饮用水中磷与细菌再生长的关系

采用改进的可同化有机碳(AOC)和微生物可利用磷(MAP)方法,针对T市J水厂水源水、处理工艺以及一条配水干管中磷对细菌生长的限制作用进行了研究.结果表明:①水源水与处理工艺中MAP较高(5～38μg/L),配水管网中MAP较低(<5μg/L),且管网水中的MAP随着管线的延长基本保持不变.②常规处理工艺能够有效地去除水中的MAP(去除率为34.0%～83.7%).③在水源水和处理工艺中,水样的AOC_{potential<、sub>、AOCP与AOCnative没有显著差别,说明AOC是微生物生长繁殖的决定因素.该研究配水干管中,水样的AOCpotential、AOCP为AOCnative的2～8.7倍,磷成为细菌再生长的限制因子.}     

区域土壤质量对土地利用变化响应研究——以土壤氮元素为例

选取长江三角洲典型地区--原锡山市作为研究区域,以1982和2005年土壤全氮和速效氮作为研究对象,探讨区域土地利用变化对土壤氮含量的影响。通过统计分析表明,20年来原锡山市土壤全氮含量降低016 g/kg,速效氮含量降低763 mg/kg。通过变异函数分析,20年来原锡山市全氮和速效氮的变异函数理论模型呈指数型,但块金方差与基台值的比值、自相关阀值发生了较大变化;Kriging插值分析结果表明,1982年全氮和速效氮分布较简单,2005年全氮分布较复杂,速效氮分布较简单,同时kriging插值分析还表明,20年来原锡山市土壤全氮含量降低,空间变异变化显著;土壤速效氮含量变化较小,空间差异变化明显。     

醋酸改性纳米黑碳对Cu~(2+)、Cd~(2+)吸附能力的研究

用醋酸对黑碳进行改性,通过改性纳米黑碳(MBC)对Cu2+、Cd2+的吸附/解吸试验,探究MBC对Cu2+、Cd2+的吸附特性及吸附稳定性。结果表明,Cu2+和Cd2+在MBC上的吸附动力学过程可分为快吸附和慢吸附两个阶段,且MBC对Cu2+的吸附效率大于Cd2+。Cu2+和Cd2+在MBC上的吸附等温线均能用Langmuir和Freundlich方程拟合,Cu2+和Cd2+在MBC上的最大吸附量分别为13.513、11.364mg/g,且MBC对Cu2+和Cd2+均为优惠吸附。MBC上Cu2+和Cd2+的解吸量均随着吸附量的增加而增大,易解吸态Cu2+在MBC上的解吸率为6.12%~10.25%,Cd2+为9.58%~11.81%,MBC对Cu2+的吸附稳定性大于Cd2+。将醋酸改性与已有改性方法对比,表明醋酸改性条件温和、能耗低、经济环保,将有很大的研发前景。     

烧结机共处置过程中重金属Cd、As的挥发特性研究

选取优级纯化学试剂Cd Cl2和As2S3来模拟危险废物中的重金属,按一定比例将其与烧结矿原料均匀混合后进行共处置煅烧。主要研究了在煅烧过程中Cd和As的挥发规律,同时对煅烧所得烧结矿进行消解实验求得固化的重金属量。实验结果表明,Cd的挥发率随着温度的升高和时间的增加而不断增大,直到达到一个平衡而不再继续增大,对Cd的挥发进行动力学模拟得到挥发率α与煅烧温度T和煅烧时间t的关系式为α=1-exp(-0.669exp(-3567.6/T)t)。而As则呈现出温度越高挥发率越低的规律,当温度为1 200℃时,煅烧75 min后As的挥发率仅为9.8%,即共处置过程中As与烧结矿原料发生化学反应而固化下来,挥发较少,可认为对人体健康和环境造成的危害较小。     

乙二胺还原的氧化石墨烯对镉离子的动态吸附

以乙二胺(EDA)还原氧化石墨烯(GO)制得一种吸附剂材料,即还原态氧化石墨烯(RGO)。考察了动态条件下Cd2+溶液的初始浓度、流速及吸附床高度对穿透曲线的影响,同时利用Bed-Depth-Service Time(BDST)模型对吸附床高度与穿透时间的关系进行线性拟合分析,研究了RGO对Cd2+溶液的动态吸附性能。结果表明,RGO可以有效地去除水溶液中的Cd2+,随着吸附床高度的增加,离子的去除率增大,穿透时间延长;当溶液初始浓度增大时穿透时间缩短,离子的去除率减小;而溶液的流速加快,穿透时间和去除率都相应减小。吸附床高度与穿透时间的关系可用BDST模型较好地进行描述,预测新的操作条件下的穿透时间与实验值误差均小于5%。     

