Infection of Melanoplus sanguinipes Grasshoppers following Ingestion of Rangeland Plant Species Harboring Vesicular Stomatitis Virus

Knowledge of the many mechanisms of vesicular stomatitis virus (VSV) transmission is critical for understanding of the epidemiology of sporadic disease outbreaks in the western United States. Migratory grasshoppers [Melanoplus sanguinipes (Fabricius)] have been implicated as reservoirs and mechanical vectors of VSV. The grasshopper-cattle-grasshopper transmission cycle is based on the assumptions that (i) virus shed from clinically infected animals would contaminate pasture plants and remain infectious on plant surfaces and (ii) grasshoppers would become infected by eating the virus-contaminated plants. Our objectives were to determine the stability of VSV on common plant species of U.S. Northern Plains rangelands and to assess the potential of these plant species as a source of virus for grasshoppers. Fourteen plant species were exposed to VSV and assayed for infectious virus over time (0 to 24 h). The frequency of viable virus recovery at 24 h postexposure was as high as 73%. The two most common plant species in Northern Plains rangelands (western wheatgrass [Pascopyrum smithii] and needle and thread [Hesperostipa comata]) were fed to groups of grasshoppers. At 3 weeks postfeeding, the grasshopper infection rate was 44 to 50%. Exposure of VSV to a commonly used grasshopper pesticide resulted in complete viral inactivation. This is the first report demonstrating the stability of VSV on rangeland plant surfaces, and it suggests that a significant window of opportunity exists for grasshoppers to ingest VSV from contaminated plants. The use of grasshopper pesticides on pastures would decrease the incidence of a virus-amplifying mechanical vector and might also decontaminate pastures, thereby decreasing the inter- and intraherd spread of VSV.Vesicular stomatitis virus (VSV) is a highly transmissible rhabdovirus that causes economically important, Office of International Epizootics (OIE)-reportable disease outbreaks, primarily in horses and cattle of western U.S. rangelands. Vesicular stomatitis (VS) is endemic in portions of the southeastern United States, Mexico, and South America. Outbreaks in the western United States are sporadic, occurring every 2 to 9 years over the past 23 years, with the most recent outbreak in 2006. During outbreaks, clinically infected animals salivate excessively and shed copious amounts of virus (4 to 6 log units of virus per ml) (8). Virus-laden saliva contaminates facilities (e.g., water and feed troughs, stables, and corrals) as well as the environment (e.g., plants and soil), allowing extensive animal-to-animal transmission once the virus is in the herd (16). Insects are believed to play important roles in the initial introduction of the virus into a herd from undetermined natural reservoirs, as well as transmitting it across large distances between herds of similar or different species during animal movement quarantines (8).The protocol of veterinary practitioners regarding VS is to control the spread of virus during outbreaks by keeping all animals on the premises; cleaning and disinfecting all personnel materials, instruments, equipment, vehicles, feed bunks, and water sources; and instructing personnel to shower and change clothing and boots when moving between herds. According to the OIE, soil and plants are suspected sources of virus, although no report to date confirms this. Therefore, decontamination of corrals and pastures is not a current recommendation. Sand flies, black flies, and biting midges (Culicoides sonorensis) have all been shown to be competent vectors, capable of transmitting the virus during blood feeding (2, 3, 12, 17). Thus, the control of biting insects in barns and other housing areas with screens and repellents is advised.Although research has traditionally focused on these hematophagous insects as important VSV vectors, the migratory grasshopper Melanoplus sanguinipes (Fabricius) was recently shown to be an efficient amplifying reservoir and a possible mechanical vector for VSV (10). M. sanguinipes is distributed in North America from Alaska to Mexico and from coast to coast. It is a serious pest of both crops and grasslands, causing more crop damage than any other species of grasshopper in the United States (14). Grasshoppers are typically ingested by grazing animals when they are immobile during one of five molting stages. It is estimated that grazing cattle consume approximately 50 of these molting grasshoppers per day (10). In a previous study, grasshoppers were shown to amplify ingested VSV as much as 1,400-fold and to maintain high virus titers for at least 28 days (10). The route of VSV entry into cattle eating the infected grasshoppers was via scarifications on the tongue and gums, typically seen in cattle on rangeland pastures. Of significance to this study, the grasshopper-cattle-grasshopper transmission cycle is based on the assumptions that (i) virus shed from clinically infected animals would contaminate pasture plants and remain infectious on plant surfaces and (ii) grasshoppers would become infected by eating the virus-contaminated plants. To determine the stability of VSV on plants and the window of opportunity for grasshoppers to ingest viable VSV from those contaminated plants, we exposed rangeland plant species typically consumed by grasshoppers to VSV and determined the titer of virus over time. Several plant species harbored viable virus as long as 24 h. Grasshoppers were fed virus-contaminated plants, held for 21 days, and tested for virus. Current decontamination practices during VSV outbreaks do not address the viral contamination of pastures or the control of nonhematophagous virus-amplifying insect species such as grasshoppers. To that end, a commonly used no-withdrawal grasshopper pesticide was evaluated for its ability to inactivate VSV. A decontamination/deinfestation approach, as an additional VS control strategy for livestock in pastures, is discussed.     

