防治牡丹根腐病的有效药剂筛选

采用菌丝生长速率法和孢子萌发法,分别测定了咪鲜胺、醚菌酯、苯醚甲环唑、百菌清、多菌灵、代森锰锌等6种杀菌剂对牡丹根腐病菌的室内毒力。结果表明,6种药剂对病菌菌丝生长的EC50大小顺序为：咪鲜胺<多菌灵<代森锰锌<苯醚甲环唑<百菌清<醚菌酯,其中以咪鲜胺对牡丹根腐病病菌的菌丝生长抑制作用最强, EC50为0.200 mg/L;多菌灵、代森锰锌、苯醚甲环唑、百菌清依次减弱,醚菌酯的抑制菌丝生长的作用最小,EC50为33.98 mg/L。6种药剂对病菌孢子萌发的EC50大小顺序为：百菌清<咪鲜胺<苯醚甲环唑<多菌灵<代森锰锌<醚菌酯;其中以百菌清对牡丹根腐病菌的孢子萌发抑制作用最强,EC50为0.343 mg/L;咪鲜胺、苯醚甲环唑、多菌灵、代森锰锌依次减弱,醚菌酯抑制孢子萌发的作用最小,EC50为38.4 mg/L。     

取代酰腙类化合物的合成及其杀虫活性研究

以对氯苯甲酸、甲醇、水合肼、对硝基苯甲醛、对甲氧基苯甲醛、苯乙酮为原料,合成了对硝基苯甲醛对氯苯甲酰腙、对甲氧基苯甲醛对氯苯甲酰腙及苯乙酮对氯苯甲酰腙。目标化合物的结构通过核磁共振氢谱、元素分析和红外光谱进行了表征,并试验了目标化合物对菜粉蝶幼虫的杀虫活性。活性筛选试验结果表明,对硝基苯甲醛对氯苯甲酰腙的触杀活性和胃毒活性最强。系列浓度试验表明,处理24h后,对硝基苯甲醛对氯苯甲酰腙对菜粉蝶幼虫的触杀活性和胃毒活性的EC50分别为497.85mg/L、287.01mg/L;处理48h后,二者分别为272.21mg/L、145.75mg/L。     

非洲凤仙茎基腐病病原学及药剂敏感性1）

对非洲凤仙（Impatiens wallerana Hook．f．）茎基腐病的症状进行了描述,结合病原形态特征、培养特性及rDNA－ITS序列分析结果,确定该病害由Rhizoctonia solani Kühn AG4－HG－Ⅰ融合群引起。病菌的生物学特性研究表明：菌丝较适生长温度为25～30℃;菌丝生长较佳的培养基为OA和PSA,较佳的碳源为D－（＋）麦芽糖、α－乳糖和可溶性淀粉,较佳的氮源为硝酸钾和硝酸钠;pH＝7时菌丝生长最好;光照条件对菌丝生长无影响;菌丝致死条件为51℃、10 min。采用生长速率法测定了病菌对30种杀菌剂的敏感性,结果表明,病菌对≥300亿个· g－1内生芽孢杆菌WP、1000亿个· g－1枯草芽孢杆菌WP、25％肟菌·50％戊唑醇WG、40％氟硅唑EC敏感性较高,对其EC50＜1．0 mg· L－1,可以作为田间防治非洲凤仙茎基腐病的首选杀菌剂。     

Toxicity of chlorine to different sizes of black tiger shrimp (Penaeus monodon) in low-salinity shrimp pond water

An experiment was conducted, in a dark room with controlled temperature (27.3–28.4 °C), to determine the acute toxicity of chlorine concentration to black tiger shrimp (Penaeus monodon fabicus) of sizes 0.02 g, 2.75 g, 8.47 g and 23.65 g. Toxicity tests on each of these shrimp sizes were run in triplicate in glass jars under static conditions without media renewal. The concentration of active chlorine that killed 50% of the shrimp of each size after 24‐h exposure (LC₅₀‐24 h) was used as an indicator of acute toxicity. Chlorine concentrations applied in the shrimp toxicity test ranged from 2.0 to 14.5 mg L^?1 in shrimp pond water. As the test water contained total suspended solids of 22.0–85.0 mg L^?1 and total ammonia nitrogen of 0.18–0.40 mg L^?1, the resultant concentrations of combined residual chlorine ranged from 0.6 to 3.5 mg L^?1, which were the effective doses causing shrimp mortality. The test results showed that 24‐h LC₅₀ for average shrimp size at 0.02, 2.75, 8.47 and 23.65 g occurred in water containing combined residual chlorine at a concentration of 0.91, 1.39, 1.74 and 1.98 mg L^?1, for which the original application doses were 6.96, 2.05 11.50 and 13.34 mg L^?1 respectively.     

二氯异氰尿酸钠、溴氯海因、敌杀死对鲶鱼的急性毒性试验

用生物毒性试验方法进行二氯异氰尿酸钠、溴氯海因、敌杀死对鲶鱼 (9～ 1 1cm )的急性毒性试验 ,结果表明三种药物的安全浓度分别为 0 1 8mg/L、 0 56mg/L、 0 0 0 4mg/L。     

大蒜精油对灰茶尺蠖的室内毒力及田间防效

采用大蒜精油对灰荼尺蠖进行了室内及田间药效试验,结果表明大蒜精油对灰茶尺蠖的致死中浓度(LC50)为1038.60 mg/L,50％大蒜精油100～250倍液对灰荼尺蠖低龄幼虫具有良好的速效性和持效性,建议生产中可在灰茶尺蠖1～2龄幼虫发生期喷施100～250倍液大蒜精油.这一结果为开发大蒜精油作为茶树主要害虫的新型低...     

