集团公司安全生产环境保护职业健康工作会议访谈录

3月26日至3月28日,2003年度中国石油集团公司安全生产环境保护职业健康工作会议在青岛召开。会议期间,代表们分组进行了热烈的讨论,本刊记者参加了环境保护组的讨论,并就集团公司2003年环境保护工作部署及当前环境保护热点问题走访了集团公司质量安全与环保部董国永副主任及有关专家。 记者:董主任,任总在大会总结讲话中肯定了此次会议开得很成功,主题突出,目标和任务明确,措施具体可行,对集团公司今后的HSE工作,起到了积极的推动和指导作用。请您具体谈谈2003年环境保护工作的主要目标和任务。 董主任:王海森主任在报告中明确指出,2003年…     

认清形势 明确任务 开拓进取 努力开创集团公司安全生产、环境保护和职业卫生工作新局面——王海森主任在集团公司安全、环境与健康工作会议上的报告(环保部分摘编)

这次集团公司安全、环境与健康工作会议是在集团公司重组改制取得阶段性成果的形势下召开的。会议的主要任务是 :深入贯彻落实国务院及集团公司安全生产紧急电话会议、２０００年全国环境保护工作会议、集团公司２０００年工作会议精神 ,总结去年的工作 ,部署今年的任务 ,统一认识 ,明确任务 ,紧紧围绕集团公司改革和发展的任务目标 ,努力开创安全生产、环境保护和职业卫生工作的新局面。１１９９９年工作情况１９９９年是极不平凡的一年 ,各企事业单位在集团公司的正确领导下 ,认真贯彻落实年初集团公司工作会议和６月份召开的领导干部会议…     

在集团公司安全生产环境保护与健康工作会结束时的总结讲话

同志们： 集团公司安全生产环境保护和健康工作会议，经过与会代表的共同努力，完成了预定的各项议程，今天就要结束了。这次会议，集团公司党组非常重视，做过专门研究。马富才总经理亲自批示了有关文件，阎三忠副总经理几次听取质量安全与环保部的工作汇报和工作安排，郑虎副总经理专门就安全总监设置问题组织有关部门进行了研究，做出了重要指示。特别是在集团公司集中深入开展“三讲”活动当中，集团公司决定召开这次会议，体现了集团公司领导对我们工作的重视和关怀，也说明了这次会议的重要性和我们任务的紧迫性。会议期间，阎总做了…     

阎三忠同志在集团公司2001年安全环境与健康工作会议上的讲话

跨入新世纪之际,集团公司召开安全环境和健康工作会议。这是一次很重要的会议。今年是新世纪的第一年,是实施“十五”计划的开局年,对如何起好步、开好局,党组很重视,专门进行过研究。刚才,海森同志的工作报告,总结了工作,分析了形势,部署了任务,提出了要求。很全面,我完全同意。希望大家会后认真贯彻。1 回顾“九五”,安全环境和健康工作取得了显著成绩“九五”期间,对于集团公司来说,是极不平凡的五年。集团公司经历了两次大的重组,进行了经营机制的转换。面对新形势、新情况、新问题,集团公司所属企业认真贯彻党和国家对…     

阎三忠副总经理在集团公司2002年安全生产电话会议上的讲话

同志们： 今天召开的集团公司安全生产电话会，主要是认真贯彻党中央、国务院对安全生产、环境保护的一系列重要指示，具体落实国务院安全生产电视电话会议和集团公司工作会议精神，总结回顾2001年安全、环保工作，安排部署2002年安全、环保各项任务，动员广大干部职工进一步认清形势，统一思想，坚定信心，确保集团公司安全生产形势的稳定，以优异成绩迎接党的十六大胜利召开。 刚才，大港油田集团有限责任公司、辽河石油勘探局和新疆石油管理局介绍了经验，讲得很好，值得各企业学习借鉴。会议授予大庆石油管理局等16个单位为2001年度安全…     

集团公司召开2021年质量健康安全环保工作会议 深入学习贯彻习近平总书记重要讲话和指示批示精神 坚决扛起责任担当防范化解重大风险 为公司高质量稳定发展提供坚实保障

