语丝拾粹

美国是最后的硬骨头,现在是啃的时候了。——联想集团CEO杨元庆联想集团的全球化征服计划分四步走。其一换标、收购IBM,在全球企业级市场占一定份额;其二进攻包括金砖四国在内的新兴市场;其三在欧洲、日本市场拥有一定主导地位,获得赢利能力;而第四步,即在美国市场占有一定主导地位,获得赢利能力。     

试论TRIZ理论在校企合作中的应用

TRIZ理论可以帮助研究人员快速发现问题本质,激发创新思维,打破知识领域的界限,实现技术突破。TRlZ理论对推进苏联的军事、工业、航空航天等领域科技的发展起到了巨大的作用。推进创新方法的研究和应用是我国自主创新战略的重要组成部分,受到全社会的高度重视。温家宝总理2007年7月做出“自主创新、方法先行”的重要指示。TRIZ理论的引入符合我国深入贯彻“科学发展观”的要求,具有增强自主创新能力的作用。     

万钢：紧紧抓住重大战略机遇 努力实现创新驱动发展

万钢近日在《求是》上撰文指出：面对科技创新和产业变革的新机遇新形势,我们必须按照中央要求,＂牢牢把握科技革命和产业变革与我国转变发展方式交汇的机遇,牢牢把握世界科技创新格局调整的机遇,牢牢把握经济发展水平不断提高和市场不断扩大的机遇＂,切实增强机遇意识、忧患意识和责任意识,大力提升自主创新能力,支撑经济社会又好又快发展。机遇稍纵即逝。我们要清醒地看到,     

辽河保护区治理与保护能力建设研究

辽河保护区治理与保护能力的建设,通过界碑、围栏、标示牌、宣传牌等设施建设,重点区域的水质、生态监测站点建设,保护区综合管理平台建设,应急保障体系建设,形成保护区完善的综合监控网络体系,全面提高保护区基础设施与监控能力。同时,应使全民参与对＂母亲河＂的保护。     

铁山港海草生态区水体自净能力与水、生、化之间的关系

利用2008年1月～11月间对铁山港湾海草生态区进行的4个季节全面调查所获取的数据资料,首次探讨了该生态区水体自净能力与水动力特征及生物、化学因子之间的关系。结果表明:研究海区之所以具有较强的水体自净能力,其一与该海区具有强潮型的往复流水动力特征有关,在水体自净过程中起主导控制作用;其二与海区具有适宜的水温、快速的复氧能力、富足的溶解氧(DO)水平、最适合好氧微生物繁殖生长的环境条件有关,明显偏低的总有机碳(TOC)含量和丰富的总氮(TN)储量是有机物获得快速降解、营养盐获得快速再生、化学净化能力较强的重要体现;其三与生物链作用所体现的生化过程影响有关,DO含量与生物因子多呈显著以上负相关的季节变化特征以及三种形态N与生物因子在不同季节显示的相关性以事实佐证了这一点;而富足的TN储量、显著偏低的溶解无机氮(DIN)含量与繁盛的浮游动植物生物量及丰富的生物多样性同时出现的特征,正是研究海区具有较强生物净化能力的综合体现。与化学净化能力相比,生物净化能力显示出更强的优势,具有海草生态区的水体自净特点。     

水溶性有机物电子转移能力与荧光峰强度的关系研究

以不同来源的水溶性有机物（DOM）为供试材料,采用电化学方法和荧光光谱法研究了DOM电子转移能力及其与荧光峰强度的关系.采用库仑安培法测定DOM电子转移能力,其中测得的电子接受能力为635.6～1 049.3μmol.（g.C）-1,电子供给能力为27.3～42.3μmol.（g.C）-1.利用循环伏安法研究DOM电化学活性,发现其氧化还原电位在-731～-996 mV（vs.Ag/AgCl）之间.经过电位跃阶法三次氧化还原循环后电子转移能力仍可维持在232.1～897.2μmol.（g.C）-1之间,电子循环率为36.7%～78.2%,说明DOM具有重复利用、反复转移电子的特性.采用荧光激发发射光谱法（EEMS）测定DOM的类富里酸荧光峰强度并比较其与DOM电子转移能力的关系,发现DOM的类富里酸荧光峰强度与DOM的电子循环率具有显著相关（r2=0.92）.实验结果为理解DOM在元素循环、污染物降解以及生物地球化学循环中的作用提供科学依据.     