ERRATUM: New Body Mass Estimates for Omomys carteri,a Middle Eocene Primate From North America. Am J Phys Anthropol 109:41–52.

Payseur BA, Covert HA, Vinyard CJ, Dagosto M. 1999. New Body Mass Estimates for Omomys carteri, a Middle Eocene Primate From North America. Am J Phys Anthropol 109:41–52. This article included an incomplete Table 2. The final two columns, showing “Intercept” and “SEE” data were omitted. The complete Table 2, with these two columns included, is provided below.     

FREUDEIA KASZAB, A NEWLY RECORDED GENUS AND A NEW SPECIES FROM CHINA (COLEOPTERA, TENEBRIONIDAE,TENTYRIINI)

报道中国鳖甲族1新纪录属及1新种:异颚弗鳖甲Freudeia heteromaxillaria sp.nov.,描述了新种的形态特征并附鉴别特征图和整体照片.新种模式标本保存于中国科学院西北高原生物研究所和河北大学博物馆.     

河西走廊天然固沙植被区地表甲虫多样性及其对沙漠化的指示作用

干旱、半干旱区沙漠化强烈影响动植物分布及多样性,地表甲虫是荒漠中主要的动物类群,它们对沙漠化引起的植被和土壤环境变化响应十分敏感。鉴于此,以河西走廊中部张掖绿洲外围的天然固沙植被区作为研究区,依据沙漠化发育程度选择流动沙丘（ASD）、丘间低地（IL）、半固定（SFSD）和固定沙丘（FSD）4种生境,调查了地表甲虫群落组成及影响甲虫分布的植被和土壤环境。研究发现,4种生境地表甲虫群落组成明显不同并存在季节变异,5月ASD与IL、SFSD和FSD生境地表甲虫群落的相异性大于8月。5月和8月SFSD生境地表甲虫活动密度均显著高于其他生境,8月FSD生境地表甲虫多样性指数显著高于其他生境。不同大小甲虫对沙漠化的响应模式不同,大中型甲虫对沙漠化的响应较小型甲虫敏感,这在5月表现尤为明显。地表甲虫与环境因子的RDA分析结果表明,12个植被和土壤环境因子解释了49.8%的地表甲虫群落变异,其中植被环境解释了甲虫群落变异的16.3%,土壤环境解释了甲虫群落变异的4.2%,植被和土壤环境相互作用解释了甲虫群落变异的29.3%。pRDA分析结果表明,草本物种丰富度、灌木盖度、土壤有机碳含量和粗砂含量是影响地表甲虫分布的主要环境因子,它们解释了43.7%的地表甲虫群落变异。Pearson相关分析表明,草本物种丰富度与地表甲虫活动密度呈显著正相关,而与地表甲虫均匀度呈显著负相关;灌木盖度与地表甲虫多样性呈显著正相关;地表甲虫物种丰富度与灌木盖度和草本物种丰富度均呈显著正相关。此外,研究还发现戈壁琵甲、克氏扁漠甲、中华砚甲和甘肃齿足象可以用于指示FSD生境,东鳖甲属昆虫可以用于指数SFSD生境,谢氏宽漠王可以用于指示IL及ASD生境。     

Gas—liquid chromatographic determination of flurazepam and its major metabolites in plasma with electron-capture detection

A sensitive and selective gas—liquid chromatographic method, using the electron-capture detector for the quantitative determination of flurazepam and its major blood metabolites is described. After extraction and back-extraction steps, flurazepam (I) is well separated from its main metabolites, N-1-hydroxyethylflurazepam (metabolite II) and N-1-desalkylflurazepam (metabolite III). Metabolite II is quantitated after forming its stable tert-butyldimethylsilyl derivative by reaction with tert-butyldimethylchlorosilane—imidazole reagent. The procedure permits the rapid and selective routine determination of flurazepam and its metabolites (II and III) in plasma with a detection limit of 3 ng/ml for flurazepam (I), 1 ng/ml for metabolite II and 0.6 ng/ml for metabolite III. The procedure is linear over the range of concentrations encountered after administration of a single oral therapeutic dose. No interference from the biological matrix is apparent. The suitability of the method for the analysis of biological samples was tested by studying the variation with time of flurazepam and its metabolites' plasma concentrations in normal human volunteers after a single, therapeutic 30-mg oral dose of flurazepam.     

