多孔柔性载体在非流化状态下处理污水的效能

对自行研制的多孔柔性载体在非流化状态下,处理低浓度有机污水的效能及生物活性进行了试验,结果表明：污水经处理后,检测指标ＣＯＤＣｒ去除率８０％以上,ＢＯＤ５去除率９０％以上;多孔柔性载体表面附着生物活性较高,可作为良好的生物载体。     

曲霉AH625产酶条件与酶液降解制备壳寡糖

从特定土壤中分离出一株能分泌胞外甲壳酶的高产菌株曲霉AH62 5 ,在以甲壳素为唯一碳、氮源的平板上长势良好 ,该菌株在生长培养基中振荡培养 72h ,再转移至诱导培养基中培养 2 4h ,酶活力可达 0 .51 2u/mL。研究表明 ,该菌株的最佳产酶条件是 :温度2 8℃ ,起始 pH4 .8,诱导底物为 1 .5 %的水溶性壳聚糖 ,0 .1 %的表面活性剂Tween80能使产酶量提高 2～ 3倍。用粗酶液在 50℃ ,pH5 .0条件下降解壳聚糖 ,得Mw 为 1 1 2 7,Mw/Mn 为 1 .53的壳寡糖。     

Carbon dioxide and methane emission from subsurface peatlands and its controlling factors北大核心CSCD

Peatland is an efficient carbon dioxide (CO2) sink on the continent and plays an important role in global carbon cycle. Climate change and human activities, two of the notable global environmental issues, have accelerated the degradation of peatlands during recent years. Global warming will increase the rate of aerobic decomposition in the surface of peatlands. Carbon stored in the subsurface of peatlands will be metabolized if the climatic conditions become favorable for decomposition. This study reviewed the carbon circle of subsurface peatland in natural environment and in environments disturbed by human activity or climate change. Furthermore, the major factors (environmental and human factors) that affect the carbon cycle were also discussed. According to a previous study, subsurface peatland will rapidly participate in the carbon cycle when the peatland is degraded. Water level, vegetation, and temperature were the main natural factors affecting the carbon cycle, whereas drainage, farming, and grazing were the main anthropogenic factors. Further studies should focus on different soil layer carbon dynamics, inorganic carbon content, and conservation and restoration of peatlands. The study methods should be a combination of macro with micro scale and focus on developing deep peat research techniques. Most of the previous studies focused on greenhouse gas emission and their response factors in short-term experiments. Thus, the mechanism and process of subsurface carbon are not clear and needs further study. © 2018 Science Press. All rights reserved.     

刈割对牧草地下部根区土壤养分及土壤酶活性的影响

对不同刈割强度对牧草地下部根区土壤养分状况及土壤酶活性进行了研究,结果表明,牧草刈割对根区土壤养分、土壤酶活性和土壤微生物数量存在一定影响。不同刈割强度对牧草根区土壤有机质、全磷和全钾含量无明显影响。土壤全氮、碱解氮、速效磷、速效钾含量均因刈割强度的增加而显著下降。土壤蔗糖酶、脲酶活性因刈割处理强度的增加而下降;土壤过氧化氢酶活性则表现为相反的变化趋势。刈割对土壤微生物总数量的影响较大,表现为轻刈割>不刈割>重刈割。     

除草剂硝磺草酮对土壤微生物生态效应研究

采用室内培养试验,研究了硝磺草酮对土壤酶活性和微生物群落功能多样性的影响.结果表明,土壤过氧化氢酶和蔗糖酶活性随硝磺草酮浓度增加呈现先增加后降低的趋势,但比对照处理都有所升高,分别增加了22.6%~41.0%和3.4%~54.2%,且在硝磺草酮浓度为50mg/kg时达到最大.与之相反,尿酶活性则降低了12.0%~18.6%,但差异性不明显(P > 0.05).施用一定浓度的硝磺草酮激活了土壤微生物活性,微生物群落丰富度、均匀性和多样性都呈增长趋势,单孔的平均颜色变化率(AWCD)值和利用速率均随硝磺草酮浓度增加而增大,微生物群落对碳水化合物类、氨基酸类、多聚物类、羧酸类、胺类和酚酸类利用率整体上均有所提高,与对照相比,最大增幅分别达到5.3、1.0、4.4、3.2、0.2和6.8倍,但不同浓度硝磺草酮处理下土壤微生物在利用碳源的类型上是存在一定的差异.     