正1月8日,集团公司2021年质量健康安全环保工作会议在京召开,深入学习贯彻习近平生态文明思想和习近平总书记关于安全生产的重要论述,落实健康中国建设要求,强化"质量是企业生命"的理念,坚持治标与治本并重,坚持识别大风险、消除大隐患、杜绝大事故,进一步推进集团公司向本质安全环保型企业迈进。     

回顾 总结 部署

3月26日至3月28日,备受关注的2003年度中国石油集团公司安全生产环境保护职业健康工作会议在青岛召开。 会议期间王海森主任做了题为“与时俱进,开拓创新,推进安全环境健康工作再上新水平”的报告,指出此次会议的主要任务是:总结回顾过去三年安全生产,环境保护和职业健康工作,分析形势,安排部署2003年工作,推进安全环境健康工作再上新水平。回顾三年的成绩,主要体现在:安全环保健康目标和责任制不断落实;安全环保健康规章制度逐步完善;安全环保机构得到加强和充实;健康安全环境管理体系全面推进;建设项目环境管理规范进行;安全环保科技创新…     

2007年青海省环境保护工作会议掠影

2007年2月1日，青海省环境保护工作会议在西宁召开。会议的主要任务是：总结2006年全省环境保护工作，学习贯彻省委十届九次全委会议和全国环境保护厅局长会议精神，安排部署2007年工作任务，动员各地各部门和全省环保工作者，鼓足干劲，努力开创全省环保工作的新局面。2007年青海省环境保护工作会议掠影@刘仪     

开拓进取扎实工作努力实现全省环境保护工作的新突破--祁生奎副局长在全省环境保护工作会议上的讲话

这次全省环境保护工作会议是在我省社会经济陕速健康发展的新形势下召开的一次重要会议。会议的主要任务是，学习贯彻中央人口资源环境工作座谈会、全国环境保护厅局长座谈会、落实省委十届三次全委会、省委经济工作会议和全省人口资源环境工作座谈会精神，总结工作，表彰先进，安排部署2004年环保任务。     

总公司召开安全生产环境保护会议

总公司召开安全生产环境保护会议１９９３年１２月６日至１０日，总公司在石油管道局新乡输油公司召开了石油企业安全生产和环境保护工作会议。来自３６个石油企业和总公司机关及直属单位的２００余名代表出席了会议。总公司技术监督局主持会议，国家环境保护局给大会发来...     

Atrazine, isoproturon, mecoprop, 2,4-D, and bentazone adsorption onto iron oxides

Iron oxides are important components influencing the adsorption of various inorganic and organic compounds in soils and sediments. In this study the adsorption on iron oxides of nonionic and ionic pesticides was determined as a function of solution pH, ionic strength, and pesticide concentration. The investigated iron oxides included two-line ferrihydrite, goethite, and lepidocrocite. Selected pesticides comprised atrazine (6-chloro-N2-ethyl-N4-isopropyl-1,3,5-triazine-2,4-diamine), isoproturon [3-(4-isopropylphenyl)-1,1-dimethylurea)], mecoprop [(RS)-2-(4-chloro-2-methylphenoxy)propionic acid], 2,4-D (2,4-dichlorophenoxyacetic acid), and bentazone [3-isopropyl-1H-2,1,3-benzothiadiazin-4(3H)-one 2,2-dioxide]. The adsorption of the nonionic pesticides (atrazine and isoproturon) was insignificant, whereas the adsorption of the acidic pesticides (mecoprop, 2,4-D, and bentazone) was significant on all investigated iron oxides. The adsorption capacity increased with decreasing pH, with maximum adsorption reached close to the pKa values. The addition of CaCl2 in concentrations from 0.0025 to 0.01 M caused the adsorption capacity to diminish. The adsorption of bentazone was significantly lower than the adsorption of mecoprop and 2,4-D, illustrating the importance of a carboxyl group in the pesticide structure. The adsorption capacity on the iron oxides increased in the order: lepidocrocite < goethite < two-line ferrihydrite. The maximum adsorption capacities of meco-prop and 2,4-D on goethite were found to be equivalent to the site density of singly coordinated hydroxyl groups on the faces of the dominant (110) form, suggesting that singly coordinated hydroxyl groups are responsible for adsorption. Differences in adsorption capacities between iron oxides can be explained by differences in the surface site density of singly coordinated hydroxyl groups. The maximum measured adsorption capacity of mecoprop on two-line ferrihydrite was equivalent to 0.2 mol/mol Fe.     