生物质炭对溶液中Cd~(2+)的吸附

以玉米秸秆、稻壳在350~500℃制成的生物质炭作为吸附剂,研究其对溶液中Cd2+的吸附特性。通过模拟实验,考察了初始p H、生物质炭用量、吸附时间和Cd2+的起始浓度对吸附的影响。结果表明,2种生物质炭对Cd2+的吸附反应适应p H范围较宽(4.0~7.0);玉米秸秆炭和稻壳炭对Cd2+的吸附速度较快,分别在10和20 min时达到吸附平衡;玉米秸秆炭对溶液中Cd2+的吸附遵循Langmuir等温线模型,而稻壳炭对Cd2+的吸附遵循Freundlich等温线模型。在实验设定的条件下,玉米秸秆炭对溶液中Cd2+的吸附能力强于稻壳炭。     

Remediation capacity of Cd and Pb ions by mycelia of Imleria badia,Laetiporus sulphureus,and Agaricus bisporus in vitro cultures

The goal of this study was to evaluate cadmium and lead accumulation ability of in vitro cultures biomass containing selected edible mushroom species derived from the environment (Laetiporus sulphureus, Imleria badia) and those of commercial origin (Agaricus bisporus). Atomic absorption spectrometry was used to evaluate the content of Cd(II) and Pb(II) on the medium supplemented with Cd(II) or Pb(II), each of them at the same concentration of 5·10^?5 M. The highest concentration of Cd(II) ions was determined in the biomass from L. sulphureus in vitro cultures, while the highest concentration of Pb(II) ions was found in the biomass from A. bisporus in vitro cultures. The greatest Cd(II) and Pb(II) accumulation ability in mycelium per dry weight was shown for L. sulphureus. Among the test species, biomass of A. bisporus showed the lowest ability for the bioaccumulation of Cd(II); however, comparable ability for the remediation of Pb(II) was provided by the biomasses from A. bisporus and I. badia in vitro cultures. The results confirm the possibility of using these mushroom species for remediation and indicate the relationship between bioaccumulation of heavy metals and the test species.     

The effects of alginate microspheres on phytoremediation and growth of Lemna minor in the presence of Cd

Today, the removal of increased amount of contaminant concentrations in nature such as metals, nanoparticles, has become an essential issue to struggle with. In this paper, both the toxic effects of non-essential Cd on Lemna minor in presence of alginate microspheres and metal removal capacity of Cd-exposed L. minor and microspheres were investigated. Three test groups were constructed: group (L) containing Lemna, group (M) containing alginate microsphere and group (L?+?M) containing alginate microsphere and Lemna. Five different levels of Cd concentrations were added into these groups. Estimation models were constructed to estimate Cd removal capacities of L. minor and microspheres, and time-concentration-dependent growth (GRC) rates of both microsphere-containing and non-containing groups were modelled by regression analysis. It was seen that microspheres alone only had no positive or negative effects on Lemna growth. It was observed that, for all test groups the time-dependent growth rate has both increase–decrease trends in general. The toxicity effect of Cd on Lemna growth was reduced by adding microspheres into medium. Furthermore, the results stated that test groups containing only microspheres (M, 0–97.56%) and consortium groups (M?+?L, 0–98.26%) were slightly more successful in Cd removal process compared to Lemna (L) groups (L, 0–97.32%).     

Characterisation of early responses to cadmium in roots of Salix matsudana Koidz

This study deals with the characterisation of early responses of roots of Salix matsudana in respect to oxidative stress, subcellular distribution, and chemical forms when exposed to 50 μmol/L Cd. Within 12 h, the root length is reduced and the contents of O₂^??, H₂O₂, and malondialdehyde are increased by 49%, 43%, and 35%. Cd is mainly retained in the cell walls; small amounts are distributed into other cell organelles. The largest proportion of Cd is found in the NaCl extractable, pectate-, and protein-integrated fraction.     

Biodynamic modelling and the prediction of accumulated trace metal concentrations in the polychaete Arenicola marina

The use of biodynamic models to understand metal uptake directly from sediments by deposit-feeding organisms still represents a special challenge. In this study, accumulated concentrations of Cd, Zn and Ag predicted by biodynamic modelling in the lugworm Arenicola marina have been compared to measured concentrations in field populations in several UK estuaries. The biodynamic model predicted accumulated field Cd concentrations remarkably accurately, and predicted bioaccumulated Ag concentrations were in the range of those measured in lugworms collected from the field. For Zn the model showed less but still good comparability, accurately predicting Zn bioaccumulation in A. marina at high sediment concentrations but underestimating accumulated Zn in the worms from sites with low and intermediate levels of Zn sediment contamination. Therefore, it appears that the physiological parameters experimentally derived for A. marina are applicable to the conditions encountered in these environments and that the assumptions made in the model are plausible.