苯胺类化合物微生物降解研究进展

苯胺类化合物是广泛应用的化工材料,已经造成了严重的环境污染,并危及了人体健康.利用微生物方法处理环境中的污染物质目前备受青睐,它有着物理和化学方法不可比拟的优越性.对苯胺类化合物的微生物降解研究现状进行了系统的综述,包括具有降解苯胺类化合物能力的微生物类群、苯胺类化合物的降解途径及苯胺类化合物降解的影响因素,提出了苯胺类化合物生物降解研究中存在的问题和尚需进一步研究的方面.     

硝化抑制剂的加量对生化需氧量值影响的探讨

BOD作为衡量水体受有机污染程度的重要指标,其反映的可生化降解性是其他参数无法替代的。在5日生化培养时间内,硝化作用的耗氧量取决于是否存在足够数量的能进行此种氧化作用的微生物,许多二级生化处理的出水和受污染较久的水体中,往往含有大量硝化微生物,因此测定这种水样时应抑制其硝化反应。通过对特定水体硝化抑制剂添加与否及加量多少对BOD5测定结果的影响,分析并探讨抑制特定水体硝化过程的最佳条件。在严格质量控制的基础上,对特定行业和环境水体的实际样品进行硝化抑制剂添加与否和加量及时间培养曲线等对比实验,通过所得到的比对数据以化学需氧量值与BOD5之间关系为基准,对硝化抑制剂的加量进行了探究。     

中空纤维膜生物反应器处理生活污水的特性

中空纤维膜生物反应器生活污水处理特性的试验研究结果表明：Ｄ ＨＲＴ为１．５ｈ,ＣＯＤ容积负荷为５．７６ｋｇ／（ｍ＾３·ｄ）条件下,均可实现９０％以上的ＣＯＤ去除率;对ＮＨ３－Ｎ的去除率可稳定在９０％以上,高ＭＬＳＳ浓度８０００－１００００ｍｇ·Ｌ）提供了内部厌氧环境,使膜生物反应器的Ｔ－Ｎ去除率可达５０－６０％,中空纤维生物反应器处理高效,不受冲击负荷影响,操作管理方便,其生活物反应器体积比常规生     

代氰预镀铜工艺研究及应用

对代氰预镀铜工艺进行了实验研究和应用研究。结果表明：该工艺对钢铁及锌合金等金属具有良好的结合力,具有较宽的工艺条件,对杂质的容许力强,分散能力好,具有强脱脂除油能力,代氰预镀溶液成分带入后道工序不产生或不产生明显影响等,已基本达到了氰化预镀铜工艺的水准。     

柳州地区酸沉降临界负荷的确定

为了对目标沉降量的制定提供定量依据,根据现场调查和实验测量获得柳州红壤的物理化学特性,地表水化学行性及降水化学背景和现状的数据,应用改进的ＭＡＧＩＣ模型计算不同酸沉降量下土壤的酸化过程。结果表明：柳州土壤已处于酸化状态并呈现继续酸化趋势,表层土壤敏感性较强,而底层土壤和地表水缓冲能力较强。     

Photocatalytic remediation of γ-HCH contaminated soil induced by α-Fe2O3 and TiO2

Heterogeneous photocatalytic degradation of γ-HCH on soil surfaces was carded out to evaluate the photocatalytic effectiveness of α-Fe2O3 and TiO2 toward degrading γ-HCH on soil surfaces. After being spiked with γ-HCH, soil samples were loaded with α-Fe2O3 or TiO2 and exposed to UV-light irradiation. Different catalyst loads, 0%, 2%, 5%, 7%, and 10% (wt.)α-Fe2O3 ; 0%, 0.5%, 1%, 2:(Wt.)TiO2, were tested for up to 7 d irradiation. The effects of soil thickness, acidity, and humic substances were also investigated. The obtained results indicated that the γ-HCH photodegradation follows the pseudo-first-order kinetics. The addition of α-Fe2O3 or TiO2 accelerates the photodegradation of γ-HCH, while the photodegradation rate decreases when the content of α-Fe2O3 exceeds 7% (wt.).The degradation rate increases with the soil pH value. Humic substances inhibit the photocatalytic degradation of γ-HCH., and trichlorobenzene are detected as photodegradation intermediates, which are gradually degraded with the photodegradation evolution.     

应用物种敏感性分布评价敌敌畏对淡水生物的生态风险

敌敌畏是一类重要的有机磷杀虫剂,但其对水生生态的影响至今研究较少。为了评价其生态风险,构建了淡水水生生物对敌敌畏的物种敏感性分布(species sensitivity distribution,SSD)模型,在此基础上,讨论了影响SSD模型的主要因素;并分析了该模型的不确定性;推导了敌敌畏对不同类别生物的5%危害浓度HC5(hazardous concentration for 5%the species)阈值;整理收集了我国重要流域水体中敌敌畏的环境浓度;结合SSD模型计算了对淡水生物的潜在影响比例(potentially affected fraction,PAF)。结果表明:1)不同模型的选择会影响HC5的结果,且Burr III模型拟合结果较好,推导的HC5值为0.37μg·L-1;2)无脊椎动物在敌敌畏低浓度范围内的敏感性明显高于脊椎动物。甲壳类动物与昆虫和蜘蛛类相似,敏感度较高,鱼类则较低;3)应用Burr III模型构建SSD时,参数k值对HC5最为敏感,蒙特卡罗随机模拟得到HC5变化范围为0.05~40.57μg·L-1,均值为5.07μg·L-1;4)敌敌畏对我国淡水生态影响较小,PAF均低于1%,其中黄河和太湖流域敌敌畏的生态风险高于其他河流湖泊,珠江口和南海北部较低。上述研究结果为评价敌敌畏对全国不同水体水生生物的潜在生态风险提供了科学依据。     

