商陆和烟草对锰胁迫的抗氧化响应研究

研究植物的重金属累积能力对于植物修复和植物冶金意义重大.Mn超累积植物商陆(Phytolacca americana L.)的耐性/累积机制至今还不清楚,为了研究商陆在Mn胁迫下的抗氧化酶作用,将萌发6周的商陆和烟草幼苗分别放入1 mmol·L~(-1)或3 mmol·L~(-1)的1/2 Hoagland营养液处理4 d,实验表明商陆叶片光合速率降低幅度显著低于烟草,而烟草MDA含量和电解质渗漏量增加幅度大于商陆.如1 mmol·L~(-1) Mn处理4 d后,与对照相比,商陆和烟草的光合速率分别降低13.3%和75.5%;烟草MDA含量和电解质渗漏量分别增加347.3%和120.1%,而商陆的MDA含量和电解质渗漏量没有明显增加,表明Mn胁迫对超累积植物引起的氧化损伤明显低于非累积植物.随着Mn处理浓度的提高和时间的延长,2种植物叶片SOD和POD活性均迅速增加,其中商陆SOD活性的增加幅度大于烟草;另外,商陆CAT活性持续上升,而烟草CAT活性显著下降.如在1 mmol·L~(-1) Mn处理下,商陆SOD、POD和CAT活性分别提高161.1%、 111.3%和17.5%;烟草SOD和POD提高55.5%和206.0%,而CAT下降15.6%,表明商陆的抗氧化酶,特别是CAT,能够有效地清除Mn毒产生的自由基.这些结果说明抗氧化酶的抗氧化能力是重金属累积植物商陆的Mn耐性机制之一.     

基于形态与in vitro方法的铬污染土壤生物可给性研究

铬（Cr）是电镀类场地的主要污染物.开展土壤中Cr（III）和Cr（VI）的生物可给性研究对于准确评估Cr污染场地风险,克服污染场地过度修复问题十分关键.本研究采集我国栗钙土、红壤、潮土3种典型土壤,通过添加相同浓度污染物的方式制备成Cr（III）或Cr（VI）污染土壤.随后利用5种体外方法（in vitro）,对3种土壤经口摄入的Cr生物可给性进行比较与健康风险评估.进而从土壤理化性质、Cr赋存形态、土壤矿物组成方面,对不同土壤在溶解度生物可给性研究联盟（SBRC）方法中的生物可给性差异进行分析.结果表明,基于生物可给性的Cr污染土壤健康风险评估能够显著降低风险水平,提高风险控制值,其中,SBRC方法在评估中更具有保守性.3种土壤在相同的Cr（III）和Cr（VI）污染浓度下,栗钙土相较于红壤和潮土在肠期具有更高的生物可给性和健康风险.此外,土壤黏粒、有机质含量及迁移系数能够影响土壤Cr的生物可给性,土壤矿物种类赋存不同也是造成Cr（III）和Cr（VI）在不同土壤中生物可给性差异的重要因素.     

Effects of Cu2+ and humic acids on degradation and fate of TBBPA in pure culture of Pseudomonas sp. strain CDT

Soil contamination with tetrabromobisphenol A(TBBPA) has caused great concerns;however, the presence of heavy metals and soil organic matter on the biodegradation of TBBPA is still unclear. We isolated Pseudomonas sp. strain CDT, a TBBPA-degrading bacterium, from activated sludge and incubated it with ~(14)C-labeled TBBPA for 87 days in the absence and presence of Cu~(2+)and humic acids(HA). TBBPA was degraded to organic-solvent extractable(59.4% ± 2.2%) and non-extractable(25.1% ± 1.3%) metabolites,mineralized to CO_2(4.8% ± 0.8%), and assimilated into cells(10.6% ± 0.9%) at the end of incubation. When Cu~(2+)was present, the transformation of extractable metabolites into non-extractable metabolites and mineralization were inhibited, possibly due to the toxicity of Cu~(2+)to cells. HA significantly inhibited both dissipation and mineralization of TBBPA and altered the fate of TBBPA in the culture by formation of HA-bound residues that amounted to 22.1% ± 3.7% of the transformed TBBPA. The inhibition from HA was attributed to adsorption of TBBPA and formation of bound residues with HA via reaction of reactive metabolites with HA molecules, which decreased bioavailability of TBBPA and metabolites in the culture. When Cu~(2+)and HA were both present, Cu~(2+)significantly promoted the HA inhibition on TBBPA dissipation but not on metabolite degradation. The results provide insights into individual and interactive effects of Cu~(2+)and soil organic matter on the biotransformation of TBBPA and indicate that soil organic matter plays an essential role in determining the fate of organic pollutants in soil and mitigating heavy metal toxicity.     

