蜜蜂褪黑素的测定方法

在脊椎动物中,褪黑素(5-甲氧基-N-乙酰色胺,MLT)是一种由松果体分泌的具有典型光周期信号作用的神经内分泌激素。近年在昆虫头部也发现了这种化学物质。该文简述了褪黑素常见测定方法,详细介绍了褪黑素的免疫测定方法RIA(radionimmunoassay),并使用该方法初步测定了中华蜜蜂ApisceranaFabricius工蜂头部褪黑素的含量,结果显示褪黑素含量与工蜂的社会分工相关。     

太湖现生介形虫

分别于1989年和2004年两次共采集了43个太湖表层沉积物样品,检查发现其中的34个样品中含有现生介形虫,共计12属15种,其中Dolerocypria taalensis,Fabae formiscandona cf.fabaeformis,Physocypria kraepelini和Darwinula stevensoni等4个种最为常见和数量最多,构成了太湖现生介形虫群中的优势成分。长期以来,国内有学者将水体矿化度180mg／l作为介形虫生存的低极限值,由此认为矿化度低于此值的太湖等水体中不存在介形虫(杨留法,1986,1992)。本次调查和国外的相关资料证明,淡水介形虫可以在矿化度低于180mg／l的水体中生存。     

代谢组学及其应用

对代谢组学的概念、特性、发展历史做了简要介绍,综述了当前代谢组学研究中的数据采集、数据分析中采用的技术,及代谢组学在疾病诊断、药物毒性研究、植物和微生物等邻域的应用,并对代谢组学的发展作了展望。     

低剂量率下高线性能量转移碳离子束辐照人类唾液腺细胞的存活效应

利用日本千叶重离子医用加速器 HIMAC 提供的碳离子束,对人类唾液腺细胞 (HSG) 在剂量率为 0.5 Gy/h 的低剂量率条件下进行了辐照,运用标准的克隆形成法得到了 3 种不同剂量平均线性能量转移 (LET) 碳离子束辐照 HSG 细胞的剂量存活效应 . 与先前 HSG 细胞在治癌剂量率 (1~5 Gy/min) 下对相近剂量平均 LET 碳离子束辐照的剂量存活效应数据相比, HSG 细胞对高 LET 碳离子束辐射表现出明显的剂量率效应 . 为在相同条件下得到碳离子束对 HSG 细胞的相对生物学效应 (RBE) ,利用 60Co-γ射线在剂量率为 0.5 Gy/h 的条件下辐照了 HSG 细胞,得到该细胞系对低 LET 射线响应的剂量存活效应 . 与先前在治癌剂量率下得到的 RBE 值相比,低剂量率条件下得到的 RBE 值总体减小 . 由实验发现的剂量率效应及低剂量率条件下 RBE 值的减小,表明由高 LET 碳离子束造成的辐射损伤在低剂量率条件下也存在着显著的修复效应 . 据此,对辐射造成细胞致死的原因进行了探讨 .     

甲基 - 苯基四氢吡啶对脑不对称小鼠纹状体内多巴胺和白介素含量的影响

为探讨甲基 - 苯基四氢吡啶 (MPTP) 注射后脑不对称小鼠纹状体内多巴胺降低程度,及纹状体内细胞因子水平变化, C57BL/6J 小鼠经过伸爪取食试验,筛选为反映脑不对称的左利鼠和右利鼠,并接受 25 mg/kg MPTP 腹腔注射连续 5 天,检测注射后的第 1 天,第 3 天和第 14 天纹状体内多巴胺及代谢物含量和细胞因子 IL-1 β、 IL-6 的动态水平 . 结果表明,无论在左利鼠还是右利鼠,纹状体内多巴胺含量在 MPTP 注射后每个检测时间点都显著降低,纹状体内 IL-1 β水平在第 1 天显著降低,纹状体内 IL-6 水平在 MPTP 注射后每个检测时间点也显著降低 . 实验结果同时表明,左利鼠和右利鼠 IL-1 β和 IL-6 的基础水平有显著不同 . MPTP 注射后,与右利小鼠相比,左利小鼠有较高的多巴胺翻转降低和较低的细胞因子表达,而且,纹状体内多巴胺水平与纹状体内 IL-6 水平呈正相关 . 这些结果提示, MPTP 诱导多巴胺丢失伴随着黑质纹状体系统内细胞因子水平的改变,而且,脑不对称有可能通过影响纹状体内细胞因子水平而进一步影响 MPTP 诱导的多巴胺降低的程度 .     