利手、优势足及扣手的遗传方式初探

采用Slater区分单基因和多基因遗传的计算模式及Smith无偏分析方法对21个家系资料的分析表明：利手、优势足、扣手特征均为常染色体单基因显性遗传,R型为显性性状。虽然环境因素对这类特征的表现也有一定的影响,但遗传因素仍起主要作用。 Abstract:The data of 21 families were analyzed by the method of Slater's calculating model to differentiate between single-gene and multi-gene heredity and by the method of non-deviation analysis.The results showed that the hereditary mode of handedness or preferential foot or hand-clasping is the dominant heredity of single gene of autosome,and the right type of all of them is the dominant character.In a way,although environmental factors affected the phenotypes of these characters,hereditary factors were also the decisive ones.     

利手、优势足及扣手的遗传方式初探

采用Slater区分单基因和多基因遗传的计算模式及Smith无偏分析方法对21个家系资料的分析表明：利手、优势足、扣手特征均为常染色体单基因显性遗传,R型为显性性状。虽然环境因素对这类特征的表现也有一定的影响,但影响因素仍起主要作用。     

以MyD88 TIR二聚化为靶点的抗炎抑制剂筛选模型的建立

MyD88是IL-1R/TLR受体超家族向细胞内转导胞外信号时募集到受体胞浆尾部的重要接头蛋白．由TIR结构域介导的MyD88分子同源二聚化是它招募到受体胞浆尾部的前提,然后二聚化的MyD88再募集下游信号分子,传递信号,引发促炎基因的表达．本研究旨在建立一种模型,以实现活细胞原位的、基于荧光信号变化的MyD88二聚化抑制物的高通量筛选．我们分别构建了MyD88 TIR与GFP和RFP的融合蛋白表达质粒,瞬时转染HeLa细胞,在488 nm激发光下,转染GFP-MyD88 TIR和RFP-MyD88 TIR细胞,检测到绿色荧光与红色荧光间的共振能量转移(FRET)．而当细胞转染GFP-MyD88 TIR和RFP或RFP-MyD88 TIR和GFP,因TIR二聚化不能实现,FRET效率受到严重影响．实验结果提示,依赖双阳性表达GFP-MyD88 TIR和RFP-MyD88 TIR的细胞株,检测不同化合物对于荧光FRET效率的影响,可以建立MyD88 TIR二聚化抑制药物的筛选模型．此外,我们构建了原核表达质粒,利用纯化的His-MyD88 TIR分别与GST或GST-MyD88 TIR蛋白进行体外结合实验,发现GST-MyD88 TIR(而非GST)可以与His-MyD88 TIR相互结合．结果的差异性提示,利用His-MyD88 TIR和GST-MyD88 TIR体外结合实验分析,可以进一步确定抑制物是否直接阻断了TIR的相互作用．结合真核细胞的荧光FRET阻断结果和原核表达的重组蛋白相互作用分析,可确定MyD88 TIR二聚化的抑制物．利用这一模型可以对商品化的小分子库、自行制备的天然产物组分进行广泛的筛选,从中获得有效抑制MyD88二聚化的化合物,参与对MyD88信号通路依赖的慢性炎症、自身免疫性疾病的药物治疗．     

生物软件在序列分析过程中的运用

介绍了组合使用BLAST、FASTA/BLASTScan3.2,或用多序列比对软件,从数据库中快速提取大数量目标序列,最后用MEGA4快捷编辑整理大数量序列的方法。还介绍了一种生成核酸序列与其氨基酸序列相似性百分率整合表格的方法。简述了对引物设计的基本认识并介绍了多重引物兼容性筛选软件;对构建系统发育树的认识并引出分子进化树构建软件MEGA4的使用和PAUP 4.0常用建树命令模块。期望这些方法和软件的使用能解决生物序列分析过程的常见问题。