Distribution and degradation of dinitroaniline herbicides in an aquatic ecosystem

The accumulation potential of six, structurally related, dinitroaniline herbicides was investigated in an aquatic ecosystem. The herbicides investigated were trifluralin (α,α,α-trifluoro-2,6-dinitro-N,N-dipropyl-p-toluidine), profluralin [N-(cyclopropylmethyl)-α,α,α-trifluoro-2,6-dinitro-N-propyl-p-toluidine], dinitramine [N³,N³-diethyl-2,4-dinitro-6-(trifluoromethyl)-m-phenylenediamine], chlornidine [N,N-bis(2-chloroethyl)-2,6-dinitro-p-toluidine], fluchloralin [N-(2-chloroethyl)-2,6-dinitro-N-propyl-4-(trifluoromethyl)aniline], and butralin [4-(1,1-dimethylethyl)-N-(1-methylpropyl)-2,6-dinitrobenzenamine]. The herbicide (0.1 mg) plus 1 μCi of ¹⁴C-labeled herbicide was adsorbed on 100 g of soil (1 ppm), added to individual aquariums, and flooded with 4 liters of water. Algae, snails, and daphnia were added, and ¹⁴C in water was monitored for 30 days. Fish were added on Day 30, and all components were harvested 3 days later. Bioaccumulation ratios (concentration in organism/concentration in water) for fish depended on the amount of their exposure to sunlight: Aquariums held in the dark had higher ratios for fish (235–755) than did those exposed to sunlight (32–83). Bioaccumulation ratios in the dark for fish based on ¹⁴C from bound soil residues of butralin and profluralin were 76 and 119, respectively. Direct repeated applications of profluralin (without soil) at 4-day intervals resulted in a rapid increase, then a decrease in bioaccumulation ratios for Gambusia, but a continuous increase for catfish.     

The degradation of dinitramine (N3,N3-diethyl 2,4-dinitro-6-trifluoromethyl-m-phenylenediamine) in soil

Radioactive dinitramine (1) was incorporated at $\text{1}\text{2}$ Ib/acre (0.6 ppm) in Anaheim silty loam soil and its degradation studied over an 8-month period. For both specifically—¹⁴CF₃ and -Ring-UL-[¹⁴C] labeled (1), only ca. 20% of the radioactivity was lost from the incorporated zone. Mehanol- or acetonitrile-extractable radioactivity decreased rapidly over the initial 60 days reaching 20% after 244 days. Two compounds were isolated and characterized as (1), 0.05 ppm, and 6-amino-1-ethyl-2-methyl-7-nitro-5-trifluoromethylbenzimidazole (2), 0.06 ppm. Two other compounds were tentatively identified by TLC as monodealkylated dinitramine (3), 0.01 ppm, and 6-amino-2-methyl-7-nitro-5-trifluoromethylbenzimidazole (4), 0.01 ppm, Sodium hydroxide (10%) and anionic surfactant (10%) were effective in removing up to 50% of the residual bound radioactivity (i.e., nonacetonitrile extractable), while dimethylamine (25%) released 26%; extraction by acid was less effective.     

Effects of various classes of herbicides on four species of algae

Chlorella pyrenoidosa, Chlorococcum sp., Lyngbya sp., and Anabaena variabilis were cultured in Bold's basal medium. They were treated with 0.1, 1.0, and 10 μM concentrations of 2-chloro-2′, 6′-diethyl-N-(methoxymethyl)acetanilide (alachlor), 2-chloro-4-(ethylamino)-6-(tert-butyl-amino)-s-triazine (terbuthylazine), 2-sec-butyl-4,6-dinitrophenol (dinoseb), 1,1-dimethyl-3-(α,α,α-trifluoro-2,6-dinitro-N-propyl-p-toluidine) (profluralin), 2, 4-bis(isopropylamino)-6-(methylthio)-s-triazine (prometryne), and (2,4-dichlorophenoxy)acetic acid (2,4-D). Growth of all algal species tested was markedly reduced by the triazines. Alachlor, dinoseb, and fluometuron inhibited growth of some algae at higher concentrations while 2,4-D and profluralin did not inhibit growth at the concentrations tested. Photosynthesis was greatly inhibited by the triazines, even at the 0.1 μM concentration. Fluometuron was very toxic to the blue-green algae but had less effect on the green algae tested. Lyngbya was most susceptible to photosynthesis reduction by the herbicides. The concentrations of herbicides tested had little effect on respiration of the algae species. It appears that effects on algal growth were due primarily to inhibition of photosynthesis rather than to other metabolic processes.     