镉胁迫对苎麻(Boehmeria nivea)根系及叶片抗氧化系统的影响

镉(Cd)是非必需和毒性最强的重金属元素之一,不合理的开发利用可导致土壤受到Cd的严重污染,严重危及土壤环境或水环境。以苎麻为材料,采用模拟镉(Cd)污染盆栽培养法,选择21 d和49 d等2个不同胁迫期,测定不同浓度Cd2+胁迫下苎麻根系与叶片中渗透调节物质含量、超氧化物岐化酶(SOD)活性、过氧化物酶(POD)活性、过氧化氢酶(CAT)活性、丙二醛(MDA)含量及根系活力的变化。结果表明,高浓度胁迫49 d后,苎麻根系中的渗透调节物质含量明显高于叶片含量,且极显著高于对照,并在240 mg·L~(-1)Cd处理下出现最高值;胁迫49 d时,根系与叶片的渗透调节物质含量与Cd2+浓度极显著正相关。在2个不同胁迫周期,苎麻根系的SOD与POD活性均明显高于叶片;在胁迫21 d时,根系的CAT活性低于叶片,而胁迫49 d后,则明显高于叶片;胁迫21 d时,苎麻根系与叶片的抗氧化酶活性均较胁迫49 d要高;胁迫49 d时,根系POD活性与Cd2+浓度呈极显著正相关,表明根系POD酶在抗氧化酶中占主导地位。不同胁迫时长下苎麻根系或叶片的MDA含量变化趋势不明显,但根系或叶片受胁迫21 d后的MDA含量随Cd2+浓度增加的波动相对受胁迫49 d后的更明显,表明植物早期生理功能出现暂时性的修复。2个不同胁迫周期内,不同浓度镉胁迫下苎麻的根系活力均比对照组下降。研究显示,苎麻根系与叶片对镉胁迫的应答机制不同,且在不同胁迫时间下的响应机理差异较大,根系表现出更强的耐受能力。     

赣南某钨矿区土壤重金属污染状况研究

为研究钨矿区土壤重金属的污染现状,采集尾矿堆积区土壤样品,用ICP-MS测定土壤重金属(Cr、As、Mn和Pb)含量,采用Kriging插值法分析土壤重金属的空间分布特征,并分析测定土壤脲酶、过氧化氢酶、蔗糖酶的活性.结果表明土壤重金属的浓度均值高于背景值,Cr、As、Mn、Pb的均值分别是土壤背景值的2.26,3.06,1.85和2.59倍.空间分析表明Mn和Pb间两种元素具有较为相似的分布,Cr、As、Mn和Pb 4种重金属的空间分布相关性强,且呈条带状分布.土壤酶活性结果进一步验证重金属的污染状况,土壤酶活性低于对照样,土壤脲酶、过氧化氢酶、蔗糖酶分别是对照的7%~93%和5%~86%、11%~90%.逐步多元回归法分析表明,在Cr、As、Mn、Pb复合污染条件下,矿区土壤不同酶活性表现出抑制或者激活作用,但各重金属元素对不同的酶活性的影响系数是不一样的,蔗糖酶对复合重金属污染最为敏感. 主成分分析表明土壤酶活性的指标能较好地反映钨矿矿区土壤重金属复合污染状况.     

