我国的劳动安全监察制度与压力容器事故预防

分析了压力容器事故的主要原因 ,介绍了劳动安全监察制度 ,研究了该制度对减少压力容器事故所起的作用 ,为预防压力容器事故 ,对劳动安全监察制度的发展 ,提出了自己的见解与看法。     

美国海军舰艇命名体系研究

美国海军舰艇命名体系由任命前缀、舰艇名称、分类代号、舷号4类要素构成,首先分析了每类要素对于命名体系的贡献,然后基于美国海军舰艇命名体系,以美国海军舰艇名册为数据源,通过要素提取、规则建立等步骤分析美国海军现役舰艇组成。经过分析,美国现役715艘舰艇分为战斗舰、辅助舰、战斗艇、支援艇、未在分类代号中定义等5大类67类型177级别,通过对比基于类型与级别规则、基于任命前缀规则的结果挖掘出美国海军现役舰艇组成规律。     

加压上流式好氧污泥床(PUASB)法处理制药废水初探

在进水ＣＯＤ为５００－６００ｍｇ／Ｌ、压力ｐ＝０．２ＭＰａ、回／流比Ｒ＝６条件下,加压上流式好氧泥泥床平均ＣＯＤ去除率为７１％,出水基本达到国家排放标准;进水ＣＯＤ为１０００ｍｇ／Ｌ以上,在ｐ＝０．３ＭＰａ、Ｒ＝６条件下,ＣＯＤ去除率仍可达到７０％左右。     

小冲杆试验测定重离子辐照A508-3钢的硬化和脆化

目的采用小冲杆测试方法测量高能重离子辐照反应堆压力容器A508-3钢的辐照硬化和脆化特性,为工况条件下反应堆压力容器寿命预测提供实验依据。方法采用兰州重离子加速器提供的高能C^(6+)离子通过减能装置在290℃条件下开展A508-3钢辐照实验,并在样品表面形成一定厚度、准均匀分布的离位损伤层。通过开展不同辐照剂量辐照样品的小冲杆测试,得到不同辐照剂量A508-3钢的小冲杆载荷-位移曲线。通过对小冲杆测试得到的载荷-位移曲线的分析,测定不同辐照剂量样品的辐照硬化和脆化特性。结果压力容器A508-3钢辐照样品的硬化和脆化随着辐照剂量的增加逐渐增强,0.15 dpa以前呈线性增长,而后缓慢增大,约0.2 dpa时达到饱和趋势。结论通过小冲杆测试可以得到离子辐照样品的硬化和脆化行为,A508-3钢辐照硬化和脆化行为具有一致的变化趋势。     

医药工业专用压力容器--开环反应罐的检测及安全评价

对医药化工合成专用设备－－开环反应罐进行了多年跟踪检测，积累了检测数据，对其安全可靠性进行了探索。     

蓄能器爆炸事故原因推断及防控措施

囊式蓄能器是液压系统中常用的压力容器。在更换胶囊和(或)充装氮气时如操作不当,有发生爆炸的风险。通过对一起蓄能器爆炸事故的调查,经计算、推论,得出此次爆炸是一起物理爆炸。并就事故发生原因及其爆炸强度、危害程度进行了分析。提出生产商和使用单位应制定科学的、可行的标准操作程序(Standard Operation Program,SOP),并要求工人在实际操做中严格执行,加强过程控制,避免事故的发生。     

黑龙江省船舶防污染现状及对策分析

分析了黑龙江省船舶防污染工作的现状，提出了当前工作中存在的主要问题，并结合黑龙江水域的特点和现有经济条件，提出了具体的改进措施和防范对策。     

密相流态化气力输送技术的工业试验研究

对燃煤电厂密相流态化气力输送系统的不同工况进行1：1工业试验研究。在不影响粉煤灰正常输送的前提下，采集系统核心部件仓泵的压力曲线及数据，对其进行分析。研究认为，仓泵的设计压力至少可以降低为0.8MPa，并对管路系统提出改进方案，为密相流态化气力输送的设计和运行提供参考依据。     

Assessment of Management to Mitigate Anthropogenic Effects on Large Whales

United States and Canadian governments have responded to legal requirements to reduce human‐induced whale mortality via vessel strikes and entanglement in fishing gear by implementing a suite of regulatory actions. We analyzed the spatial and temporal patterns of mortality of large whales in the Northwest Atlantic (23.5°N to 48.0°N), 1970 through 2009, in the context of management changes. We used a multinomial logistic model fitted by maximum likelihood to detect trends in cause‐specific mortalities with time. We compared the number of human‐caused mortalities with U.S. federally established levels of potential biological removal (i.e., species‐specific sustainable human‐caused mortality). From 1970 through 2009, 1762 mortalities (all known) and serious injuries (likely fatal) involved 8 species of large whales. We determined cause of death for 43% of all mortalities; of those, 67% (502) resulted from human interactions. Entanglement in fishing gear was the primary cause of death across all species (n = 323), followed by natural causes (n = 248) and vessel strikes (n = 171). Established sustainable levels of mortality were consistently exceeded in 2 species by up to 650%. Probabilities of entanglement and vessel‐strike mortality increased significantly from 1990 through 2009. There was no significant change in the local intensity of all or vessel‐strike mortalities before and after 2003, the year after which numerous mitigation efforts were enacted. So far, regulatory efforts have not reduced the lethal effects of human activities to large whales on a population‐range basis, although we do not exclude the possibility of success of targeted measures for specific local habitats that were not within the resolution of our analyses. It is unclear how shortfalls in management design or compliance relate to our findings. Analyses such as the one we conducted are crucial in critically evaluating wildlife‐management decisions. The results of these analyses can provide managers with direction for modifying regulated measures and can be applied globally to mortality‐driven conservation issues. Evaluación del Manejo para Mitigar Efectos Antropogénicos sobre Ballenas Mayores