闽西北马尾松人工林营养元素的积累与分配格局

通过定位监测与取样分析,研究了41 a生马尾松人工林生态系统中的林木、林下植被、地被物及土壤等各组分营养元素含量、积累及分配特征.对林木的养分含量分析显示,除Ca元素外,针叶的养分含量最高,其次是枝、根、皮,树干的养分含量最低.林下植被层的养分含量比较高,其养分含量大小排列顺序为Ca＞N＞K＞Mg＞P;凋落物中各元素的含量与林木养分含量基本一致;土壤中K含量最高,其次是Mg,而Ca、N、P的含量则比较低.通过对林木生产力的分析表明,马尾松的养分年积累量为110.79 kg·hm-2·a-1,其中叶占34.47%,树干占22.56%,皮、枝和根分别占21.43%、10.91%和10.63%.马尾松林生态系统养分总贮量为187864.77 kg hm-2,其中土壤占98.70%,林木占1.18%,林下植被和凋落物养分元素总贮量较低,仅占总贮量的0.12%.     

Cloning,expression, and functional identification of CaSWEET7 and CaSWEET15 genes in Canarium album北大核心CSCD

糖外排转运蛋白(sugars will eventually be exported transporters,SWEET)介导植物光合同化产物蔗糖的跨膜运输.以橄榄(Canarium album(Lour.)Raeusch.)果实为材料,通过气相色谱串联质谱(GC-MS)检测橄榄果实中糖组分及含量变化,利用RT-PCR技术克隆得到CaSWEET7和CaSWEET15基因开放阅读框(ORF)序列.结果表明:CaSWEET7和CaSWEET15基因ORF全长分别为774 bp和951 bp,分别编码长度为257个和316个氨基酸残基,具有2个MtN3_slv结构域;进化树分析表明,CaSWEET7属于CladeⅡ,CaSWEET15属于CladeⅢ.实时荧光定量PCR(qRT-PCR)技术检测其在不同发育时期的果实中相对表达量变化,结果表明,随着果实发育,CaSWEET7和CaSWEET15表达量逐渐递增,且与果实发育蔗糖含量变化呈显著正相关(相关性系数分别为0.931和0.904,P<0.05);利用酵母功能互补证明CaSWEET7和CaSWEET15基因编码的蛋白具有转运蔗糖能力.本研究表明CaSWEET7和CaSWEET15基因可能在橄榄果实蔗糖积累中发挥作用.(图9表2参44)     

Co-present Pb(II) accelerates the oxidation of organic contaminants by permanganate: Role of Pb(III)

• Simultaneous removal of organic contaminants and Pb(II) was achieved by Mn(VII). • Pb(II) enhanced Mn(VII) oxidation performance over a wide pH range. • Pb(II) did not alter the pH-rate profile for contaminants oxidation by Mn(VII). • Mn(VII) alone cannot oxidize Pb(II) effectively at pH below 5.0. • Pb(III) plays important roles on enhancing Mn(VII) decontamination process. The permanganate (Mn(VII)) oxidation has emerged as a promising technology for the remediation and treatment of the groundwater and surface water contaminated with the organic compounds. Nonetheless, only a few studies have been conducted to explore the role of the heavy metals (especially the redox-active ones) during the Mn(VII) oxidation process. In this study, taking Pb(II) as an example, its influence on the Mn(VII) decontamination performance has been extensively investigated. It was found that, with the presence of Pb(II), Mn(VII) could degrade diclofenac (DCF), 2,4-dichlorophenol, and aniline more effectively than without. For instance, over a wide pH range of 4.5–8.0, the dosing of 10 μmol/L Pb(II) accelerated the DCF removal rate from 0.006–0.25 min⁻¹ to 0.05–0.46 min⁻¹ with a promotion factor of 1.9–9.4. Although the UV-vis spectroscopic and high resolution transmission electron microscopy analyses suggested that Mn(VII) could react with Pb(II) to produce Mn(IV) and Pb(IV) at pH 6.0–8.0, further experiments revealed that Pb(II) did not exert its enhancing effect through promoting the generation of MnO₂, as the reactivity of MnO₂ was poor under the employed pH range. At pH below 5.0, it was interesting to find that, a negligible amount of MnO₂ was formed in the Mn(VII)/Pb(II) system in the absence of contaminants, while once MnO₂ was generated in the presence of contaminants, it could catalyze the Pb(II) oxidation to Pb(IV) by Mn(VII). Collectively, by highlighting the conversion process of Pb(II) to Pb(IV) by either Mn(VII) or MnO₂, the reactive Pb(III) intermediates were proposed to account for the Pb(II) enhancement effect.