21世纪企业的主要模式──敏捷制造企业

２０世纪９０年代以后，由于科学技术的迅猛发展，知识─技术─产品的周期日益缩短，如何加速开发质优价廉的新产品就成为企业竞争的核心内容。２１世纪即将到来，世界无疑将沿着２０世纪的道路继续向前发展，它的趋势是：新产品开发速度日益加快、产品生命周期不断缩短、生产批量越来越小、市场竞争日趋激烈；加上环太平洋地区的兴起，有能力参与这场竞争的企业不断增多。这一切虽给企业带来了机遇，但也给企业造成了严酷的生存环境。为了适应这种环境，１９９１年美国在总结日本、德国和本国经验的基础上，提出把现有企业改造成敏捷制造企业（ＡｇｉｌｅＭａｎｕｆａｃｔｕｒｉｎｇＥｎｔｅｒｐｒｉｓｅ）的模式，并认为这是奠定美国２１世纪经济霸主地位的战略举措。敏捷制造企业是从客观经济发展的实践中总结出来的。我国如何改造企业并和世界经济接轨，敏捷制造企业给我们提出了值得高度重视的发展方向，本文对此作了较为详尽的论述。

21世纪智能机器人发展预测

智能机器人是作为扩大计算机的功能和人工智能的实验床而形成和发展起来的.80年代中期基于感觉控制的智能机器人进入实用阶段.90年代将以装配机器人为先导产品,以电子、电气、精密机械制造为先导应用产业普及,特种机器人也将取得突破性的进展.本文对21世纪的下一代机器人的单元技术,应用领域及其前景作了预测.

贵州都匀牛角塘富镉锌矿床中镉的分布及赋存状态探讨

对贵州都匀牛角塘富镉锌矿的研究发现该矿床高度富集镉，矿石中镉含量一般为2284×10^-6-9850×10^-6，最高为13400×10^-6，比地壳克拉克值（0.2×10^-6)高5－6个数量级，比工业品位高n×10-n×10^2倍，且其储量达到大型矿床的规模，在世界上十分罕见。镉主要以类质同象存在于闪锌矿中，少量镉以硫镉矿等独立矿物形式存在于矿床的氧化带，是风化淋滤过程中形成的镉的次生矿物。

铅－210、钍－228、钚年代学在滇池、洞庭湖和昆明湖环境问题上的应用

笔者在大量的文献调研基础上，试图利用 ~(210)Pb、~(228)Th 等短半衰期的铀系子体确定某些湖泊沉积物的沉积速率及年代，结合 239，240 pu 在我国内陆湖泊的分布规律，以全球 pu 随时间的分布规律探索其测年的可能性，以多核素方法探讨测年结果的可靠性，建立沉积的时间尺度。同时，利用这些核素作示踪研究沉积物表层的生物扰动所造成的混合效应。通过对沉积物垂直方向上物质成份。矿物成份和元素分析，研究沉积环境的演化及近百年工业污染的历史。根据所选湖泊的纬度差别，研究湖泊沉积环境和沉积物类型对所研究的核素方法的影响。本论文是首次利用多核素方法研究我国一些内陆湖泊的环境问题，对在我国继续开展这方面研究具有重要意义。

Comparative study by infrared spectroscopy and microcalorimetry of the CO adsorption over supported palladium catalysts

The adsorption of CO on Al(2)O(3), ZrO(2), ZrO(2)-SiO(2), and ZrO(2)-La(2)O(3) supported Pd catalysts was studied by adsorption microcalorimetry and infrared (TR) spectroscopy. Some interesting and new correlations between the results of microcalorimetry and IR spectroscopy have been found. The CO is adsorbed on palladium catalysts in three different modes: multibonded (3-fold), bridged (2-fold), both on Pd(lll) and (100) planes, and linear (1-fold) adsorbed species. The corresponding differential adsorption heats lie in the field of high (210-170 kJ/mol), medium (140-120 kJ/mol), and low (95-60 kJ/mol) values, respectively. The nature of the support, the reduction temperature, and the pretreatment conditions affect the surface structure of the Pd catalysts, resulting in variations in the site energy distribution, i.e., changes in the fraction of sites adsorbing CO with specific heats of adsorption. Moreover, the CeO(2); promoter addition weakens the adsorption strength of CO on palladium. Based on the exposed results, a correctness factor, which considers the percentages of various CO adsorption states, must be introduced when one calculates the Pd dispersion using CO adsorption data.

Low temperature heat capacity of (S)-ibuprofen

Molar heat capacities of ( S)-ibuprofen were precisely measured with a small sample precision automated adiabatic calorimeter over the temperature range from 80 to 370 K. Experimental heat capacities were fitted into a polynomial equation of heat capacities ( C-p,C- m) with reduced temperature ( X), [ X = f(T)]. The polynomial equations for ( S)-ibuprofen were C-p,C- m(s) = - 39.483 X-4 - 66. 649 X-3 + 95. 196 X-2 + 210. 84 X + 172. 98 in solid state and C-p,C- m(L) = 7. 191X(3) + 4. 2774 X-2 + 56. 365 X + 498. 5 in liquid state. The thermodynamic functions relative to the reference temperature of 298. 15 K, H-T - H-298.15 and S-T - S-298.15, were derived for the( S)-ibuprofen. A fusion transition at T-m = (324. 15 +/- 0. 02) K was found from the C-p - T curve. The molar enthalpy and entropy of the fusion transition were determined to be (18. 05 +/- 0. 31) kJ.mol(-1) and (55. 71 +/- 0. 95) J.mol(-1).K-1, respectively. The purity of the ( S)-ibuprofen was determined to be 99. 44% on the basis of the heat capacity measurement. Finally, the heat capacities of ( S)-ibuprofen and racemic ibuprofen were compared.