压缩天然气加气站日常运营环境影响分析——以洛阳市某加气站为例

鉴于压缩天然气(CNG)加气站日常运行对周边环境影响的高风险状态,文章依据洛阳市某CNG加气站生产运营状况,对其运营过程中可能造成的环境影响进行预测、评析,并提出了合理的防范措施。     

基于社会科学统计程序(SPSS)回归性分析的尾矿库事故预测模型

基于社会科学统计程序(SPSS)软件的分析功能,对调查研究中获取的尾矿库案例进行数据提炼和分类编码,找出相关因子并进行回归性分析。最终目的是找出尾矿库各个因素的内在联系,建立简单的尾矿库事故模型,从而可以初步预测尾矿库事故发生的可能性。该预测模型为尾矿库事故的研究提出了新方法,对于防灾减灾以及保护人民生命财产安全起到了积极作用。     

Preliminary study on removing Cs+/Sr2+ by activated porous calcium silicate—A by-product from high-alumina fly ash recycling industry

¹³⁷Cs⁺/⁹⁰Sr²⁺-containing radioactive wastewater is one of the most important problems that the world has been facing with. A by-product, activated porous calcium silicate, is generated at high levels by the pre-desiliconizing and soda-lime-sintering processes for producing Al₂O₃ from high-alumina fly ash. In order to examine if this by-product could be used as an absorbent for removal of ¹³⁷Cs⁺/⁹⁰Sr²⁺ from radioactive wastewater, various parameters, such as pH, adsorbent dose, contact time, and initial concentration, were discussed. Results indicated that the equilibrium reached in about 2 hr. Activated porous calcium silicate was highly pH sensitive and able to remove Cs⁺/Sr²⁺ in a near-neutral environment. The adsorption equilibrium was best described by Freundlich isotherm equations, and the adsorption of Cs⁺/Sr²⁺ was a physical process. The adsorption kinetic data could be better fitted by the pseudo-second-order model, and the adsorption was controlled by multidiffusion. Current study showed that activated porous calcium silicate has a good adsorption of Cs⁺/Sr²⁺ for their removal. However, other characteristics, such as selectivity because of coexisting cations, elution and regeneration, thermal stability, and acid resistance, should be discussed carefully before using it in an actual field.

Implications:Removing ¹³⁷Cs⁺/⁹⁰Sr²⁺ from radioactive wastewater is one of the tough issues that has been attracting more and more attention world widely, which is the same as fly ash. For recycling high-alumina fly ash, in which Al is extracted to produce Al₂O₃, a huge amount of activated porous calcium silicate is generated year by year. In this paper, this by-product was successfully used as an absorbent to remove ¹³⁷Cs⁺/⁹⁰Sr²⁺ from radioactive wastewater for the first time. Factors that affect the absorbability and the mechanisms were discussed in details, providing a possible choice for disposal of ¹³⁷Cs⁺/⁹⁰Sr²⁺-containing radioactive wastewater.     

基于方波溶出伏安法的电化学传感器检测水体中痕量铅

基于方波溶出伏安法运用丝网印刷电极探索了一种利用电化学传感器检测水样中痕量铅的方法.得到了该检测方法的最佳参数:方波频率30 Hz,振幅80 mV,电位增量5 mV;0.5 mol/L的支持电解质(KCl);沉积电位-1.1 V,沉积时间400 s.在该优化条件下,在浓度为25 ～ 500μg/L范围内溶出峰电流与铅离子浓度呈良好的线性关系(R2=0.9945).对于几种其他金属离子的干扰实验结果表明,Mn2的存在严重抑制铅离子的峰电流.     

煤炭开采对粮食安全的影响及其对策

从开采方法、土地复垦与综合治理、经济和政策等方面采取措施,可以最大限度地减小采矿对土地资源的破坏,治理好矿区土地资源,保护好耕地,实现粮食产需总量的大体平衡。“保护粮食安全”关键是抓好耕地保护,根据可持续发展原则,综合考虑矿业经济发展与矿区生态环境保护的关系,走矿业“绿色开采”的道路,研究有利于矿区耕地保护的采矿新技术,使资源开发与耕地保护协调发展,同时还应对煤矸石和粉煤灰进行充分利用、防治水体受到污染、采用先进的土地复垦技术对土地资源的浪费和破坏进行治理,把土地复垦中的经济效益、社会效益和生态效益统一起来,为粮食生产奠定基础。     

含锌废水处理技术的研究进展

综述了传统的物理化学法和生物法处理含锌废水的原理,系统阐述了其研究进展.微生物固定技术是一种新兴而有效的生物处理技术,尤其是硫酸盐还原菌固定化技术,将厌氧活性污泥包埋,构建稳定高效的微生物体系,以加强其抗毒性和处理效率.因此,在含锌废水处理方面具有很大的发展潜力,有望得到广泛应用.     

水环境中铬的存在形态及迁移转化规律

综合评述了水环境中铬的存在形态、污染特征及其迁移转化规律的研究现状.水体中铬主要是三价和六价,存在形态分为溶解态、离子交换态、有机结合态、无机沉淀态、残留态,迁移转化过程主要是水解、沉淀、络合、吸附和氧化还原等.对铬在水体中迁移和转化过程的动力学模型进行了论述.