中国数字地震台网（CDSN）数据管理中心（DMC）计算机网络系统

介绍了经过第二期技术改造后的中国数字化地震台网（ＣＤＳＮ）数据处理中心（ＤＭＣ）的计算机网络和远程通信系统的硬件和软件配置情况。     

新一代系统CDSN应用地震数据的格式及其使用方法

ＣＤＳＮ正处在更新换代的重要时期，为了使广大地震研究人员更好地应用ＣＤＳＮ资料，本文详细叙述了更新的ＣＤＳＮ地震事件数据格式，提出了新数据与已发行数据格式相兼容的办法，同时说明了有关格式转换程序的使用方法。     

CDSN台站用C语言调用ORACLE数据库的震级计算软件

新一代ＣＤＳＮ台站的地震信息管理,采用ＯＲＡＣＬＥ关系数据库系统。该系统主要由ＯＲＡＣＬＥ的核心,ＳＱＬ＊ＰＬＵＳ接口及各种实用程序组成（图１）。台站ＳＵＮ工作站系统配置的ＡＲＳ软件,是分析处理数字化地震资料的较为理想的应用软件。支持该软件的就是ＯＲ...     

陕西交道全新世黄土-黑垆土磁化率的CBD研究

根据黄士高原中部交道剖面全新世黄土－黑垆土剖面的非磁滞磁化率和ＣＢＤ提取前后的磁化率、频率磁化率以及热磁分析结果,分析了磁性矿物的种类和磁畴状态,讨论了古土壤的磁化率增强,指出ＣＢＤ技术强有力的支持古土壤磁化率增强的土壤成因观点．虽然ＣＢＤ能非常有效地溶解土壤成因的磁赤铁矿,但并不是完全选择性地溶解土壤成因的磁铁矿颗粒．此外,通过对样品ＣＢＤ处理前后磁化率数据的分析,从土壤化学角度为黄土的风成说提供了新证据。     

西园隧洞引水工程对滇池CODMn的影响分析

本文在滇池湖流特性研究的基础上,建立了滇池平面二维ＣＯＤＭｎ输移扩散数学模型, 模型对污染物进入滇池水体后的输移扩散规律进行模拟分析,对滇池周围西园隧洞引水工程第一系列污染控制工程措施对滇池主要污染指标ＣＯＤＭｎ的影响进行评价,为综合治理滇池提供了理论依据。     

ARS软件滤波器在CDSN台站中的扩展应用

在ＣＤＳＮ台站用数字滤波方法对数字地震仪进行抑制噪声滤波,方法简单易行。通过震例检验,把本人新创造的滤波器用ＡＲＳ软件中含有的滤波器相结合,对地震信号的识别有一定的参考意义,有助于提高编辑地震报告的Ｐ波利用率。     

一种BASIC通用菜单驱动程序的设计

在对ＣＣＤＯＳ汉字操作系统和ＢＡＳＩＣ语言特点的认真分析和处理后，得到了一个良好的通用菜单驱动程序，它完全可在不加改动或很少改动的情况下应用以汉字ＣＣＤＯＳ为操作系统的各种菜单驱动程序中。     

一种便携式高分辨率康普顿背散射扫描仪

兰博集团开发生产的ＬＢＤ１０１型康普顿背散射扫描仪（ＣＢＳ），可以由被测物的单侧进行检查，广泛用于工业领域的无损检测（ＮＤＴ）和无损评价（ＮＤＥ）。这种新仪器采用非常简单而紧凑的单源和单探测器系统。其扫描范围为２００ｍｍ（Ｘ向）×２００ｍｍ（Ｙ向）×１００ｍｍ（Ｚ向或深度），用自动升降装置可调节检测高度为２００ｍｍ～２０００ｍｍ。ＬＢＤ１０１优越的技术指标包括：最高的空间分辨率优于０．８ｍｍ，最好的密度分辨率约为１％，最小可探测的缺陷体积小于０．６ｍｍ３，最小可探测的缺陷大小为０．８，最小可探测裂纹宽度为０．１５ｍｍ。辐射防护安全性能好，辐射剂量率非常低。本文摘要并详细比较了ＣＯＭＳＣＡＮ１６０和ＬＢＤ１０１型ＣＢＳ扫描仪的性能和主要技术指标。本文列出了设计便携式高分辨率ＣＢＳ扫描仪的主要技术问题，还给出了实际检测结果     

中国数字地震台网数据管理中心Y2K问题的解决方法及getda new软件

叙述了中国数字地震台网（ＣＤＳＮ）数据管理中心（ＤＭＣ）的计算机２０００年问题（Ｙ２Ｋ）的解决情况,着重介绍了为解闷Ｋ问题而编制的ｇｅｔｄａｔａ＿ｎｅｗ软件的功能,特点,结构和工作原理,并结合几个典型实例,对用法和应用情况进行说明,另外,本文对ｇｅｔｄａｔａ＿ｎｅｗ所涉及的部分ＡＳＬ的程序也作了简介。     

CD-300BG工业CT数采系统的设计与实现

本文主要介绍了基于ＡＴ总线的ＣＤ－３００ＢＧ工业ＣＴ数据采集系统的体系结构及其工作原理,并对该系统设计进行了较详细的分析和论证,同时也对该系统进行实际使用后的评价。     