Simultaneous copper bioaccumulation,growth and lipase production of Rhizopus delemar in molasses medium: optimisation of environmental conditions using RSM

In this study, the bioaccumulation of Cu(II) ions by R. delemar and their influence on growth of the microorganism were assessed, and the impact of Cu(II) ions on the activity of lipase enzyme degradation of lipids in wastewaters by enzymatic hydrolysis was received for consideration. Optimisation of Cu(II) bioaccumulation process was performed by varying three independent parameters (pH, temperature and Cu(II) concentration) using a central composite design (CCD) under response surface methodology (RSM). For the maximum Cu(II) bioaccumulation and lipase production at a desired level of the biomass concentration level, a total of 20 experimental runs were set and the experimental data fitted to the empirical second-order polynomial models. The adequacies of the predicted models for the Cu(II) bioaccumulation, lipase activity and biomass concentration were confirmed by the coefficients of multiple regression (R²), which were adjusted to be 99.6%, 94.5%, 93.4%, respectively indicating reasonably good models for practical implementation. A maximum Cu(II) bioaccumulation of 36.81 mg/L was obtained at pH 6.0, at 32.6°C, and at 50 mg/L initial Cu(II) concentration. The lipase activity of R. delemar decreased only from 505 U/L in Cu(II)-free fermentation medium to 476 U/L in the presence of Cu(II) giving 5.74% decrease in lipase activity.     

土壤酶和微生物量碳对土壤低浓度重金属污染的响应及其影响因子研究

土壤酶和微生物量碳是反映土壤健康的重要微生物性质指标。土壤重金属污染能够对土壤微生物性质产生影响,然而土壤酶和微生物量碳对土壤重金属污染的响应受到土壤本身理化性质的影响。通过北京市建成区233个样点的数据监测和实验室模拟,研究了土壤脲酶活性和微生物量碳对土壤低浓度重金属污染的响应以及受土壤理化性质的影响。研究结果表明:在野外主要重金属污染的浓度范围内(Cd 0.003~0.98μg·g-1,Cu 13.4~207.9μg·g-1,Zn 29.4~322μg·g-1,Pb 4.02~174μg·g-1),土壤脲酶活性、微生物量碳(MBC)和有机碳(SOC)的含量与土壤中Cd、Cu、Zn和Pb的浓度正相关,而微生物量碳占有机碳的比率(MBC/SOC)与重金属浓度负相关;脲酶活性、MBC/SOC与重金属浓度建立的相关关系只能解释总变异的5%~10%。实验室模拟试验表明,土壤酶活性受土壤重金属含量和土壤性质联合效应的影响;土壤有机质含量和pH是影响酶活性的主要土壤理化性质。引入土壤有机碳含量和pH两个参数,重新建立脲酶活性、MBC/SOC与土壤中重金属浓度的关系,建立的相关关系的决定系数变大,能够解释总变异的14%~17%。     

皇竹草对土壤阿特拉津的降解特性

为了探明种植皇竹草(Pennisetum hydridum)对土壤阿特拉津降解的促进作用,通过盆栽试验研究了皇竹草对土壤阿特拉津的降解动态、转移特征以及土壤阿特拉津残留浓度与土壤相关酶活性的关系。结果表明:与未种植皇竹草相比,种植皇竹草土壤阿特拉津降解率明显提高,皇竹草对未灭菌和灭菌土壤阿特拉津的降解率分别提高52.84和42.38百分点;与未种植皇竹草处理相比,灭菌和未灭菌条件下种植皇竹草处理阿特拉津在土壤中的半衰期可分别缩短64.35和53.21 d;土壤中阿特拉津被皇竹草吸收后逐步由地下部分向地上部分转移,随着培养时间的延长,转移系数变大;土壤中阿特拉津残留浓度与土壤过氧化氢酶、过氧化物酶、转化酶和多酚氧化酶活性呈显著负相关(P0.05或P0.01)。认为种植皇竹草有助于阿特拉津的降解。