fatty acids accumulated in the treated sporidia. Fungitoxicity of CGA-64251 is attributed to inhibition of ergosterol biosynthesis at the stage of sterol C-14 demethylation.     

N-羟基-N-2-[N-(4-氯苯基)-3-吡唑氧基甲基]-苯胺的合成

高效低成本合成N-羟基-N-2-[N-(4-氯苯基)-3-吡唑氧基甲基]-苯胺。以2-[(N-4-氯苯基)-1H-吡唑-3-基氧甲基]硝基苯和碳酸氢钠为原材料,5%Pt/C为催化剂,通入氢气还原得N-羟基-N-2-[N-(4-氯苯基)-3-吡唑氧基甲基]-苯胺,并对不同条件下的试验结果进行了分析。优化条件为氢气进气压力为0.2Mpa,5%Pt/C催化剂与2-[(N-4-氯苯基)-1H-吡唑-3-基氧甲基]硝基苯的配比为5∶60,温度为30℃,反应时间为4h。该反应条件下产物反应收率≥97%,含量≥97%,生产成本低、操作简便非常适合工业化生产。     

Organophosphorus poisoning: A comparative study of the toxicity of chlorfenvinphos [2-chloro-1- (2′, 4′, -dichlorophenyl) vinyl diethyl phosphate] to the pigeon,the pheasant and the Japanese Quail

The acute oral toxicity of chlorfenvinphos [2-chloro-1-(2′, 4′-dichlorophenyl)vinyl diethyl phosphate] was measured in pigeon (Columba livia), pheasant (Phasianus colchicus), and quail (Coturnix coturnix japonica) and the compound was shown to be particularly toxic to pigeons. Additionally, all three species were fed chlorfenvinphos at 100 ppm in their diet for two or four weeks and esterase measurements were made by conventional and electrophoretic methods on extracts of liver, kidney and brain. The conventionally measured esterase inhibition correlated well with the acute oral toxicity figures. A more detailed study of the histochemically stained electrophoregams showed some discrepancies compared with conventional methods but offered a possible explanation of the inter-species toxicity difference in that it revealed differential inhibition of some brain iso-esterases in pigeon but not in pheasant or quail.     

Metolachlor (2-chloro-N-[2-ethyl-6-methylphenyl]-N-[2-methoxy-l-methylethyl] acetamide) and the metolachlor safener CGA 43089 [α-(cyanomethoximino)-benzacetonitrile] in sorghum seedlings: Correlations between morphological effects and ethylene formation

Treatment of germinating sorghum [Sorghum bicolor (L.) Moench] seeds with the grass herbicide, metolachlor (2-chloro-N-[2-ethyl-6-methylphenyl]-N-[2-methoxy-1-methylethyl] acetamide), causes growth retardation, promoted by thickening of the first leaf and thus inhibition of unfolding of secondary leaves, and increased ethylene production. Sorghum seeds pretreated with the safener CGA 43089 [α-(cyanomethoximino)-benzacetonitrile] exhibit neither morphological deformations nor ethylene production upon metolachlor treatment. Aminoethoxyvinylglycine [l-2-amino-4-(2-aminoethoxy)-trans-3-butenoic acid], a specific inhibitor of ethylene formation in higher plants, decreases ethylene formation by metolachlor-treated sorghum seedlings; the observed deformations, however, remain unchanged. Sorghum control seedlings which grow against a covering plate build up ethylene concentrations as after herbicide treatment, but without induction of the morphological symptoms. These observations suggest that the plant hormone ethylene is a symptom and not the inducer of the morphological effects visible after metolachlor treatment of sorghum seedlings.     

Synthesis and Insecticidal Activity of Some New 3-[4(3H)-Quinazolinone-2-(yl)thiomethyl]-1,2,4- triazole-5-thiols

A series of 14 new 3-[4(3H)-quinazolinone-2-(yl)thiomethyl]-1,2,4-triazoles were prepared and characterized by elemental analyses, IR, [¹H] NMR and mass spectral data. Four of the compounds showed insecticidal activity equivalent to that of malathion against the adult stage of the blow fly (Chrysomyia albiceps). However, their activity against the larval stages of this insect species was considerably weaker.     