Variation of soil fertility and carbon sequestration by planting Hevea brasiliensis in Hainan Island, China

The development of rubber industry depends on the sustainable management of rubber plantation. To evaluate the environmental effects of planting Hevea brasiliensis on a subsystem of tropical forest ecosystem, the variation of soil fertility and carbon sequestration under rubber plantation within 30-year life period were investigated in Hainan Island. Results showed that （1） with the increase of stand age of rubber plantation, soil fertility decreased all along. From 1954 to 1995, soil organic matter, total N, available K and available P decreased by 48.2%, 54.1%, 56.7% and 64.1%, respectively. （2） If the complete return of litters was considered without additional fertilizer application to the soil of the rubber plantations, the consumption periods for P, N, K, Mg were only 825 years, 329 years, 94 years and 65 years, respectively~ To improve soil fertility is essential for rubber plantation development. （3） The C sequestration of rubber trees per hectare accounts for 272.08 t within 30-year life period and 57.91% of them was fixed in litters. In comparison with C sequestration by rain forest （234.305 t/hm^2） and by secondary rain forest （150.203 t/hm^2）, rubber forest has more potentials for C fixation. On the base of above results, the following measures would benefit the maintenance of soil fertility and the development of rubber industry, including applying fertilizer to maintain the balance of soil nutrients, intercropping leguminous plant to improve soil fertility, reducing the collection of litters, optimizing soil properties to improve element P availability such as applying CaCO3. The information gathered from the study can be used as baseline data for the sustainable management of rubber plantation elsewhere.     

中国区域可持续发展综合优势能力空间关联分析

采用空间统计方法研究了中国31个省、市、自治区的可持续发展综合优势能力的空间关联关系,结果显示中国可持续发展的总资产能力、总负债能力和综合优势能力均存在较强的空间依赖性。综合优势能力Z值与总资产Z值存在显著正相关（R=0.944）,而与总负债Z值存在显著的负相关（R=-0.952）。利用综合优势能力空间关联Z值对中国可持续发展能力进行初步的分区,并采用古典聚类（K means）方法对中国可持续发展能力进行同质性研究,利用K聚类结果对空间聚类（G统计）结果进行修正,将中国可持续发展能力划分为3种区域类型：中国东部沿海强发展区域、中国中部中等发展区域和中国西部弱发展区域。分区结果与中国传统的东部、中部、西部区域划分基本对应,东部沿海省市除海南和广西处于中等发展类型外,其他省市均处在强发展类型之列,中国中部全部省市均处于中等发展类型而中国西部全部省市均处于弱发展类型。     

Methanotrophic community structure of aged refuse and its capability for methane bio-oxidation

Aged refuse from waste landfills closed for eight years was examined and found to contain rich methanotrophs capable of biooxidation for methane. Specially, community structure and methane oxidation capability of methanotrophs in the aged refuse were studied. The amount of methanotrophs ranged 61.97 103–632.91 103 cells/g (in dry basis) in aged refuse from Shanghai Laogang Landfill. Type I and II methanotrophs were found in the aged refuse in the presence of sterilized sewage sludge and only Type I methanotrophs were detected in the presence of nitrate minimal salt medium (NMS). The clone sequences of the pmoA gene obtained from the aged refuse were similar to the pmoA gene of Methylobacter, Methylocaldum, and Methylocystis, and two clones were distinct with known genera of Type I methanotrophs according to phylogenetic analysis. Aged refuse enriched with NMS was used for methane biological oxidation and over 93% conversions were obtained.     

Evaluation of adsorption capacities of humic acids extracted from Algerian soil on polyaniline for application to remove pollutants such as Cd(Ⅱ), Zn(Ⅱ) and Ni(Ⅱ) and characterization with cavity microelectrode

The adsorption capacities of new humic acids isolated from Yakouren forest (YHA) and Sahara (Tamenrasset: THA) soils (Algeria) and commercial humic acid (PFHA) on polyaniline emeraldine base (PEB) were studied at pH 6.6. Also the adsorption of heavy metals such as Cd2+, Zn2+ and Ni2+ on humic acid-polyaniline systems (HA-PEB) was investigated at the same conditions. HA-PEB compounds were characterized by scanning electron microscopy (SEM), infrared spectrometry and cavity microelectrode. In addition, batch adsorption and cavity microelectrode were used in the adsorption study of Cd2+, Zn2+ and Ni2+ on HA-PEB. To develop biocaptors of polluting metals using a cavity microelectrode modified by HA-PEB systems, the adsorption kinetic and adsorption capacity were investigated. The SEM analysis showed that the presence of humic acid affected the PEB surface and caused the formation of a granular morphology. The maximum adsorption capacities (qmax) of PFHA, THA and YHA determined by adsorption isotherms were 91.31, 132.1 and 151.0 mg/g, respectively. Batch adsorption results showed that qmax of Cd2+, Zn2+ and Ni2+ on HA-PEB followed the order: THA-PEB > YHA-PEB > PFHA-PEB. The voltammograms obtained with HA-PEB modified cavity microelectrode showed the appearance of new redox couples reflecting the adsorption of HA on PEB. Metal-humic acid-polyaniline voltammograms were characterized by appearance of oxidation-reduction couples or reduction wave corresponding to metal. Finally, the result may be exploited to develop a biocaptor based on the cavity microelectrode amended by THA-PEB and YHA-PEB.