Enhanced Mineralization of [14C]Atrazine in Kochia scoparia Rhizospheric Soil from a Pesticide-Contaminated Site

Mineralization of atrazine (6-chloro-N²-ethyl-N⁴-isopropyl-1,3,5- triazine-2,4-diamine) in soil treated with a mixture of atrazine and metolachlor (2-chloro-6′-ethyl-N-(2-methoxy-1-methylethyl)acet-o-toluidide at concentrations typical of point-source contamination (50 μg g⁻¹ each) was significantly greater (P<0·001) in rhizospheric soil from Kochia scoparia (L.) Roth., a herbicide-resistant plant, than in non-vegetated and control soils. Soils were collected from an agrochemical dealership contaminated with several herbicides, including atra-zine, metolachlor, trifluralin (α,α,α-trifluoro-2,6-dinitro-N,N-dipropyl-p-toluidine and pendimethalin (N-(1-ethylpropyl)-2,6-dinitro-3,4-xylidene), at concentrations well exceeding the field application rates. Mineralization rates of ring-labeled atrazine in both rhizospheric and non-vegetated soils were quite high (>47% of the initial ¹⁴C applied after 36 days) compared to literature values. These results suggest that plants such as Kochia might be managed at pesticide-contaminated sites to help facilitate microbial degradation of wastes such as atrazine in soil.     

Growth regulator inhibition of tobacco callus growth

The activity of two groups of growth regulators, substituted dinitroanilines and nitrophenylhydrazines, were evaluated in a tobacco (Nicotiana tabacum L. “X-73”) callus tissue bioassay. Molar concentrations required to inhibit fresh weight gain by 50% (I₅₀) was determined by using linear regression analysis on data obtained by testing a range of five concentrations of each chemical. All chemicals tested were inhibitory to callus tissue grown in the dark. Cell division seemed to be the primary activity inhibited. The most active of the dinitroaniline series was α,α,α-trifluoro-2,6-dinitro-N-ethyl-N-2′,6′-dichlorobenzyl-p-toluidine (I) (I₅₀ = 1.5 × 10^?10M). I and two other N-(o-halobenzyl) dinitroanilines were more active than α,α,α-trifluoro-2,6-dinitro-N-ethyl-N-2′-chloro-6′-fluorobenzyl-p-toluidine (IV), which is being developed commercially for suppression of axillary buds in tobacco. The two most active nitrophenylhydrazines tested were 1,1-dimethyl-2-(2′,6′-dinitro-3′-n-propylamino-α,α,α-trifluoro-p-tolyl)hydrazine (XVIII) and 3′,5′-dinitro-p-(2,2-diethylhydrazino)-N-methoxy-N-methylbenzamide (XIX) (I₅₀ values of 7.9 × 10^?9 and 9.3 × 10^?9M, respectively). Factors such as electronic distribution, steric hindrance, and lipid solubility were considered to influence the biological activity of the compounds tested.     

Microbial dealkylation of trifluralin in pure culture

Mixed populations of soil microorganisms were enriched in the presence of trifluralin (α,α,α-trifluoro-2,6-dinitro-N,N-dipropyl-p-toluidine) and 180 pure strains were subsequently isolated. About a third were able to liberate 1.5–6% ¹⁴CO₂ from 0.15 mM [propyl-1-¹⁴C]trifluralin after growing for 21 days on a complex medium. One strain, identified as a Candida sp., showed a ¹⁴CO₂ evolution of 11%. The amount of liberated ¹⁴CO₂ could not be enhanced by adding small concentrations (<3%) of solvents to the culture, by varying the concentration of trifluralin, or by varying the composition of the complex medium. The Candida sp. was unable to cleave the aromatic ring of trifluralin or to use trifluralin as a sole source of carbon or nitrogen. Only traces (< 1%) of dealkylated trifluralin were accumulated in the culture.     