5种药剂对枸杞棉蚜室内毒力及田间防效

为了明确5种药剂对枸杞棉蚜的适宜施药剂量,开展了室内毒力测定和田间药效试验.结果 表明,1％甲维盐EC对枸杞棉蚜的毒力最高,50％噻虫嗪WG毒力最低,24 h LC50分别为2.44 mg/L和1875.69 mg/L.5种药剂毒力大小依次为甲维盐＞啶虫脒＞吡蚜酮＞呋虫胺＞噻虫嗪.田间试验结果表明,随着施药时间的延长,...     

A new plant-based bioassay for aquatic sediments

Background, Goal and Scope  To date, standardised bioassays for the assessment of the ecotoxicological potential in sediments and dredged material use test organisms like bacteria, algae and crustaceae. This paper presents the development and application of a novel sediment contact test (whole sediment) withMyriophyllum aquaticum, a representative of rooted aquatic macrophytes. The aim of the present study is to demonstrate the value of a sediment contact test with rooted macrophytes as a supplement to existing test batteries in order to improve the assessment of sediment toxicity. Methods  The newly developed sediment contact test withMyriophylhim aquaticum was applied to natural whole sediments. For performing the test, whorls ofMyriophyllum aquaticum were directly planted in the native sediment and incubated in the light at 24°C (cf. section results and discussion). The end points of the test were the number of the shoots and the fresh weight of the whole plants. The duckweed growth inhibition test withLemna minor according to ISO/DIS 20079 was performed in pore waters from sediment samples. The results of the sediment contact test withMyriophyllum aquaticum were compared with each other and with those of the aquatic duckweed test. Results and Discussion  A test protocol for the new plant-based sediment contact test using the aquatic plantMyriophyllum aquaticum as an indicator was developed. The best control sediment proved to be the OECD sediment (OECD 207). A test period of 10 days appeared to be sufficient for the test. The increase of biomass and the derived growth rate were found to be the most suitable evaluation parameters. The growth behaviour ofMyriophyllum aquaticum differed depending on the origin of sediments. Therefore, plant-affecting contamination, that is bound in sediments, was indicated. Conclusions  The novel sediment contact test withMyriophyllum aquaticum can indicate phytotoxic effects in sediments. Therefore, it allows a better assessment of the overall-toxicity in whole sediments. Recommendations and Outlook  The sediment contact test withMyriophyllum aquaticum is a valuable tool for the evaluation of the ecotoxicological risk potential of waters and sediments. It should become a complement to a standardised test battery generally used for the assessment of sediment toxicity.     

Short- and long-term effects of heavy metals on phosphatase activity in soils: An ecological dose-response model approach

Summary The aim of this study was to provide manageable data to help establish permissible limits for the pollution of soil by heavy metals. Therefore the short-and long-term effects of heavy metal pollution on phosphatase activity was studied in five different soil types. The results are presented graphically as logistic dose-response curves. It was possible to construct a curve for sand and silty loam soil but it was more difficult to establish a curve for sandy loam and clay soil and nearly impossible (except for Cu) for peat. The toxicity of the various metals can be compared on the basis of mmol values. In clay soils, for Cd, Cr, Cu, and Zn, the 50% effective ecological dose (ED₅₀) values were comparable (approximately 45 mmol kg^–1), but the ED₁₀ values were very different, at 7.4, 41.4, 15.1, and 0.55, respectively. At the ED₅₀ value, toxicity did not decrease with time and, in sandy soils, was approximately 2.6 mmol kg ^–1 dry soil for Cd, Cu, and Zn. In four out of five soils, the Cd toxicity was higher 1.5 years after the addition of heavy metal salts than after 6 weeks. Toxicity was least in the sandy loam, silty loam, and clay soil, and varied in general between 12 and 88 mmol kg^–1. In setting limits, the criteria selected (no-effect level, ED₁₀ or ED₅₀) determine the concentration and also the toxicity of the sequence. It is suggested that the data presented here could be very useful in helping to set permissible limits for heavy metal soil pollution.     

Cadmium‐induced changes in glutathione and phenolics of Thlaspi and Noccaea species differing in Cd accumulation

Glutathione (GSH) and phenolics play an important role in plant defense against metal‐ion toxicity. The antioxidant activity and metal‐binding capacity of these compounds can account for the protective effects. In contrast to animal‐cell models, however, the possible interplay among these substances in stress defense of plants is poorly investigated. This study compares the influence of cadmium (Cd) on the profiles of both soluble phenolics and GSH in shoots of different Thlaspi and Noccaea species: two ecotypes of the nonhyperaccumulator T. arvense differing in Cd resistance (ecotype Aigues Vives, Cd‐sensitive, and ecotype Jena, Cd‐resistant) and two Cd‐tolerant Cd‐Zn hyperaccumulators N. praecox and N. caerulescens (formerly Thlaspi praecox and T. caerulescens). To reveal the possible influence of Cd‐induced sulfur (S) shortage on the stress response, plants receiving normal S concentrations (500 μM MgSO₄) and plants treated with surplus S (500 μM MgSO₄ + 500 μM K₂SO₄) were analyzed. Our working hypothesis was that species differences in tolerance to high tissue Cd concentrations should be reflected by differences in endogenous levels of GSH and phenolic compounds. The results reveal clear species‐dependent differences in both the constitutive patterns and the Cd‐ and S‐induced changes in shoot concentrations of GSH and phenolics. However, no simple relationship between these shoot concentrations and Cd accumulation and tolerance can be established.