从地理学观点看服务经济的发展

本文的目的,是研究服务经济的发展及由此引起的从工业经济向工业后经济的过渡。我们从国际观点出发进行这项研究工作,对三大洲7个工业化大国(美国、加拿大、英国、法国、西德、意大利和日本)的服务经济进行了研究和比较。什么是服务业?服务业发展演化成为一个独立的经济部门,最早是由克拉克[clark]和费希尔[Fisher]提出来的。     

东南亚锡矿带锡石多色性的特征和意义

东南亚锡矿带长约3900km,从缅甸和泰国大陆起,一直延伸到印度尼西亚群岛(见图).矿带由东带和西带组成,两带近于平行,局部为断层错开. 在此矿带内,锡矿床与花岗岩伴生,西带虽有些晚期浅成花岗岩,但中成花岗岩占优势,东带则以浅成花岗岩为主.因此,两带花岗岩之间存在着明显的矿物学差异(Hutchison,1975);同时,西带花岗岩中痕量元素的分布模式也与东带截然不同(Yeap,1974).这两个带的花岗岩有着长期而复杂的历史,每个带中都产有时代显然不同的花岗岩.不     

亚洲城市平衡化、空间一体化及经济发展的政策和规划

对亚洲许多城市规划专家和政策分析家们来说,城市化至今仍是一件高深莫测的事。过去的三十年里,迅速发展的东亚和东南亚的城市化,被描绘成经济增长的促进因素、现代化的产物、严重社会问题的根源以及阻碍财富合理分配的绊脚石。     

Sublethal effect of naphthalene on lipid peroxidation and antioxidant status in the edible marine crab Scylla serrata

The effect of naphthalene on lipid peroxidation and antioxidants status was studied in hepatopancreas, haemolymph and ovary of the Scylla serrata with reference to the active vitellogenic stage. There was an overall increase in lipid peroxidation activity in the tested samples. In contrast, the enzymatic (catalase, glutathione peroxidase, superoxide dismutase) and non-enzymatic antioxidants (vitamins C, E and glutathione) showed decreased activities for hepatopancreas, haemolymph and ovary.     

Identification of heterogeneous aquifer transmissivity using an AE-based method

Determination of hydraulic head, H, as a function of spatial coordinates and time, in ground water flow is the basis for aquifer management and for prediction of contaminant transport. Several computer codes are available for this purpose. Spatial distribution of the transmissivity, T(x,y), is a required input to these codes. In most aquifers, T varies in an erratic manner, and it can be characterized statistically in terms of a few moments: the expected value, the variance, and the variogram. Knowledge of these moments, combined with a few measurements, permits one to estimate T at any point using geostatistical methods. In a review of transmissivity data from 19 unconsolidated aquifers, Hoeksema and Kitanidis (1985) identified two types of the logtransmissivity Y= ln(T) variations: correlated variations with variance sigma2Yc and correlation scale, I(Y), on the order of kilometers, and uncorrelated variations with variance sigma2Yn. Direct identification of the logtransmissivity variogram, Gamma(Y), from measurements is difficult because T data are generally scarce. However, many head measurements are commonly available. The aim of the paper is to introduce a methodology to identify the transmissivity variogram parameters (sigma2Yc, I(Y), and sigma2Yn) using head data in formations characterized by large logtransmissivity variance. The identification methodology uses a combination of precise numerical simulations (carried out using analytic element method) and a theoretical model. The main objective is to demonstrate the application of the methodology to a regional ground water flow in Eagle Valley basin in west-central Nevada for which abundant transmissivity and head measurements are available.     

Are Taxonomic Distinctness measures compliant to other ecological indicators in assessing ecological status?

Assessing the ecological status, a concept implemented in the European Water Framework Directive [EC, 2000. Directive of the European Parliament and of the Council 2000/60/EC establishing a framework for community action in the field of water policy PE-CONS 3639/1/00, p. 72], requires the application of methods capable of distinguishing different levels of ecological quality. The Average Taxonomic Distinctness has been used as tool in this context, and we tested the robustness of Taxonomic Distinctness measures applying it in different scenarios (estuarine eutrophication, organic pollution, and re-colonisation after physical disturbance), analysing simultaneously its compliance to other types of ecological indicators. Results show that, in most of the case studies, only Total Taxonomic Distinctness was relatively satisfactory in discriminating between disturbed situations. Other Taxonomic Distinctness measures have not proved to be more sensitive than other ecological indicators (Shannon-Wiener, Margalef, and Eco-Exergy indices). Therefore, this approach does not seem to be particularly helpful in assessing systems' ecological status with regard to the WFD implementation.