小球藻对U(VI)的生物吸附特性

试验研究了小球藻吸附U(VI)的过程, 探讨了吸附机理、吸附热力学和动力学。考查了pH值、时间、U(VI)的起始浓度和温度等对吸附的影响。研究表明, pH值对小球藻的吸附效果影响较大, 小球藻吸附U(VI)的最佳pH值为6, 最大吸附量为2.7 mg/g, 吸附在5 min内基本达到平衡。小球藻对U(VI)的吸附量与其浓度的正相关; 温度在20℃~30℃时, 对铀的吸附影响不大。实验结果还表明, 吸附过程符合准二级动力学方程, 其相关系数达0.99, 该吸附为多种反应同时作用的复杂过程。U(VI)在小球藻上的吸附行为可以很好地用Langmuir等温方程来描述。     

蛋白核小球藻对Pb(Ⅱ)和Cd(Ⅱ)的生物吸附及其影响因素

藻类吸附作用影响重金属在水生生态系统中的迁移过程及其环境行为。同时,利用藻类吸附能力是修复重金属污染水体和重金属废水处理的一项清洁、廉价和高效的技术。测定了蛋白核小球藻对Pb2+和Cd2+的吸附和脱附动力学,表明吸附是快速表面过程,吸附4 h后基本达到平衡,不易脱附。研究了蛋白核小球藻对Pb2+和Cd2+的吸附热力学,绘制了吸附等温线,并用Langmuir模型进行拟合,相关系数R2分别为0.9906和0.9827,计算得到最大吸附量分别为0.373 mmol Pb/g和0.249 mmolCd/g。考察了pH值、离子强度和温度等环境因素对蛋白核小球藻吸附Pb2+和Cd2+的影响。结果表明,蛋白核小球藻对Pb2+和Cd2+的吸附量在pH值5.0—6.0之间达到最大值,并随着溶液离子强度的增加而降低,随着溶液温度的升高而增加。温度的影响还表明,蛋白核小球藻对Pb2+和Cd2+的吸附是吸热过程。实验还考察了水体环境中普遍存在的溶解性有机质主要成分-富里酸的影响,表明富里酸会抑制蛋白核小球藻对Pb2+和Cd2+的吸附,重金属离子浓度较低时的抑制效果更明显,最大抑制率分别达到了34.2%和34.9%。由于其对重金属的较高吸附量和吸附本身快速完成的特性,蛋白核小球藻有望成为较理想的生物吸附剂,在重金属污染水体的生物修复及废水处理中发挥重要作用。     

小球藻吸附镍离子的研究

在小球藻液中分别添加含不同浓度的Ni^2 ,NH4^ N,PO4^3--P溶液,研究小球藻吸附Ni2 的能力。实验结果表明,小球藻对Ni^2 的生物吸附经历了一快一慢两个过程。随着Ni^2 的浓度的增加,小球藻对Ni^2 的吸附量不断增加,在最佳pH为8.0-8.5的条件下,低氮磷浓度的组合,升高温度或加强光照有利于小球藻对Ni^2 的吸附。20℃和30℃下,小球藻对Ni^2 的吸附符合Fluendlich等温模型,小球藻在对数生长期时对Ni^2 的富集能力最强。     

小球藻吸附水中Pb2+影响因素的初步研究

对小球藻生物吸附水中Pb2 + 的影响因素作了初步研究。实验表明 :在小球藻处于指数生长期和静止期时加入Pb2 + ,去除率达 6 0 %以上 ;当藻细胞密度一定时 ,随着Pb2 + 浓度的增加 ,Pb2 + 的去除率增大 ;当Pb2 + 浓度一定时 ,随着藻细胞密度的增加 ,小球藻对Pb2 + 的去除率增大 ,藻细胞密度为 1 2 9× 10 8个 /ml时 ,去除率可达 92 82 % ;加强光照可以促进小球藻对Pb2 + 的吸附 ;在pH值为 5～ 10的范围内 ,pH对Pb2 + 吸附影响不大 ,较佳的pH值在 7左右。实验最佳条件的去除率在 90 %以上 ,去除效果较好。     

活性小球藻对铅离子的吸附与解吸特征研究

研究了活性小球藻对Pb^2＋的生物吸附、解吸及其机理。结果表明,培养至指数生长期的小球藻对Pb^2＋的吸附能力最强,吸附率可达75％。吸附液的pH值在7左右,小球藻对Pb^2＋有较好的吸附作用,吸附率可达80％。吸附的动力学实验表明,在小球藻对Pb^2＋吸附的起始阶段,吸附速度较快,10min即可达到平衡。研究还表明,加强光照可以促进小球藻对Pb^2＋的吸附在一定的浓度范围内,小球藻对Pb^2＋的吸附符合Freundlich等温吸附模型。在解吸实验中,用EDTA和HCI作为解吸剂的解吸率可分别达到近80％和60％,可以有效解吸被吸附的Pb^2＋。     