Tillage, intercrop, and controlled drainage-subirrigation influence atrazine, metribuzin, and metolachlor loss

Atrazine (6-chloro-N2-ethyl-N4-isopropyl-1,3,5-triazine-2,4-diamine) and metolachlor [2-chloro-N-(2-ethyl-6-methylphenyl)-N-(2-methoxy-1-methylethyl)acetamide] have been found with increasing occurrence in rivers and streams. Their continued use will require changes in agricultural practices. We compared water quality from four crop-tillage treatments: (i) conventional moldboard plow (MB), (ii) MB with ryegrass (Lolium multiflorum Lam.) intercrop (IC), (iii) soil saver (SS), and (iv) SS + IC; and two drainage control treatments, drained (D) and controlled drainage-subirrigation (CDS). Atrazine (1.1 kg a.i. ha-1), metribuzin [4-amino-6-(1,1-dimethylethyl)-3-(methylthio)-1,2,4-triazine-5(4H)-one] (0.5 kg a.i. ha-1), and metolachlor (1.68 kg a.i. ha-1) were applied preemergence in a band over seeded corn (Zea mays L.) rows. Herbicide concentration and losses were monitored from 1992 to spring 1995. Annual herbicide losses ranged from < 0.3 to 2.7% of application. Crop-tillage treatment influenced herbicide loss in 1992 but not in 1993 or 1994, whereas CDS affected partitioning of losses in most years. In 1992, SS + IC reduced herbicide loss in tile drains and surface runoff by 46 to 49% compared with MB. The intercrop reduced surface runoff, which reduced herbicide transport. Controlled drainage-subirrigation increased herbicide loss in surface runoff but decreased loss through tile drainage so that total herbicide loss did not differ between drainage treatments. Desethyl atrazine [6-chloro-N-(1-methylethyl)-1,3,5-triazine-2,4-diamine] comprised 7 to 39% of the total triazine loss.     

Sustainability,eco-efficiency,life-cycle management,and business strategy

This article outlines some of the rationale for integrating environment and sustainablility issues into core business practises and provides some guidance on how companies can begin to take a strategic view when selecting environmental management tools. Two of these tools, life cycle management and eco-efficiency, are outlined in brief.© 1999 Five Wind International. Reprinted with permission by John Wiley & Sons, Inc.     

Environmental concentrations of agricultural herbicides in Saskatchewan, Canada: bromoxynil, dicamba, diclofop, MCPA, and trifluralin

Herbicides are the most commonly used group of agricultural pesticides on the Canadian Prairies and, in 1990, more than 20000 Mg of herbicides were applied in the provinces of Alberta, Saskatchewan, and Manitoba. The present paper reports on environmental concentrations of five herbicides currently used in the prairie region. The herbicides bromoxynil [3,5-dibromo-4-hydroxy-benzonitrile], dicamba [3,6-dichloro-o-anisic acid], diclofop [(RS)-2-[4-(2,4-dichlorophenoxy)-phenoxy]propanoic acid], MCPA [(4-chloro-2-methylphenoxy)acetic acid], and trifluralin [alpha,alpha,alpha-trifluoro-2,6-dinitro-N,N-isopropyl-p-toluidine] were measured in the atmosphere, bulk atmospheric deposits, surface film, and dugout (pond) water at two sites near Regina, Saskatchewan, during 1989 and 1990. All five herbicides were detected in air and surface film and all but trifluralin were detected in the bulk atmospheric deposits and dugout water. Trifluralin was most frequently detected in air (79% of samples) whereas bromoxynil was present in maximum concentration (4.2 ng m(-3)). MCPA was present in maximum levels in bulk atmospheric (wet plus dry) deposits (2350 ng m(-2) d(-1)), surface film (390 ng m(-2)), and dugout water (330 ng L(-1)), whereas dicamba was most frequently detected in surface film (47%) and dugout water (97%). The highest quantities of the herbicides tended to be present during or immediately after the time of regional application.