Direct scanning tunneling microscope (STM) observation of Cr(III) complexes on hematite (001) surfaces

Scanning tunneling microscopy (STM) is used to observe, at the atomic scale, Cr(III) adsorbed to hematite (001) surfaces from aqueous solution. The Cr(III) adsorbates are relatively immobile, but estimated activation energies for surface self-diffusion are lower than those for water or hydroxyl substitution in aqueous Cr(III). Possible causes are effects of STM imaging (artifacts), high ligand-substitution rates for adsorbed species, or participation of substrate Fe (III) ligand exchange. STM imaging of suitable aqueous surface complexes is shown to be feasible, and constitutes a new way to study the relationships between microscopic and macroscopic chemical behavior of adsorbed species in aqueous systems.     

利用~(210)Pb、~(137)Cs和~(241)Am计年法测算云南抚仙湖现代沉积速率

通过对云南抚仙湖沉积物柱芯样品的~(210)Pb、~(137)Cs和~(241)Am测试表明,柱芯剖面上有明显的1963年和1986年~(137)Cs蓄积峰,验证了1975年次级蓄积峰存在的可能性,这些峰形完好的蓄积峰对抚仙湖的现代沉积环境有明显的时标意义。利用~(137)Cs计年法得到抚仙湖沉积物自1963年、1975年及1986年以来到2007年的平均沉积速率分别为0.063g/(cm~2·a)、0.052g/(cm~2·a)和0.039g/(cm~2·a),说明了过去近五十年抚仙湖沉积速率整体上经历了一个由快到慢的过程。借助于~(241)Am的1963年蓄积峰可以提高~(137)Cs计年的准确性。根据~(210)Pb CRS计年模式,计算出每个样品深度所对应的年代,与~(137)Cs计年法比较存在一定的偏差,分析了两种计年方法存在差异性的原因。通过质量深度和年代分析,抚仙湖的沉积速率变化幅度比较大,表明抚仙湖近129年来的沉积环境不稳定,可能与相应历史时期的人类活动有密切的关系。     

Acute Toxicity of Sodium Nitrite on Channa punctatus (BLOCH) and Mystus (Mystus) vittatus (BLOCH)

This paper deals with the toxicity of sodium nitrite to freshwater fishes, Channa punctatus (BL.) and Mystus (M). vittatus (Bl.) as to determine the acute toxicity. The LC 50 values were obtained by using a static bioassay method for a period of 24, 48, 72 and 96 hour intervals. The LC 50 values of sodium nitrite for C. punctatus were 375, 325, 250 and 200 ppm and for M. (M). vittatus 164, 140, 90 and 64 ppm, respectively. A profuse mucus secretion was evident at higher concentrations as compared to lower ones. The probable causes of mortality of the fishes are also discussed.     

International Journal of Sediment Research(IJSR)-Order Form(2019)

正Editing Board address:IRTCES, 20 West Chegongzhuang Rd., Beijing 100048, China IJSR is the journal of THE WORLD ASSOCIATION FOR SEDIMENTATION AND EROSION RESEARCH (WASER) and is edited by the International Research and Training Center on Erosion and Sedimentation (IRTCES).Main topics:Fluvial and estuarine processes     

Chromium(III) and Chromium(VI) Circulation in Aquatic Biocenoses

The cumulation of chromium(III) and (VI) has been studied in batch cultures of planktonic algae Microcystis incerta, Scedenesmus obliquus, Chlorella kessleri and Chlamydomonas geitleri at different chromium and algal cells concentrations. It has been found that chromium(VI) is practically not cumulated in algae, whereas chromium(III) is very rapidly cumulated in all types of algae investigated. The cumulation factor increases with the decrease of the radius of algae cells and it reaches the value of 10⁶ for Microcystis incerta even after a few hours of contact. The kinetics, the cumulation factors and the capacity of algae to cumulate chromium(III) is practically the same for living as well as for dead cells and therefore it can be concluded that the cumulation of chromium(III) is due predominantly to the chemical sorption on the surface of algal cells.     

Determination of arsenic(III) for the investigation of the microbial oxidation of arsenic(III) to arsenic(V)

Recent evaluations of acute and chronical toxicity of arsenic resulted in a reduction of the standard value for total arsenic from 40 μg/L to 10 μg/L in drinking water which will be valid in Germany after a transition period as from January 1996. Arsenic is well known as substance of deep groundwaters, mainly of geogenic origin and normally found as As(III) or As(V). As(V) is well removable by flocculation and filtration after adding iron salts. As(III), however, has to be oxidized first to As(V). Therefore, it is important for treatment techniques to be able to distinguish between As(III) and As(V). A modified determination of As(III) using flow injection analysis was installed and optimized in order to investigate whether As(III) may be oxidized to As(V) by bacteria in natural waters. The results showed that at 4°C, no As(III)-oxidation was observed within 14 days. At room temperature, however, in the bacteria-containing samples, an As(III)-oxidation was found starting after 3 to 7 days. After 14 days, no As(III) was left over. In contrast, in the sterile samples, no As(III)-oxidation could be observed within 14 days. These results demonstrated that microbial processes influence the oxidation of As(III) to As(V) in natural waters.