Antifungal mode of action of triforine

Rapidly growing mycelia of Aspergillus fumigatus treated with 10 μg/ml triforine (N,N′-bis-(1-formamido-2,2,2-trichloroethyl)-piperazine) showed little or no inhibition in dry weight increase prior to 2 h. By 2.5–3 h, triforine inhibited dry weight increase by 85%. The effects of triforine on protein, DNA, and RNA syntheses corresponded to the effect on dry weight increase both in time of onset and magnitude. Neither glucose nor acetate oxidation were inhibited by triforine.Ergosterol synthesis was almost completely inhibited by triforine even in the first hour after treatment. Inhibition of ergosterol synthesis was accompanied by an accumulation of the ergosterol precursors 24-methylenedihydrolanosterol, obtusifoliol, and 14α-methyl-Δ^{8, 24 (28)}-ergostadienol. Mycelia treated with 5 μg/ml of triarimol (α-(2,4-dichlorophenyl)-α-phenyl-5-pyrimidinemethanol) also accumulated the same sterols as well as a fourth sterol believed to be Δ^{5, 7}-ergostadienol.Identification of 4,4-dimethyl-Δ^{8, 24 (28)}-ergostadienol in untreated mycelia indicates that the C-14 methyl group is the first methyl group removed in the biosynthesis of ergosterol by A. fumigatus. The lack of detectable quantities of 4,4-dimethyl-Δ^{8, 24 (28)}-ergostadienol in triforine or triarimol-treated mycelia and the accumulation of C-14 methylated sterols in treated mycelia suggests that both fungicides inhibit sterol C-14 demethylation. The accumulation of Δ^{5, 7}-ergostadienol in triarimol-treated mycelia further implies that triarimol also inhibits the introduction of the sterol C-22(23) double bond.Two strains of Cladosporium cucumerinum tolerant to triforine and triarimol were also tolerant to the fungicide S-1358 (N-3-pyridyl-S-n-butyl-S′-p-t-butylbenzyl imidodithiocarbonate).     

Alternate pathways of metribuzin metabolism in soybean: Formation of N-glucoside and homoglutathione conjugates

Metribuzin [4-amino-6-tert-butyl-3(methylthio)-1,2,4-triazin-5(4H)-one] metabolism was studied in soybean [Glycine max (L.) Merr. Tracy]. Pulse treatment studies with seedlings and excised mature leaves showed that [5-¹⁴C]metribuzin was absorbed rapidly and translocated acropetally. In seedlings, >97% of the root-absorbed ¹⁴C was present in foliar tissues after 24 hr. In excised leaves, 50–60% of the absorbed ¹⁴C remained as metribuzin 48 hr after pulse treatment, 12–20% was present as polar metabolites, and 20–30% was present as an insoluble residue. Metabolites were isolated by solvent partitioning, and were purified by adsorption, ion-exchange, thin-layer, and high-performance liquid chromatography. The major metabolite (I) was identified as a homoglutathione conjugate, 4-amino-6-tert-butyl-3-S-(γ-glutamyl-cysteinyl-β-alanine)-1,2,4-triazin-5(4H)-one. Metabolite identification was confirmed by qualitative analysis of amino acid hydrolysis products, fast atom bombardment (FAB), and chemical ionization (CI) mass spectrometry, and by comparison with a reference glutathione conjugate synthesized in vitro with a hepatic microsomal oxidase system from rat. Minor metabolites were identified as an intermediate N-glucoside conjugate (II), a malonyl N-glucoside conjugate (III), and 4-malonylamido-6-tert-butyl-1,2,4-triazin-3,5(2H,4H)-dione (N-malonyl DK, IV) by CI and FAB mass spectrometry. Alternative pathways of metribuzin metabolism are proposed.     

Investigation on the transformation of fluchloralin by soil fungi: Identification of some metabolites

Fluchloralin [N-(2-chloroethyl)-α,α,α,-trifluoro-2,6-dinitro-N-propyl-p-toluidine] was transformed by two common soil fungi, Aspergillus flavus Link and Fusarium solani (Mart.) Sacc. in pure culture. The fungi were isolated from enrichment cultures of an analogous herbicidal compound, pendimethalin [N-(1-ethylpropyl)-2,6-dinitro-3,4-xylidine)]. Transformation of fluchloralin by these fungi resulted in the formation of several metabolites, 13 of which were identified. Besides the known mechanisms of microbial transformation of dinitroanilines, methylation of the anilino nitrogen and direct elimination of a nitro group at 2 position from the aromatic ring without any further substitution were also observed.     

