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排序方式: 共有170条查询结果,搜索用时 46 毫秒
41.
苯酚的生物降解一直受到关注。以苯酚为惟一电子供体,研究了Shewanellasp.XB对苯酚的缺氧降解特性。研究结果表明,在反硝化条件下,当C/N为13.3时,苯酚可以完全降解,NO2--N积累量很少。另外,当加入氧化还原介体,如核黄素3μmol/L、AQDS0.01mmol/L、AQS0.05mmol/L和LQ0.01mmol/L时,苯酚降解速率分别为不加介体时的1.45、1.77、1.67和1.63倍。当以氯化铵代替硝酸盐时,苯酚也能进行厌氧发酵降解。另外,菌株XB反硝化降解苯酚可能是厌氧和好氧降解的混合过程。 相似文献
42.
苯酚的生物降解一直受到关注。以苯酚为惟一电子供体,研究了Shewanella sp.XB对苯酚的缺氧降解特性。研究结果表明,在反硝化条件下,当C/N为13.3时,苯酚可以完全降解,NO-2-N积累量很少。另外,当加入氧化还原介体,如核黄素3μmol/L、AQDS 0.01 mmol/L、AQS 0.05 mmol/L和LQ 0.01 mmol/L时,苯酚降解速率分别为不加介体时的1.45、1.77、1.67和1.63倍。当以氯化铵代替硝酸盐时,苯酚也能进行厌氧发酵降解。另外,菌株XB反硝化降解苯酚可能是厌氧和好氧降解的混合过程。 相似文献
43.
醌介体催化强化酸性红B生物脱色 总被引:3,自引:0,他引:3
考察了5种结构相似的醌介体(AQS、2,7-AQDS、AQDS、1,5-AQDS和α-AQS)对酸性红B生物脱色的催化强化作用。结果表明,反应进行至5 h,在0~0.24 mmol/L AQS的浓度范围内,最高脱色率达89%(0.24 mmol/L),相对于空白组(28%)提高约3.2倍,且零级反应速率常数K与介体浓度呈正相关线性关系,K=56.571CAQS+22.616(R2=0.9012);最适实验条件为AQS浓度0.24 mmol/L,0.25%NaCl,温度35℃,pH 7;在此实验条件下,5种醌介体相对于空白组脱色效率分别提高了1.14~1.53倍,体系氧化还原电位降低了38~87 mV。本研究为解决偶氮染料生物脱色技术存在的降解速率低的问题提供了新的思路。 相似文献
44.
土壤原位覆盖对底泥的修复作用研究 总被引:2,自引:0,他引:2
在高度厌氧底泥和富营养化水体构成的模拟生态系统中,采用土壤和硅藻土进行原位覆盖,研究了覆盖技术对水.沉积物界面微环境的改善作用和不同覆盖材料对苦草生长的影响。这2种底质覆盖后,表层底泥氧化还原电位(Eh)分别提高了48.37%和46.77%,底层水体的溶解氧消耗降低,水体中的总氮(TN)和总磷(TP)含量降低;与对照箱体的苦草死亡相比,经过土壤和硅藻土覆盖的箱体中苦草正常萌发、定植和生长;硅藻土箱体苦草的生物量、叶绿素和根茎比均高于土壤覆盖箱体。因此,原位覆盖能有效改善底层水体和表层底泥的氧化还原环境,隔绝污染底泥和延缓营养盐释放,为沉水植物种子萌发和幼苗生长提供有利的生境条件。 相似文献
45.
Selective redox degradation of chlorinated aliphatic compounds by Fenton reaction in pyrite suspension 总被引:1,自引:0,他引:1
Selective redox degradation of chlorinated aliphatics by Fenton reaction in pyrite suspension was investigated in a closed system. Carbon tetrachloride (CT) was used as a representative target of perchlorinated alkanes and trichloroethylene (TCE) was used as one of highly chlorinated alkenes. Degradation of CT in Fenton reaction was significantly enhanced by pyrite used as an iron source instead of soluble Fe. Pyrite Fenton showed 93% of CT removal in 140 min, while Fenton reaction with soluble Fe(II) showed 52% and that with Fe(III) 15%. Addition of 2-propanol to the pyrite Fenton system significantly inhibited degradation of TCE (99% to 44% of TCE removal), while degradation of CT was slightly improved by the 2-propanol addition (80-91% of CT removal). The result suggests that, unlike oxidative degradation of TCE by hydroxyl radical in pyrite Fenton system, an oxidation by the hydroxyl radical is not a main degradation mechanism for the degradation of CT in pyrite Fenton system but a reductive dechlorination by superoxide can rather be the one for the CT degradation. The degradation kinetics of CT in the pyrite Fenton system was decelerated (0.13-0.03 min−1), as initial suspension pH decreased from 3 to 2. The formation of superoxide during the CT degradation in the pyrite Fenton system was observed by electron spin resonance spectroscopy. The formation at initial pH 3 was greater than that at initial pH 2, which supported that superoxide was a main reductant for degradation of CT in the pyrite Fenton system. 相似文献
46.
