汽车用钢板弹簧失效分析

目的 研究汽车用钢板弹簧断裂失效原因.方法 通过宏观分析、金相检验、力学性能分析、材质分析、断口电镜扫描及能谱分析等测试手段,对汽车用钢板弹簧的断裂失效原因进行分析.结果 汽车用钢板弹簧的失效模式为疲劳裂纹源于表面腐蚀坑处的高周腐蚀疲劳断裂.首先,板簧表面存在异常磨损,导致防护漆层局部脱落,裸露的金属基体在腐蚀环境下出现表面腐蚀坑,外界拉应力作用及腐蚀坑底部应力集中叠加导致早期疲劳裂纹在腐蚀坑底部萌生并扩展.其次,板簧表面存在脱碳现象,导致板簧表面硬度及强度降低,表面耐腐蚀性能下降,为早期疲劳裂纹的萌生创造了条件.结论 控制热处理质量,避免表面脱碳;做好定期维护保养,在簧片间加石墨润滑剂,防止长时间干磨或挤压碰撞导致漆层早期脱落;及时清理附着的泥水,减小腐蚀几率;对存在隐患的在用板簧及时更换.     

油气钻井作业对地下水污染治理研究＊

分析了钻井作业对地下水污染的特点、污染途径,针对性地提出了钻井作业对地下水污染的预防措施,以及污染物处理技术,其中氧化还原技术、气体抽取技术、环境生物技术主要用于有机物污染治理,SRB技术、废弃钻井液固化技术、钻井液转换为水泥浆(MTC)的固井技术可用于处理废弃钻井液。钻井引起的污染治理应以"预防为主,防治结合",切实推行清洁生产和HSE管理。     

厦门湾海滩微塑料污染特征

以厦门湾6个典型海滩为工作区,分析海滩微塑料的污染特征.结果表明:①厦门湾6个海滩的微塑料丰度数据范围介于(28. 1±9. 4)～(312. 7±35. 2) n·kg~(-1)之间.②厦门湾海滩微塑料分为碎片类、发泡类、薄膜类和纤维类等4种类型.各站位点均以碎片类和发泡类为主,占总数量的80%左右,薄膜类和纤维类所占比例较少.③厦门湾海滩粒径1 mm的微塑料占最大比例,超过60%.粒径为1～3 mm和3～5 mm的微塑料所占比例较小.④通过红外光谱分析,确认厦门湾海滩微塑料碎片类和纤维类的主要成分是聚乙烯,发泡类和薄膜类的主要成分是聚苯乙烯.⑤通过扫描电镜观测,大部分微塑料表面粗糙、凹凸不平,带有明显裂痕.整体而言,厦门湾海滩微塑料污染处于中等偏下的程度,陆源污染是厦门湾海滩微塑料污染的最主要来源.     

Evaluation of mercury speciation and removal through air pollution control devices of a 190 MW boiler

Air pollution control devices (APCDs) are installed at coal-fired power plants for air pollutant regulation. Selective catalytic reduction (SCR) and wet flue gas desulfurization (FGD) systems have the co-benefits of air pollutant and mercury removal. Configuration and operational conditions of APCDs and mercury speciation a ect mercury removal e ciently at coal-fired utilities. The Ontario Hydro Method (OHM) recommended by the U.S. Environmental Protection Agency (EPA) was used to determine mercury speciation simultaneously at five sampling locations through SCR-ESP-FGD at a 190 MW unit. Chlorine in coal had been suggested as a factor a ecting the mercury speciation in flue gas; and low-chlorine coal was purported to produce less oxidized mercury (Hg2+) and more elemental mercury (Hg0) at the SCR inlet compared to higher chlorine coal. SCR could oxidize elemental mercury into oxidized mercury when SCR was in service, and oxidation e ciency reached 71.0%. Therefore, oxidized mercury removal e ciency was enhanced through a wet FGD system. In the non-ozone season, about 89.5%–96.8% of oxidized mercury was controlled, but only 54.9%–68.8% of the total mercury was captured through wet FGD. Oxidized mercury removal e ciency was 95.9%–98.0%, and there was a big di erence in the total mercury removal e ciencies from 78.0% to 90.2% in the ozone season. Mercury mass balance was evaluated to validate reliability of OHM testing data, and the ratio of mercury input in the coal to mercury output at the stack was from 0.84 to 1.08.     