Mercapturic acid formation in the metabolism of propachlor,CDAA, and fluorodifen in the rat

When [¹⁴C]F₃-fluorodifen (2,4′-dinitro-4-trifluoromethyl diphenylether), carbonyl-[¹⁴C]CDAA (N,N-diallyl-2-chloroacetamide), and carbonyl-¹⁴C-propachlor (2-chloro-N-isopropylacetanilide) were fed to rats, 57 to 86% of the ¹⁴C was excreted via the urine within 48 hr. Although very little radioactivity was excreted in the feces of CDAA-treated rats, 15–22% of the ¹⁴C was excreted in the feces of propachlor- of fluorodifentreated rats and an average of 8% of the ¹⁴C remained in these rats 48 hr after treatment. Oxidation of the ¹⁴C label to [¹⁴C]O₂ was not a major process in the metabolism of these herbicides. The only major radioactive metabolite present in the 24-h urine of fluorodifen-treated rats, 2-nitro-4-trifluoromethylphenyl mercapturic acid, accounted for 41% of the administered dose of ¹⁴C. In the metabolism of CDAA, the corresponding mercapturic acid accounted for 76% of the dose; it was the only major metabolite present in the 24-h urine. In contrast, three major metabolites were detected in the 24-h urine of propachlortreated rats, and the mercapturic acid accounted for only 20% of the dose. The mercapturic acid of each herbicide was identified by mass spectrometry.     

Photodecomposition of pendimethalin

The photodecomposition of pendimethalin (N-(l-ethylpropyl)-2,6-dinitro-3,4-xylidine, l) in solution, as a thin film, and on soil surfaces under ultraviolet light and sunlight was investigated. Irradiation of pendimethalin in methanol yielded, in addition to the minor dealkylated product, the major products 2-amino-6-nitro-N-(l-ethylpropyl)-3,4-xylidine and 2-nitroso-6-nitro-3,4-xylidine. Pendimethalin was found to degrade rapidly through reductive cyclisation of a nitro group and an adjacent N-ethylpropyl group to give a cyclised benzimidazole product. The photodecomposition of pendimethalin involves oxidative dealkylation, nitro reduction and cyclisation.     

Diphenamid removal from water and metabolism by aquatic plants

Several aquatic plants and algae were effective for removal of N, N-dimethyl-2,2-diphenylacetamide ([¹⁴C]diphenamid) from water and degradation to various metabolites. Parrotfeather (Myriophyllum brasilience L.) and water hyacinth (Eichornis crossiper L.) removed large quantities of diphenamid from water while algae (Ulothrix sp., Oedogonium sp., Gloeocystis sp., and Scenedesmus sp. mixed culture) and waterthread pondweed (Potamogeton diversifolius Raf.) were less effective in reducing diphenamid concentration in the water. A somewhat stable metabolite in algae, water hyacinth, and parrotfeather was N-methyl-2,2-diphenylacetamide. Algae and water hyacinth degraded diphenamid further to unknown products. One of these compounds moved more slowly than N-methyl-2,2-diphenylacetamide on thin-layer chromatography using benzene, n-heptane saturated with water and methanol solvent. While most solvents did not resolve 2,2-diphenylacetic acid from the base, petroleum ether, ethyl ether, and formic acid (50:50:2, v/v/v) was found to move 2,2-diphenylacetic acid further than diphenamid or N-methyl-2,2-diphenylacetamide on thin-layer chromatography.     

Metabolism of substituted diphenylether herbicides in plants. II. Identification of a new fluorodifen metabolite, S-(2-nitro-4-trifluoromethylphenyl)-glutathione in peanut

The herbicide, 2,4′-dinitro-4-trifluoromethyl diphenylether (fluorodifen), is eleaved in peanut to give the metabolite, S-(2-nitro-4-trifluoromethylphenyl)-glutathione. A comparison of the glutathione conjugate isolated from treated peanut leaves and from in vitro pea epicotyl glutathione S-transferase reaction showed that both metabolites were identical. Other polar metabolites were also isolated, but not identified. The structure of the glutathione conjugate was confirmed by amino acid analysis and by mass, NMR, and infrared spectroscopy. The p-nitrophenyl moiety is also conjugated to natural products and is released as the free p-nitrophenol upon acid hydrolysis.     

Metribuzin metabolism in tomato: Isolation and identification of N-glucoside conjugates