ABSTRACTThe effects of the flooding and initial Eh of sediments on the sorption of uranium onto the sediments were analysed by flooding and static experiments. The changes in uranium species with Eh and kinetic and thermodynamic characteristics of the uranium sorption onto the sediments were investigated. The flooding experiment indicates that the initial Eh of the sediment gradually decreased with the increase in flooding time. Based on the redox potential in the flooding experiment, simulation results obtained using the geochemical simulation software PHREEQC show that the concentration of U (VI) decreased. In contrast, the concentrations of U (III), U (IV), and U (V) gradually increased. The pseudo-second-order kinetic model well fitted the experimental data, which shows that the sorption was mainly chemical sorption. The thermodynamic parameters suggest that the entropy and enthalpy under the used conditions were positive and that ΔGθ was negative. A thermodynamic analysis shows that the sorption was endothermic and spontaneous. These results are useful for the understanding of the sorption mechanism and migration of uranium onto the sediment under different initial sediment redox potentials and provide a good theoretical foundation for radioactive pollution remediation. 相似文献
47.
Mark E. Hines 《Water, Air, & Soil Pollution: Focus》2006,6(5-6):523-536
Microorganisms are responsible for the bulk of transformations that occur in surficial sediments. They are most active at
redox boundaries where they can benefit from access to various oxidants and reductants generated during redox cycling events.
To illustrate the dynamics of microbially mediated processes, especially those involving sulfur and metal cycles, processes
were compared in habitats either bioturbated by a capitellid worm or inhabited by a salt marsh grass. The presence of macrofauna
and macroflora greatly altered the three-dimensional array of redox gradients in sediments, but the type and form of reductants
and oxidants provided varied greatly; clastic sedimentary infauna subducted solid phase organic material and iron oxides,
whereas plant roots released dissolved organic matter and oxygen. These differences resulted in a bioturbated system that
exhibited a rapid sulfur cycle (residence time of minutes), but a slower iron cycle (days), whereas vegetation caused a slow
sulfur cycle and rapid iron cycle. Alteration of sediments by higher life forms also greatly affected the composition and
relative abundances of sedimentary bacteria, even on short time scales. Although redox cycling at interfaces can be somewhat
predictable, variations in response to biological and physical perturbations demonstrated wide differences in the dynamics
of redox-mediated processes. 相似文献
48.
A benthic in situ flume and a 1D biogeochemical sediment model to evaluate solute fluxes across the sediment–water interface have been developed.
The flume was successfully used to determine oxygen and nutrient fluxes at various locations of the Neckar River in Germany.
The experimental results were linked with vertical pore water concentration profiles and independently verified with the model.
By combining experimental and model results we assessed the influence of dissolved oxygen concentrations in the water column
and the availability of degradable organic matter on sediment oxygen demand. The results and the derived relations can be
used to parameterize the sediment module of large scale water quality models, allowing one to assess the influence of sediment–water
interactions on various aspects of river water quality. Moreover, the biogeochemical sediment model can help to improve the
general understanding of the processes governing solute concentrations and fluxes in sediments and across their interfaces. 相似文献
49.
50.
氧化还原介体催化强化Paracoccus versutus菌株GW1反硝化特性研究 总被引:2,自引:2,他引:0
考察了Paracoccus versutus菌株GW1的醌呼吸特性及4种结构相似的醌类介体(AQS,α-AQS,AQDS和1,5-AQDS)催化强化Paracoccus versutus菌株GW1的反硝化过程.结果表明,Paracoccus versutus菌株GW1能利用醌类介体作为其电子传递链中的电子受体进行呼吸,使醌类介体还原为相应的氢醌形式;在35℃条件下,采用间歇试验法,4种介体浓度均为0.24mmol.L-1时,可分别提高硝酸盐氮降解速率1.14~1.63倍、总氮去除速率1.12~2.02倍,其从大到小顺序为:AQDS>1,5-AQDS>AQS>α-AQS;介体可降低Paracoccus versutus菌株GW1硝酸盐降解过程中氧化还原电位约33~75 mV;介体催化强化硝酸盐降解过程中pH变化趋势与空白对照组类似,最终pH稳定在9.0左右;在0~0.32 mmol.L-1AQDS浓度范围内,体系硝酸盐氮降解零级反应速率常数K与介体的浓度cAQDS呈线性关系.本研究为解决生物脱氮技术存在降解速率低的问题提供了有效途径. 相似文献