Different in-planta and ex-planta activities of 7-chloro-4-(2-[trifluoromethyl]phenoxy)quinoline against Pyricularia grisea due to volatilization

7-Chloro-4-[2-(trifluoromethyl)phenoxy]quinoline (L Y248908) strongly inhibits mycelial growth of Pyricularia grisea in ex-planta assays but, when applied to the foliage of rice seedlings, its protective and curative properties against P. grisea are poor. The principal cause for this difference was found to be volatilization of LY248908 from treated foliage. Variations in fungal sensitivity (due to strain or development stage) and compound loss due to translocation, sequestration, metabolism, or degradation were shown not to be significant.     

1-[2-苄氧基-2-(2,4-二氟苯基)乙基]-1H-1,2,4-三唑衍生物的合成及杀菌活性

以抗真菌药物益康唑为先导化合物,设计合成了17个1-((2-取代苄基) 氧基)-2-(2,4-二氟苯基) 乙基)-1H-1,2,4-三唑类目标化合物,其中14个为首次报道,其结构均经 1H NMR、13C NMR和HRMS确认。采用菌丝生长速率法测定了目标化合物对7种植物病原菌的抑制效果,并对毒力较高的化合物进行了其对水稻纹枯病和小麦条锈病的盆栽和田间药效试验,而且测定了其对水稻纹枯病菌麦角甾醇生物合成的抑制作用。结果表明:大多数目标化合物对测试病原菌菌丝生长有较强的抑制作用,尤其对水稻纹枯病菌和番茄早疫病菌的抑制作用最好,其中对水稻纹枯病菌的EC₅₀值均低于3 μmol/L,明显高于对照药剂苯醚甲环唑和益康唑;化合物 4a 、 4b 、 4c 、 4g 、 4i 和 4l 对番茄早疫病菌的EC₅₀值均低于10 μmol/L。在浓度为250 μmol/L时,化合物 4b 和 4i 对小麦条锈病的盆栽防效均超过70%,在有效剂量为240 g/hm2时,化合物 4b 对小麦条锈病的田间防效达到81.93%。而且,化合物 4b 和 4i 在100 μmol/L时可有效抑制水稻纹枯病菌麦角甾醇的生物合成,抑制效果在80%左右。     

Herbicide perfluidone (1,1,1-trifluoro-N-[2-methyl-4-(phenylsulfonyl)phenyl]methanesulfonamide): Its metabolism in rats and chickens

Rats and chickens were each given a single oral dose (10 or 100 mg/kg body wt) of 1,1,1-trifluoro-N-[2-methyl-4-(phenylsulfonyl)phenyl-¹⁴C(U)]methanesulfonamide ([¹⁴C]perfluidone). Depending on the size of the dose, from 8.4 to 36.2% of the [¹⁴C] was eliminated in the urine and from 36.4 to 85.4% was eliminated in the feces within 48 hr after dosing. Less than 1% of the [¹⁴C] given to laying hens as [¹⁴C]perfluidone was present in the eggs produced during the first 96 hr after dosing. The percentage of the administered [¹⁴C] that remained in these animals (body with G.I. tract and contents removed) varied from 0.34 (96 hr after dosing) to 1.68% (48 hr after dosing). ¹⁴C-labeled compunds in the urine and feces from the rats and chickens were purified by solvent extraction, column chromatography, and gas-liquid chromatography, and then identified by infrared and mass spectrometry. The parent compound was the major ¹⁴C-labeled component in the urine and feces of both animals. 1,1,1-Trifluoro-N-[2-methyl-4-(3-hydroxyphenylsulfonyl)phenyl]methanesulfonamide was present in the feces of both animals. The proposed structures of other metabolites were 1,1,1-trifluoro-N-hydroxy-N-[2-methyl-4-(phenylsulfonyl)phenyl]methanesulfonamide (rat urine) and 1,1,1-trifluoro-N-{2-methyl-4-[(methylsulfonyl)-phenylsulfonyl]phenyl}methanesulfonamide (chicken urine).     