小球藻对水溶液中Zn2+、Cd2+的吸附

对小球藻生物吸附Zn^2 ,Cd^2 的影响因素进行了研究,发现小球藻对Zn^2 ,Cd^2 的生物吸附主要经历了快速的物理吸附和缓慢的化学吸附两个步骤;pH值是影响Zn^2 ,Cd^2 生物吸附的一个重要因素,pH值为6-7时,小球藻对Zn^2 ,Cd^2 的去除率较高,在实验条件下去除率可达87%以上;研究还表明,小球藻干粉比新鲜藻能富集更多的Zn^2 ,Cd^2 。用Freundlich方程模拟吸附等温线,拟合良好。     

光照强度、温度、pH、盐度对小球藻(Chlorella)光合作用的影响

利用测定净光合放氧速率的方法研究了光照强度、温度、pH、盐度对小球藻(Chlorella sp.XQ-200419)和海洋小球藻(Chlorella marina NJ-016)光合作用的影响。小球藻(Chlorella sp.XQ-200419)的适宜光照强度范围为100～1600μmo·lm-2·s-1,光饱和点在500μmo·lm-2·s-1附近;适宜温度范围为25～42.5℃,最适温度为37.5℃;适宜pH值范围为6.5～9.0,最适pH值为7.0;对盐度的适应范围较广,在0～0.6mol/L范围内,随着盐度的升高,净光合放氧速率有下降趋势。海洋小球藻(Chlorella marina NJ-016)的适宜光照强度范围为400～1600μmol·m-2·s-1,光饱和点在1400μmo·lm-2.s-1附近;适宜温度范围为25～42.5℃,最适温度为37.5℃;适宜pH值范围为5.0～9.0,最适pH值为8.0;对盐度有很好的适应性,在0～0.6mol/L范围内,随着盐度升高,净光合放氧速率明显上升。小球藻和海洋小球藻的净光合放氧速率随光照强度、温度、pH值和盐度变化的规律,表明了两种小球藻的基本生理生态学特性:能适应较强的光照强度、较高的温度、中性偏碱的环境和较高的盐度。研究结果有助于小球藻培养条件的优化。两种小球藻对光照强度、温度、pH值和盐度变化的反应也有所不同:与小球藻(Chlorella sp.XQ-200419)相比,海洋小球藻(Chlorella marina NJ-016)对光照强度有更好的适应性,对pH值变化有更宽的适应范围,适当提高盐度对其光合作用有明显的促进作用。这表明海洋小球藻(Chlorella marina NJ-016)在快速生长繁殖方面具有更大的潜力,这一研究结果为筛选适合于大量培养的优良藻种提供了依据。     

小球藻对镉离子的吸附速率方程

研究了小球藻对Cd^2 的吸附动力学。研究表明,小球藻对Cd^2 有一定的吸附作用,在吸附的起始阶段,吸附速率较快,且随温度的升高吸附速率增大,吸附过程在20min内达到平衡。结果还表明,该吸附是简单的一级反应,并由此建立了吸附反应的速率方程,推算出吸附反应的活化能Ea=31．42kl／mol。     

根霉吸附水体中重金属铬与吸附机理的研究

以根霉RhizopusLH2死菌体为吸附剂进行水体中六价铬的吸附研究.结果表明,Cr(VI)的生物吸附最优条件为:温度28℃,pH为2;线性回归相关系数为0.98,符合Langmuir吸附等温线模型;傅立叶红外变换光谱分析推断吸附机理为质子化氨基在Cr(VI)的生物吸附中起主要作用.     

普通小球藻对复合重金属镉和铬的生物吸附及影响因素

【背景】微藻对重金属具有极强的耐受性,而且有较高的吸附率,是一种优良的生物吸附剂。【目的】探究环境因素对小球藻吸附镉离子(Cd²⁺)和铬离子(Cr³⁺)的影响。【方法】以普通小球藻（Chlorella vulgaris）在不同条件下对重金属离子的吸附率为基准,利用CdCl₂·2H₂O和CrCl₃·7H₂O提供重金属离子,根据不同处理下小球藻吸附率的变化情况探讨重金属离子浓度、p H和温度等环境因素对普通小球藻吸附Cd²⁺和Cr³⁺的影响。【结果】在温度为30°C、p H值为5.5、Cd²⁺和Cr³⁺浓度分别为0.4 mg/L和4.0 mg/L及生物量为0.59 g/L的条件下,普通小球藻对复合Cd²⁺和Cr³⁺吸附率达到最大,吸附率分别达到84.5%和75.2%,同时发现普通小球藻对Cd²⁺的吸附率大于C...     

