原核表达的人乙醛脱氢酶2(ALDH2)的活性及稳定性研究

对由原核载体表达的人乙醛脱氢酶2(Aldehyde dehydrogenase 2,简称ALDH2)纯化工艺、酶活性改善、稳定性以及保存条件分别进行了参数的优化,以期为ALDH2商品化剂型开发提供理论依据。通过NAD(P)+酶活测定法,检测不同纯化工艺、金属离子以及不同保存条件对ALDH2的酶活性的影响。通过SDS-PAGE检测ALDH2在模拟胃液和胰液中的稳定性。结果显示,低离子磷酸盐缓冲液透析有利于ALDH2酶活性的恢复,且真空冷冻干燥处理可导致ALDH2酶活性下降。K+、Zn2+、Mg2+、Mn2+、Ca2+均能提高ALDH2酶活性。ALDH2在模拟胃液中稳定性良好,但在模拟胰液中迅速被降解。与此同时,ALDH2酶液在-20℃下能良好地保持其稳定性及酶活,但在4℃和30℃下保存一个月酶活急剧下降。以上结果表明,低离子磷酸盐缓冲液透析法、K+均能提高ALDH2的酶活性,同时该酶可耐受模拟胃液的降解作用,且添加山梨酸钾的ALDH2于-20℃可良好地保持其稳定性及酶活。     

单抗药物专题报告——走过孕育期，收获正当时（Ⅰ）

单抗药物以靶向性强、特异性高、副反应小等优势在癌症、自身免疫性疾病等治疗领域取得了快速发展,成为医药行业增速最快的 细分领域。报告采用文献调研、数据库检索、数据统计与分析等定性定量研究方法,从竞争优势、应用领域、给药剂型、产业现状、成长 路径等角度对国内外单抗药物领域进行多角度、多层次的分析,旨在为相关医药企业明确发展方向、确定产品研发思路及制定市场策略提 供参考。     

浮游细菌群落变化对锥状斯氏藻藻华的影响

目的:本实验以大亚湾原发性锥状斯氏藻为例,采集野外样品,分析藻华不同时期主要菌群的结构和环境样品的硫化物与赋存形态。方法:应用末端限制性片段长度多态性技术和主成分分析方法,分析藻华发生过程中浮游细菌群落相似程度的情况,得到差异显著的浮游细菌类群。选出代表类群的样品进行16S r DNA高变区测序,获取浮游细菌的分类结果及相对丰度。采用Pearson相关性分析浮游细菌、藻、硫化物两两间的相互关系。结果:早期藻华以Enterobacteriaceae为主导,各优势菌群(Enterobacteriaceae:Alteromonadaceae:Rhodobacteraceae)的比例约为8:1:21,硫元素主要以DMS形式存在;而后期Alteromonadaceae成为优势物种,各优势菌群的比例转变为3:5:25,硫的赋存形态由DMS转变为DMSO;Rhodobacteraceae在藻华的前期与后期均以优势种存在。本实验还发现藻华不同时期4种与藻呈正向相关的细菌,以及8种对藻起负向调节作用的细菌,它们在藻华生消的过程中扮演着不同的角色。结论:菌群的组成性改变与藻华生消具有一定的相关性,并对藻类的硫代谢产生影响。结果的获得有助于认识藻华微生物学过程中硫代谢的生态学功能,拓展锥状斯氏藻藻华的理论认识。     

西藏独一味属一新变型——白花独一味

描述了唇形科独一味属植物独一味[Lamiophlomis rotato.(Benth.ex Hook.f.)Kudo]的1个新变型--白花独一味[Lamiophlomis rotata(Benth.ex Hook.f.)Kudo f.dlbiflora J.Luo et S.L.Wang].原变型的花冠为淡紫色、红紫色或粉红褐色,而新变型花瓣为白色,花萼为绿色.     

低温胁迫对灰飞虱种群生长发育与繁殖的影响

为了探讨低温在灰飞虱Laodelphax striatellus(Fallén)种群发生发展中的作用,本文以南京冬季的旬平均最低温为依据,设定出-6～2℃的低温,研究了用该低温处理3～4龄若虫不同时间后,灰飞虱的存活、生长与繁殖特性。结果表明,灰飞虱3～4龄若虫有较强的耐低温能力,-6～2℃的温度下,其半致迷和半致死时间分别为1.22和20.49d。低温抑制了若虫的生长发育,发育历期明显延长。低温处理后成虫的性比有所提高,并且短翅率显著增加。3～4龄若虫低温处理1～7d后羽化的成虫有产卵前期缩短、寿命延长的趋势,但对繁殖力没有显著影响,并且低温处理2d后的产卵量要稍高于没有处理的对照。由此可见,-6～2℃低温的短期胁迫对灰飞虱种群的发生发展不会产生抑制作用。     

Community‐level changes in Australian subalpine vegetation following invasion by the non‐native shrub Cytisus scoparius