Metabolism of the insecticide SD 8280, 2-chloro-1-(2,4-dichlorophenyl)vinyl dimethyl phosphate,following its application to rice

The metabolism of the insecticide SD 8280 [2-chloro-1-(2,4-dichlorophenyl)vinyl dimethyl phosphate] in rice plants has been examined. When rice seedlings were treated with [¹⁴C]-SD 8280 the major metabolite was 1-(2,4-dichlorophenyl)ethanol which was present mainly conjugated with plant carbohydrates. This compound was also the major metabolite present in grain and straw from rice treated with [¹⁴C]-SD 8280 and grown to maturity under paddy conditions both in the glasshouse and in an outdoor enclosure. Other metabolites detected in the mature plants included 2-chloro-1-(2,4-dichlorophenyl)vinyl methyl hydrogen phosphate and 2,4-dichloro-benzoic acid, both of which occurred in free and conjugated forms. Paddy water was sampled at intervals after the application of [¹⁴C]-SD 8280 and the total residue in the water fell from initial levels of 0.28–1.1 μg/ml (expressed as SD 8280 equivalent) immediately after treatment to <0.01 μg/ml after 2–3 weeks. The total residues in the soil from these experiments were low and did not exceed 0.20 mg/kg (SD 8280 equivalents) through the 0–15 cm profile.     

3-苄基-5-(1-(2-氧代-1-氧杂螺[4,5]癸-3-烯-3-基)亚乙基)-2-氨基咪唑啉-4-酮类化合物的合成及杀菌活性

为寻找高活性的杀菌化合物,在前期合成5-(1-(4-甲基-2-氧代-1-氧杂螺[4,5]癸-3-烯-3-基) 亚乙基)-2-氨基咪唑啉-4-酮类化合物的基础上进行结构修饰,在咪唑啉-4-酮的3-位引入苄基,设计并合成了一系列未见文献报道的化合物,其结构经过核磁共振氢谱 (1H NMR)、碳谱 (13C NMR) 及高分辨质谱 (HR-ESI-MS) 确证。经高效液相色谱 (HPLC) 分析显示,Z-构型中间体化合物 6 在酸性条件下会发生氮质子化开环再环化,转化为E-构型化合物 7 。离体杀菌活性测定结果表明,3-位苄基的引入改善了该类化合物的杀菌活性,其中化合物 (E)-3-苄基-5-(1-(4-甲基-2-氧代-1-氧杂螺[4,5]癸-3-烯-3-基) 亚乙基)-2-(4-甲氧基苯基) 氨基-咪唑啉-4-酮 ( 9c ) 和 (E)-3-苄基-5-(1-(4-甲基-2-氧代-1-氧杂螺[4,5]癸-3-烯-3-基) 亚乙基)-2-(4-氟苯基) 氨基-咪唑啉-4-酮 ( 9h ) 对油菜菌核病菌的EC₅₀ 值分别为14.3和21.1 mg/L。活体杀菌活性测试结果显示,在400 mg/L下化合物 9c 对于黄瓜霜霉病和小麦白粉病的防治效果分别为 80%和85%。     

Systemic fungicidal and insecticidal activities of 1- and 2-[bis (dimethylamido)phosphoryl]-3-alkyl-5-anilino-1,2,4-triazoles

The compounds referred to in the title have been investigated for fungicidal, insecticidal and acaricidal activities in laboratory and greenhouse tests. Several representatives of this class of compounds were active against powdery mildew on apple, cucumber, and barley, and against aphids and spider mites, both when applied to the leaves and when added to the nutrient solutions of test plants. Treatment of leaf halves resulted in protection of the entire leaves. A striking difference in pesticidal activity was observed between two series of isomers. Representatives of the series with the phosphoryl group in the 1-position showed much greater pesticidal activities than their corresponding isomers with the phosphoryl group in the 2-position. The optimum activity within the two homologous series (R-H, CH₃ ... C₆H₁₃) was determined: generally the lower homologues (R-H, CH₃, C₂H₅ and i-C₃H₇) showed the greatest pesticidal activity in the systemic tests. After leaf-application the influence of the length of R was less pronounced or even reversed.Samenvatting De in de titel genoemde stoffen zijn onderzocht op fungicide, insecticide en acaricide werking in laboratorium en kasproeven. Verscheidene vertegenwoordigers van dit type verbindingen waren werkzaam tegen echte meeldauw van appel, komkommer en gerst, en tegen bladluizen en spint, dit zowel na toepassing op de bladeren als na toevoeging aan de voedingsoplossingen van proefplanten. Behandeling van bladhelften resulteerde in bescherming van de gehele bladeren. Een opvallend verschil werd waargenomen tussen de werking van twee reeksen isomeren. Vertegenwoordigers van de reeks met de fosforylgroep op de 1-plaats waren veel werkzamer dan hun isomeren met de fosforylgroep op de 2-plaats. Het optimum binnen de twee homologe reeksen (R-H, CH₃ ... C₆H₁₃) werd bepaald: in het algemeen waren de lagere homologen (R-H, CH₃; C₂H₅ en i-C₃H₇) het werkzaamst in de systemische proeven. Na een preventieve bladbespuiting was de invloed van de lengte van R minder uitgesproken of zelfs omgekeerd.     