早期形态发生:一种解决贻贝科(软体动物门:双壳纲)分类、系统发育和进化问题的方法

作者对贻贝科贝类的幼虫和幼贝期发育阶段形态结构的出现和变化顺序进行了研究,其约60个不同分类单元的个体发生可归纳为4种形态发生类型或模式。主要对3个形态发生区域的阶段形态结构的起源、发育变化和同源性做了研究。其一,即中央区域,开始形成于前双壳Ⅰ期(PD-Ⅰ),在某个分类单元它可以在前双壳Ⅱ期(PD-Ⅱ)和幼贝期(N)形成,而在其它分类单元则在前双壳Ⅱ期、幼贝期和双壳期(D)形成;第二区域,即背部后区,在幼贝期出现;第三区域,即背部前区,出现于双壳期。双壳期背部后区在某个分类单元起源于幼贝期的形态构造,在其它分类单元则可能起源于双壳期的形态构造。与在贻贝分类学上应用的成体特征相比,早期发育阶段中央和背部后区的形态结构显示出很明显的发育顺序或特征变化规律。根据以前人们熟知而尚未应用到分类和系统发育研究中的早期发育阶段形态特征,作者重新修订了Soot-Ryen的现生贻贝科种上阶元分类系统,重新提出了科内系统发育关系。修订的分类系统表明,Scarlato and Starobogatov(1984)提出的贻贝科各亚科由偏顶蛤亚科开始,沿4条系统发育路线演化发展,对应其早期发育阶段的4类形态发生类型或模式。     

A novel mutation at the JK locus causing Jknull phenotype in a Chinese family

Jk (kidd) blood group antigens are carried by the urea transporter UT-B[1,2]. The Jknull phenotype, lack-ing urea permeability in erythrocytes[3,4], has a very low frequency in all populations except Polynesians and Finns[5]. In Japan, only 14 individuals with Jk (a-b-) phenotype were identified from 638460 screened donor’s blood samples using the 2 mol/L urea solution hemolysis test[6]. The frequency of Jknull is 0.27% in Polynesian, about 0.03% in Finland[7], and extremely rare in Fran…     

Tyroserleutide tripeptide affects calcium homeostasis of human hepatocarcinoma BEL-7402 cells

Copyright by Science in China Press 2005 Primary hepatocarcinoma is one of the most fre-quent digestive-tract cancers, particularly in China. The incidence and death rate of primary hepatocarci-noma in China is the highest in the world, with about 1100 thousands people dying from primary hepatocar-cinoma per year[1]. Although the chemotherapeutic agents are the main therapeutic approach for hepato- carcinoma, they are relatively ineffective and result in many toxic and side effects. Accordin…     

Capitalizing on multi-element interactions through bal-anced nutrition——A pathway to improve nitrogen use efficiency in China,India and North America

A viable option for increasing nitrogen (N) use efficiency and mitigation of negative impacts of N on the environment is to capitalize on multi-element interactions through implementation of nutrient management programs that provide balanced nutrition. Numerous studies have demonstrated the immediate efficacy of this approach in the developing regions like China and India as well as developed countries in North America. Based on 241 site-years of experiments in these countries, the first-year N recovery efficiency (RE) for the conventional or check treatments averaged 21% while the balanced treatments averaged 54% RE, for an average increase of 33% in RE due to balanced nutrition. Effective policies to promote adoption are most likely those that enable site-specific approaches to nutrient management decisions rather than sweeping, nation-wide incentives supporting one nutrient over another. Local farmers, advisers and officials need to be empowered with tools and information to help them define necessary changes in practices to create more balanced nutrient management.     

Surface N balances and reactive N loss to the environment from global intensive agricultural production systems for the period 1970-2030

Data for the historical years 1970 and 1995 and the FAO-Agriculture Towards 2030 projection are used to calculate N inputs (N fertilizer, animal manure, biological N fixation and atmospheric deposition) and the N export from the field in harvested crops and grass and grass consumption by grazing animals. In most industrialized countries we see a gradual increase of the overall N recovery of the intensive agricultural production systems over the whole 1970-2030 period. In contrast, low N input systems in many developing countries sustained low crop yields for many years but at the cost of soil fertility by depleting soil nutrient pools. In most developing countries the N recovery will increase in the coming decades by increasing efficiencies of N use in both crop and livestock production systems. The surface balance surplus of N is lost from the agricultural system via different pathways, including NH3 volatilization, denitrification, N2O and NO emissions, and nitrate leaching from the root zone. Global NH3-N emissions from fertilizer and animal manure application and stored manure increased from 18 to 34 Tg·yr-1 between 1970 and 1995, and will further increase to 44 Tg·yr-1 in 2030. Similar developments are seen for N2O-N (2.0 Tg·yr-1 in 1970, 2.7 Tg·yr-1 in 1995 and 3.5 Tg·yr-1 in 2030) and NO-N emissions (1.1 Tg·yr-1 in 1970, 1.5Tg·yr-1 in 1995 and 2.0 Tg·yr-1 in 2030).