Question: What are the changes associated with the recent invasion by the non‐native legume, Cytisus scoparius? Location: Subalpine vegetation (1500 m a.s.l.) in Australia. Methods: We used multivariate techniques and regression analyses to assess vegetation and environmental changes across six study sites. Vegetation and environmental variables were investigated at three different stages of invasion: (1) recent invasion (8–10 yr), (2) mature invasion (15–16 yr) and (3) long‐term invasion (25 yr). Results: Substantial changes in floristic composition and species richness were evident after 15 yr and these changes became more pronounced after 25 yr. Changes due to invasion were associated with a dramatic loss of native species or a reduction in their abundance. No ‘new species’ were evident under invaded stands. Forbs were most affected by the establishment of C. scoparius, although all growth forms responded negatively. Dense canopy shading and an increasingly dense, homogeneous litter layer in the understorey as a result of C. scoparius were strong environmental drivers of vegetation change. Greenhouse studies confirmed the importance of these processes on the germination and growth of two native species. Conclusions: This study highlights the potential for C. scoparius to alter both vegetation and environmental processes in the subalpine region.     

Ecology of pollination in a tropical Venezuelan savanna

Pollination modes ecology of a total of 164 plant species was evaluated according to habitats and plant life forms in the Venezuelan Central Plain. Frequency distribution of nine pollination modes showed that, at the community level bee pollination (38.6%) was dominant. Butterfly (13.9%), fly (12.7%), and wasp (10.8%) pollination were the second most frequent. Moth (6.2%) and wind (10.4%) pollination occurred with similar frequency, and the least common were bird (3.1%), beetle (2.3%) and bat (1.9%) pollination. There was a significant interaction effect indicating that pollination mode was affected by the type of habitat. Bee pollination was the most common pollination mode in all habitats with butterfly, fly and wasp pollination being secondary for forest and forest-savanna transition; and butterfly, wasp, wind and fly pollination being secondary for savanna. Wind, butterfly and fly pollination were found in disturbed areas as secondary pollination modes. Pollination modes were significantly associated and affected by life forms. Bee pollination was dominant in all life forms with wasp, butterfly and fly pollination being the secondary for trees, shrubs, and lianas; and butterfly and wind pollination being the secondary for herbaceous species. The number of pollination modes (richness) among life forms ranged between four and nine for epiphytes and perennial herbs respectively. The highest values of diversity indexes among life forms were found in trees and shrubs. The richness and diversity indices of pollination modes were statistically higher for more structured habitats, forest and forest-savanna transition, than herbaceous habitats, savanna and disturbed areas, which is associated with the highest values of diversity indexes in trees and shrubs. Equitability was higher for forest and disturbed areas than forest-savanna transition and savanna. The results of comparative richness, equitability, diversity indices, and the frequency distribution of pollination modes of 19 samples from tropical and temperate communities indicated that richness of pollination modes may be different between tropical and temperate communities. The proportion of each pollination mode suggests four grouping: (1) rain forests and their strata, (2) grassland savanna, and associated disturbed areas, (3) temperate communities, and (4) the most heterogeneous group, contained mostly neotropical communities, including the four habitats of the Venezuelan Central Plain. The frequency of pollination modes, richness, diversity and equitability of communities, habitats, successional stages, and vegetation strata varies with respect to geography, vegetation structure, and plant species richness.     

Pollination specialization and time of pollination on a tropical Venezuelan plain: variations in time and space

Levels of specialization of the pollination systems were evaluated in 155 plant species from the Venezuelan Central Plain. In all, 29 pollination systems were found, resulting from various combinations of nine pollen‐vector types or pollinating agent classes. The number of pollen‐vector types composing a pollination system ranged from one to five. Ninety‐one species were pollinated by only a single pollen‐vector type; the frequency of pollination systems fell monotonically with increasing number of constituent pollen‐vector types. Some 30–40 per cent of bee‐, moth‐, beetle‐ and bat‐pollinated species were pollinated by that group of vectors alone. The highest incidence of co‐occurrence between pollen‐vector types was found for the combinations fly–wasp, butterfly–wasp, butterfly–fly, and to a lesser extent bird–butterfly, bat–bird, bat–moth and butterfly–moth. The average number of pollen‐vector types per plant species was significantly higher for trees and shrubs than for lianas and perennial herbs. The distribution of polyphily, oligophily, monophily and anemophily was significantly associated with life form and habitat. The relative frequencies of these types varied least through the year in the forest‐savannah ecotone and in the vegetation as a whole, reflecting the combination of life forms. There were significantly fewer night‐pollinated than day‐pollinated species. Day‐pollinated species tended to be polyphilous, and most of the night‐pollinated species were monophilous or oligophilous. Time of pollination activity was related to habitat. The relative importance of night pollination among life forms decreased from trees to perennial herbs. Plant species exclusively pollinated during the night reached a peak during the rainy season (May to November) for trees, lianas and perennial herbs. The data as a whole show that the relative frequency of polyphily, oligophily, monophily and anemophily, and the time of pollination activity are influenced by community structure and plant species richness, and may change from season to season. © 2004 The Linnean Society of London, Botanical Journal of the Linnean Society, 2004, 145 , 1–16.