Metribuzin [4-amino-6-tert-butyl-3-(methylthio)-1,2,4-triazin-5(4H)-one] metabolism was studied in tomato (Lycopersicon esculentum Mill. “Sheyenne”). Pulse-treatment studies with seedlings and excised leaves showed that [5-¹⁴C]metribuzin was rapidly absorbed, translocated (acropetal), and metabolized to more polar products. Foliar tissues of 19-day-old seedlings metabolized 96% of the root-absorbed [¹⁴C]metribuzin in 120 hr. Excised mature leaves metabolized 85–90% of the petiole-absorbed [¹⁴C]metrubuzin in 48 hr. Polar metabolites were isolated by solvent partitioning, and purified by adsorption, thin-layer, and high-performance liquid chromatography. A minor intermediate metabolite (I) was identified as the polar β-d-(N-glucoside) conjugate of metribuzin. The biosynthesis of (I) was demonstrated with a partially purified UDP-glucose: metribuzin N-glucosyltransferase from tomato leaves. A possible correlation between foliar UDP-glucose: metribuzin N-glucosyltransferase activity levels and differences in the tolerance of selected tomato seedling cultivars to metribuzin was suggested. The major polar metabolite (II) was identified as the malonyl β-d-(N-glucoside) conjugate of metribuzin.     

Metabolism of substituted diphenylether herbicides in plants. I. Enzymatic cleavage of fluorodifen in peas (Pisum sativum L.)

A “soluble” glutathione S-transferase that catalyzes the cleavage of the herbicide, 2,4′-dinitro-4-trifluoromethyl diphenylether (fluorodifen), was isolated and partially characterized from epicotyl tissues of pea seedlings. A 32-fold purification of the enzyme was achieved by differential centrifugation, ammonium sulfate precipitation, Sephadex gel filtration, and DEAE-cellulose ion exchange chromatography. The enzyme had a pH optimum of 9.3–9.5 and was specific for reduced glutathione, with an estimated apparent K_m value of 7.4 × 10^?4M. Limited specificity studies with four substituted ¹⁴C-labeled diphenylether compounds indicated that fluorodifen was the only effective substrate, with an estimated apparent K_m value of 1.2 × 10^?5M. Differences and similarities between the pea epicotyl enzyme and other plant and animal glutathione S-transferases were discussed from the standpoint of substrate specificity, pH optima, distribution, stability, and inhibitor studies.     

Cold storage degradation of the herbicide metribuzin in field soil samples awaiting analysis

In conjunction with a study of herbicide degradation in the field, metribuzin (4-amino-6-tert-butyl-4,5-dihydro-3-methylthio-l,2,4-triazin-5-one) was shown to be degraded at-37±5°C in soil samples awaiting analysis. Products of this degradation process include the known derivatives DADK (6-tert-butyl-2,3,4,5-tetrahydro-l,2,4-triazine-3,5-dione) and DK (4-amino-6-tert-butyl-2,3,4,5-tetrahydro-l,2,4-triazine-3,5-dione) and these products themselves have been shown to be degraded further under the same storage conditions. Loss of the herbicide can be approximated using half order kinetics with respect to metribuzin; however, loss of both previously identified metabolites is most rapid when metabolite concentrations are highest. Assuming half order kinetics, samples of Almasippi very fine sandy loam containing metribuzin (0.5 mg/kg) can be expected to lose 50% of the herbicide in 282 days at - 37°, a period which is short enough to affect residue analysis results significantly should samples be stored for extended lengths of time prior to analysis. Implied in these results is the desirability of immediate analysis following collection of samples; otherwise rates of loss during storage must be determined to allow adjustment of results to compensate for residue losses in samples awaiting analysis.     

Assessment of the antifungal activity of selected biocontrol agents and their secondary metabolites against <Emphasis Type="Italic">Fusarium graminearum</Emphasis>

Fusarium graminearum (teleomorph: Gibberella zeae) is the causal agent of several destructive diseases in cereal crops worldwide. In the present study we have evaluated the potential of two strains of Trichoderma sp. (T23, and T16), a strain of Paecilomyces sp. (PS1), and their secondary metabolites (SMs) in suppressing F. graminearum. Results from dual culture experiments show that in the presence of either Trichoderma sp., or Paecilomyces sp. mycelial growth of F. graminearum is considerably inhibited. Strain T23 causes the greatest inhibition (83.8%), followed by strain T16 (72.2%), and strain PS1 (61.9%). Likewise, mycelial growth of the pathogen is completely inhibited (≥ 98%) when grown under exposure to volatile metabolites excreted from Trichoderma cultures. Bioautographic analyses using culture filtrates revealed that several antifungal SMs are excreted. Among five metabolites tested, 6-pentyl-alpha-pyrone (6PAP) from strain T23, and PF3 from strain PS1 exhibit pronounced antifungal activity against F. graminearum. A new method for mass production of perithecia of F. graminearum which is simple and more effective than traditional methods was developed, which allows an increase in perithecial formation of more than 5-fold. Using this method, we found, that in the presence of SMs perithecial formation was negatively affected. Perithecial production was suppressed by 81.4% and 76.6% using 200 μg ml^?1 of either 6PAP or PF3, respectively. Moreover, ascospore discharge was significantly suppressed (67.0%) when perithecia were exposed to the metabolite F116 produced by T16. Including 6PAP or PF3 in conidial suspensions impeded germination of conidia completely. Similarly, both metabolites strongly inhibited ascospore germination (? 90%).     