Flow analysis of major and trace elements in residues from large-scale sewage sludge incineration

Increase of sewage sludge (SS) has led to the construction of more incineration plants, exacerbating to the production of SS incineration residues. However, few studies have considered the mass balance of elements in large-scale SS incineration plants, affecting the residues treatment and utilization. In this study, flow analysis was conducted for major and trace elements in the SS, the fly ash (sewage sludge ash, SSA) and bottom ash from two large-scale SS incineration plants. The elemental characteristics were compared with those of coal fly ash (CFA), and air pollution control residues from municipal solid waste incineration (MSWIA), as well as related criteria. The results showed that the most abundant major element in SSA was Si, ranging from 120 to 240 g/kg, followed by Al (76–348 g/kg), Ca (26–113 g/kg), Fe (35–80 g/kg), and P (26–104 g/kg), and the trace elements were mainly Zn, Ba, Cu, and Mn. Not all the major elements were derived from SS. Most trace elements in the SS incineration residues accounted for 82.4%–127% of those from SS, indicating that SS was the main source of trace elements. The partitioning of heavy metals in the SS incineration residues showed that electrostatic precipitator ash or cyclone ash with high production rates were the major pollutant sinks. The differences in some major and trace elements could be indicators to differentiate SSA from CFA and MSWIA. Compared with related land criteria, the pollutants in SSA should not be ignored during disposal and utilization.     

辐射环境安全事故的应急准备和演练

核技术的广泛应用给人类带来巨大利益的同时,也不可避免地产生一定程度的危害。结合辐射环境安全事故的特点,从事故类型、应急组织、应急响应准备、应急响应处置、应急演练的开展等方面详细阐述了如何开展辐射环境安全事故应急准备和演练,以提高辐射应急处置能力和水平。     

农药污染对蚯蚓的群落结构与超微结构影响的研究

报道了农药污染对蚯蚓的群落结构与超微结构影响的研究,结果表明：随着农药污染程度增加,蚯蚓的种类和数量则减少。超微结构在扫描电镜下可观察到重污染区壮伟环毛蚓（Pheretimarobusta）胃粘膜出现溃疡灶,并产生穿孔现象;在中污染区只有微绒毛萎缩病变;在重污染区发现肠粘膜上的纤毛发生紊乱及萎缩,纤毛顶端膨大呈球形。对精子观察可见在中污染区就出现了畸形精子。在透射电镜下观察可见重污染区壮伟环毛蚓胃肠道粘膜上皮细胞中的粗面内质网（RER）出现扩张,高尔基复合体也产生扩张状,线粒体发生肿胀,线粒体嵴消失呈空泡状。另可见细胞核膜间隙扩张、断裂,核染色质边集或减少,胞质呈大片空白。蚯蚓以上病变指标均能很灵敏反映土壤农药污染程度。     

固原市农田土壤微塑料的分布特征及风险评估

为探明固原市农田土壤中微塑料分布特征,通过现场采集调查、显微镜观察和傅里叶变换红外光谱等方法分析了固原市农田土壤中微塑料的丰度、类型、颜色、大小和外形等特征,用污染负荷指数法（PLI）评估了微塑料污染风险.结果表明,固原市农田土壤（耕作层）微塑料丰度为186.32~1286.24 n ·kg^-1,设施农业土壤微塑料丰度分别较非设施农业有膜和无膜种植土壤显著增加35.56%和228.91%,耕作层微塑料丰度是犁底层的0.31倍.PE （26.42%~62.83%）和PP （27.64%~42.62%）为主要的微塑料类型,设施农业土壤微塑料种类数显著大于非设施农业.<100 μm微塑料占32.21%~42.52%,而>1000 μm只占0.28%~12.31%,耕作层微塑料粒径比犁底层高47.39%,设施农业土壤微塑料粒径最大,非设施无膜种植最小.微塑料形状主要为薄膜、纤维、碎片和微珠,其中纤维状丰度最大,薄膜状次之.共检测出7种颜色的微塑料,以白色和黑色为主.研究区污染风险总体为低风险,设施农业土壤微塑料污染风险最高.研究结果将为我国农田土壤微塑料污染评估及微塑料土壤环境行为提供数据参考.     

火电厂海水淡化工艺的技术经济分析及选择

简述了膜法与低温多效蒸馏法海水淡化原理,对低温多效和多套反渗透海水淡化装置进行了技术经济比较分析,比较分析了其制水综合成本和运行成本。比较结果表明,低温多效法高于反渗透法,反渗透法海水淡化加一级反渗透与低温多效法相当。并且,对八角电厂2种待选海水淡化方案做了经济技术比较,最终确定了八角电厂的海水淡化方案。     

核电厂核事故应急疏散研究

根据我国法规、标准与美国核管委对核电厂核事故应急疏散的要求,考虑我国核电厂特殊的厂址条件与社会环境,分析核事故应急疏散的可行性。通过应急疏散行为研究、厂区的交通需求估计和路网分析,对不同情境,考虑核事故应急疏散的特殊问题,分别采用人工容量分析与宏观仿真模拟得到应急疏散时间。针对某核电厂,给出核事故应急疏散分析的一般步骤、方法与计算结果。对宏观仿真模型的主要参数进行灵敏度分析,找出影响应急疏散时间的主要因素,提出缩短应急疏散时间的针对性措施。