N-[2-(4,6-二甲氧基嘧啶-2-氧基)苯亚甲基]取代胺类衍生物的合成及除草活性

以水杨醛为原料,经取代、加成和消除反应合成了6个标题化合物(3a~3f),其中4个(3a~3d)为新化合物,其结构经核磁共振氢谱、质谱和元素分析确认。初步的除草活性测试结果表明,在有效成分150 g/hm2的剂量下,除化合物3f对稗草Echinochloa crus-galli的抑制率为55%外,其余5个化合物对供试杂草的抑制率均在80%以上,部分化合物对稗草、早熟禾Poa annua、反枝苋Amaranthus retroflexus或小藜Chenopodium album的抑制率达100%。     

N-苯基-2-(4,6-二甲氧基-2-嘧啶氧基)-6-氯-苄胺(ZJ1835)的除草活性研究

为明确新化合物N-苯基-2-(4,6-二甲氧基-2-嘧啶氧基)-6-氯-苄胺(ZJ1835)在棉花田的应用前景,就其对棉花的安全性、选择性、杀草谱和田间应用技术进行了研究。室内生物测定结果表明,ZJ1835对棉花生长初期有一定矮化作用,但不影响出苗和后期生长,在有效剂量225 g/hm2下对棉花安全性好;对不同棉花品种之间的安全性有一定差异,其中对王岳9913的安全性最好,其次为银山1号和福棉6号,对冀丰197安全性略差;该化合物在棉花与马唐、反枝苋之间的选择性系数分别为2.14和13.00,具有较好的选择性;多数田间常见杂草对其敏感,杀草谱较广。田间试验结果显示,ZJ1835在90～120 g/hm2有效剂量下对供试棉花安全性好,对棉田杂草总防效为82.1%～92.8%,具有一定的开发应用潜力。     

Phototransformation of napropamide [N,N-diethyl-2-(1-naphthyloxy)propionamide] in aqueous solution: influence on the toxicity of solutions

The main photoproducts formed in an aqueous solution of napropamide irradiated in UV light are N,N-diethyl-2-(1-hydroxynaphthalen-2-yl)propionamide, N,N-diethyl-2-(4-hydroxynaphthalen-1-yl)propionamide and 1-naphthol. These account for c.60%, 15% and 10% of napropamide converted respectively. No influence of the irradiation wavelength or of oxygen was observed. The same products were obtained by irradiation of methanolic solutions. The three identified products result from the cleavage of naphthoxy–carbon bond. The first two products imply a photo-Fries rearrangement. The influence of irradiation on the toxicity of the solutions was studied by the Microtox™ test. The significant increase observed may be attributed partly to the formation of 1-naphthol. © 1998 Society of Chemical Industry     

N-｛5-[1-(2,4-二氯苯氧)乙基]-1,3,4-噻二唑-2-基｝ -N''-芳酰基硫脲的合成及其生物活性

通过2-氨基-5- -1,3,4-噻二唑与芳酰基异硫氰酸酯反应,合成了12 个新的芳酰基硫脲,采用核磁共振氢谱、红外光谱和元素分析确证了它们的结构。初步的生物活性测定试验表明,部分化合物具有良好的植物生长调节活性,其中化合物 2c、2j 具有较好的生长素活性,其促进率分别为26.6%与26.9%,但不及对照β-吲哚乙酸。     

吡啶衍生物研究(V):2-[(2-氯吡啶)-4-基]-5-芳胺基-1,3,4-噻二唑的合成及杀菌活性

合成了一系列 2 - [(2 -氯吡啶 ) - 4 -基 ]- 5-芳胺基 - 1,3,4 -噻二唑类化合物 ,其结构经元素分析、1H NMR、和 13 C NMR确认。初步生物活性测定表明 ,合成化合物对某些真菌生长表现出较好的抑制活性 ,如 I- 0 2在 50 0 μMg· m L-1剂量下对水稻纹枯病菌生长的抑制率达87.5%。     