Trifluralin effects on tobacco callus tissue: Mitosis and selected metabolic effects

Inhibition of growth of pith callus of tobacco (Nicotiana tabacum, var. S-73) by the herbicide trifluralin (α,α,α - trifluoro - 2,6 - dinitro - N,N- dipropyl - p - toluidine) was previously observed. Inhibition of cell division in callus tissue of varying age by this herbicide was investigated using the Feulgen reagent and light microscopy. Upon staining and counting the number of cells in each phase of mitosis, a decrease in the number of cells in metaphase, anaphase, and telophase in the treated tissues was found. In addition to this reduction, arrested metaphases and multinucleated cells were observed. Similar results were observed with 10^?4M colchicine. The effects of trifluralin on incorporation of ¹⁴C-precursors into callus RNA, DNA, and protein were also investigated. Apparent RNA, DNA, and protein synthesis in callus were inhibited by trifluralin (5 × 10^?6M) treatment. The inhibition, however, was not expressed until 5–7 days after initiating treatment. Colchicine also affected apparent RNA, DNA, and protein synthesis; however, these effects were different than those observed with trifluralin. Incorporation of ¹⁴C-amino acids into protein was most severely inhibited by colchicine.     

Influence of the herbicides hexazinone and chlorsulfuron on the metabolism of isolated soybean leaf cells

The effects of the herbicides hexazinone [3-cyclohexyl-6-(dimethylamino)-1-methyl-1,3,5-triazine-2,4(1H,3H)-dione] and chlorsulfuron (2-chloro-N-[(4-methoxy-6-methyl-1,3,5-triazin-2-yl)aminocarbonyl]benzenesulfonamide) on the metabolism of enzymatically isolated leaf cells from soybean [Glycine max (L.) Merr., cv. ‘Essex’] were examined. Photosynthesis, protein, ribonucleic acid (RNA), and lipid syntheses were assayed by the incorporation of specific radioactive substrates into the isolated soybean leaf cells. These specific substrates were NaH¹⁴CO₃, [¹⁴C]leucine, [¹⁴C]uracil, and [¹⁴C]acetate, respectively. Time-course and concentration studies included incubation periods of 30, 60, and 120 min and concentrations of 0.1, 1, 10, and 100 μM of both herbicides. Photosynthesis was the most sensitive and first metabolic process inhibited by hexazinone. RNA and lipid syntheses were also inhibited significantly by hexazinone whereas the effect of this herbicide on protein synthesis was less. The most sensitive and first metabolic process inhibited by chlorsulfuron was lipid synthesis. Photosynthesis, RNA, and protein syntheses were affected significantly only by the highest concentration of this herbicide and longest exposure. Although these two herbicides may exert their herbicidal action by affecting other plant metabolic processes not examined in this study, hexazinone appears to be a strong photosynthetic inhibitor, while the herbicidal action of chlorsulfuron appeared to be related to its effects on lipid synthesis.     

新型含吡唑杂环邻氨基苯甲酰胺类化合物的合成与杀螨活性

以氯虫苯甲酰胺和氟虫腈的结构为基础,通过活性亚结构拼接的方法,设计合成了24个新型含吡唑杂环邻氨基苯甲酰胺类化合物,其结构经1H NM R、IR及APCI-M S表征。初步生物活性测试结果表明:化合物5-溴-N-[4-氯-2-甲基-6-(甲氨基甲酰基)苯基]-1-1-[2,6-二氯-4-(三氟甲基)苯基]-4-三氟甲基亚磺酰基-1H-吡唑-3-甲酰胺(5k)和5-溴-N-[4-溴-2-甲基-6-(甲氨基甲酰基)苯基]-1-[2,6-二氯-4-(三氟甲基)苯基]-4-三氟甲基亚磺酰基-1H-吡唑-3-甲酰胺(5l)在500 mg/L下对朱砂叶螨Tetranychus cinnabarinus的致死率为100%,但在100 mg/L下其致死率则分别降至30%和50%。所得结果可为邻氨基苯甲酰胺类化合物构效关系研究提供参考。