Recent advances in the study of Kaposi's sarcoma-associated herpesvirus replication and pathogenesis

It has now been over twenty years since a novel herpesviral genome was identified in Kaposi's sarcoma biopsies. Since then, the cumulative research effort by molecular biologists, virologists, clinicians, and epidemiologists alike has led to the extensive characterization of this tumor virus, Kaposi's sarcoma-associated herpesvirus(KSHV; also known as human herpesvirus 8(HHV-8)), and its associated diseases. Here we review the current knowledge of KSHV biology and pathogenesis, with a particular emphasis on new and exciting advances in the field of epigenetics. We also discuss the development and practicality of various cell culture and animal model systems to study KSHV replication and pathogenesis.     

The structure, reproduction and taxonomy of Vidalia and Osmundaria (Rhodophyta, Rhodomelaceae)

Comprises species occurring mostly in subtidal habitats in tropical, subtropical and warm-temperate areas of the world. An analysis of the type species, V. spiralis (Sonder) Lamouroux ex J. Agardh, a species from Australia, establishes basic characters for distinguishing species in the genus. These characters are (1) branching patterns of thalli, (2) flat blades that may be spiralled on their axis, (3) width of the blade, (4) primary or secondary derivation of sterile and fertile branchlets and (5) position of sterile and fertile branchlets on the thalli. Application of the latter two characters provides an important basic method for separation of species into three major groups. Osmundaria , a genus known only in southern Australia, was studied in relation to Vidalia , and its separation from the Vidalia assemblage is not accepted. Species of Vidalia therefore are transferred to the older genus name, Osmundaria. Two new species, Osmundaria papenfussii and Osmundaria oliveae are described from Natal. Confusion in the usage of the epithet, Vidalia fimbriala Brown ex Turner has been clarified, and Vidalia gregaria Falkenberg, described as an epiphyte on Osmundaria pro/ifera Lamouroux, is revealed to be young branches of the host, Osmundaria prolifera.     

New or rare chromosome counts in Artemisia L. (Asteraceae, Anthemideae) and related genera from Kazakhstan

Fifteen chromosome counts of six Artemisia taxa and one species of each of the genera Brachanthemum, Hippolytia, Kaschgaria, Lepidolopsis and Turaniphytum are reported from Kazakhstan. Three of them are new reports, two are not consistent with previous counts and the remainder are confirmations of very scarce (one to four) earlier records. All the populations studied have the same basic chromosome number, x = 9, with ploidy levels ranging from 2x to 6x. Some correlations between ploidy level, morphological characters and distribution are noted.     

肝癌中HBV和HCV基因和抗原的分布及意义

采用原位分子杂交方法检测HCV RNA及HBV X基因;采用免疫组织化学方法研究HCV核心抗原,非结构区C33c抗原及HBxAg在肝细胞肝癌中的定位及分布.结果表明(1)HCV RNA、HBV X基因在肝细胞肝癌组织检出率分别为40%(55/136)和82%(112/136).HCV RNA定位于癌细胞的胞浆内,阳性细胞呈散在、灶状及弥漫分布三种形式;HBV X基因在肝癌细胞中的分布呈胞浆型、核型及核浆型,阳性细胞也呈上述三种分布形式;(2)HCV C33c抗原、核心抗原在肝细胞肝癌中的阳性率为81%(133/164)及86%(141/164).C33c抗原定位于癌细胞及肝细胞的胞浆内;核心抗原既定位于癌细胞核中,又可定位于胞浆中.C33c抗原阳性细胞以灶状分布为主;而核心抗原阳性细     

Selection with two alleles and complete dominance

For a plant selection model with frequency-independent viabilities, fertilities and selfing rates, it is shown that apart from global fixation, for certain parameter combinations a protected polymorphism and facultative fixation (either allele may become fixed according to initial frequencies) may both occur. Facultative fixation requires different selling rates for the dominant and recessive type. Protection of the polymorphism requires resource allocation for male and female function. In this connection the problem of purely genetically caused population extinction is discussed.
For general frequency dependence and regular segregation, the chances for establishment of a completely recessive gene are compared to those of a completely dominant gene. It is proven that the process of establishment of the recessive gene, despite a fitness advantage, may be considerably endangered by drift effects if random mating prevails. The recessive gene may reach the same effectivity in establishment as a dominant gene, only if the recessive homozygote mates exclusively with its own type during the period of establishment.