丹皮酚衍生物——3-羟基-1-(2-羟基-4-甲氧基苯)-3-(2'-溴苯)-1-丙酮的合成及其抗菌活性

从牡丹根皮中提取丹皮酚,将丹皮酚精制后与2-溴苯甲醛在室温及碱催化下发生亲核加成反应,生成一种丹皮酚衍生物——3-羟基-1-(2-羟基-4-甲氧基苯)-3-(2'-溴苯)-1-丙酮,产率为78.6%,其结构用紫外光谱(UV)、红外光谱(IR)、质谱(MS)及核磁共振谱(NMR),结合元素分析等进行表征。单晶X-衍射(X-ray diffraction)测定结果表明:该晶体属单斜晶系;P2(1)/n空间群;晶胞参数:a=0.99380(15) nm,b=0.80617(12) nm,c=1.9251(3) nm,α=90.0(2)°,β=103.287(2)°,γ=90(2)°,V=1.5010(4) nm3,Dc=1.554 mg/cm3, μ=2.751 mm-1,F(000)=712,Z=4,R1=0.0290,ωR2=0.0660,R(int)=0.0322。该丹皮酚衍生物具有抗菌活性,对植物源真菌油菜菌核病菌Sclerotinia sclerotiorum和番茄灰霉病菌Botrytis cinerea的最小抑菌浓度(MIC)分别为0.36和0.48 g/L,对病源细菌福氏志贺菌Shigella flexneri 51065和金黄色葡萄球菌Staphylococcus aureus ATTCC25925的MIC分别为0.02和0.06 g/L。     

Physiological effects of methyl 2-[4(2,4-dichlorophenoxy)phenoxy] propanoate on oat,wild oat,and wheat

Methyl 2-[4-(2,4-dichlorophenoxy)phenoxy]propanoate (dichlofop-methyl) is a selective herbicide for wild oat (Avena fatua L.) control in wheat (Triticum aestivum L.). Dichlofop-methyl inhibited IAA-stimulated elongation of oat and wheat coleoptile segments by 51 and 13%, respectively, at 10 μM concentrations. Dichlofop-methyl alone had no auxin activity at concentrations of 0.1, 1.0, and 10 μM. The inhibitory effect of dichlofop-methyl was overcome partially by increasing the IAA concentration or by application of 3,6-dichloro-o-anisic acid (dicamba), a herbicide with weak auxin activity. The de-esterified free acid metabolite, 2-[4-(2,4-dichlorophenoxy)phenoxy]-propionic acid (dichlofop), at 10 μM inhibited auxin-stimulated oat coleoptile elongation by 23%, but it did not affect wheat coleoptile elongation at the same concentration. Both dichlofop-methyl and dichlofop inhibited root growth in excised shoots and seedlings of wild oat but had no effect on wheat. Dichlofop was a more effective inhibitor of root growth than dichlofop-methyl. The results suggest that dichlofop-methyl functions as a strong auxin antagonist, while the metabolite, dichlofop, inhibits root growth and development by another mechanism. The herbicidal effect of dichlofop-methyl may be the net effect of two biologically active forms of the compound each with a different mode of action acting at different sites within a susceptible plant.     

Residues of clenpirin [2-(3,4-dichiorophenylimino)-l-n-butyl pyrrolidine] in the fatty tissues of steers and in butter fat

A series of trials in which cattle were either treated dermally or dosed orally with clenpirin [2-(3,4-dichlorophenylimino)-l-n-butyl pyrrolidine] was undertaken. Tissue fat from steers and butter fat from milking cattle were sampled and residue levels determined colorimetricaliy. Residues following a single application of clenpirin (9 litres/beast at 0.25% w/v) reached an average maximum of 2.0 mg/kg in body fat and then declined to 0.2 mg/kg after 14 days. Multiple applications (9 litres/beast at 0.25% w/v) resulted in a progressive buildup of residues in body fat to about 30 mg/kg after 4 treatments. When steers were dosed orally with technical clenpirin at 700 mg/beast/day for 15 days the average fat level reached 0.7 mg/kg. In a series of trials with milking cattle a single dermal exposure (0.23-0.3% w/v aqueous emulsion) yielded residues in butter fat ranging from 1 5.5-51 1 mg/kg at the first sampling 5 h after treatment. Six days later these had declined to about 0.8 mg/kg.