基于等效粒径的无粘性泥沙起动条件对比研究

通过将等效粒径引入非均匀沙起动条件表达式,得到了基于等效粒径的非均匀沙起动条件统一表达式,并从反映泥沙的非均匀性引起的荫蔽(暴露)作用与分选作用角度对当前有一定影响的非均匀沙起动条件的等效粒径表达式进行了对比研究。结果表明,各家公式都能够反映泥沙的非均匀性引起的荫蔽(暴露)作用,较粗泥沙颗粒的等效粒径小于其自身粒径,容易起动,较细泥沙颗粒的等效粒径大于其自身粒径,较难起动。但是不同公式之间还是有一定的差异,主要反映在细颗粒的荫蔽作用方面。不同公式区分非均匀沙颗粒间荫蔽(暴露)作用的特征粒径是不同的。韩其为、张启卫、刘兴年公式能较好的反映泥沙起动时的分选作用。对于细颗粒泥沙而言,Egiazaroff、Hayashi与秦荣昱公式在冲刷时体现由于床沙粒径不同而产生的分选作用相对较差。     

Cu2+和Cd2+在蒙脱石-胡敏酸复合体上的吸附及其竞争

土壤和水体中的腐殖酸常常与粘土矿物紧密结合成为特殊的复合体.这种粘土矿物-腐殖酸复合体对重金属的吸附作用既有别于粘土矿物,更有别于腐殖酸.以蒙脱石和胡敏酸分别作为粘土矿物和腐殖酸的代表,通过一系列实验研究了Cu2+、Cd2+在单一体系和共存体系条件下在蒙脱石-胡敏酸复合体上的吸附作用,同时探讨了二者的竞争特点.实验结果表明,在单一体系条件下,蒙脱石-胡敏酸复合体对Cu2+的吸附量始终明显大于Cd2+,且二者的吸附量均随其初始浓度的增大而呈线性增大;而在Cu2+和Cd2+共存体系条件下,Cu2+的吸附量始终略大于Cd2+的吸附量,即复合体对Cu2+的吸附有较好的选择性.在吸附过程中,复合体中的蒙脱石与Cd2+和Cu2+的阳离子交换作用处于主导地位.无论是在单一体系还是在共存体系中,Cd2+优先替换电价相同而半径略大的Ca2+,而Cu2+则优先替换半径相近、电价低的Na+.因此,Cd2+的存在使Cu2+在复合体上的吸附量明显地减小,而Cu2+的存在对Cd2+的吸附几乎没有影响.这些实验结果将有助于深入探讨重金属离子在土壤、水体等环境中的迁移-固定行为.     

硅酸盐细菌在矿物表面上的吸附及其选择性——以正长石和黑云母为例

以硅酸盐细菌和正长石、黑云母为实验材料,研究了正长石和黑云母单独存在以及二者共存时,吸附时间和细菌浓度对硅酸盐细菌在其表面上吸附行为的影响。研究结果表明:1)硅酸盐细菌在正长石和黑云母上单位面积吸附量达到最大的时间分别为40min和30min,对应的细菌浓度分别为25×106个/mL和30×106个/mL;2)在细菌浓度相同时,无论是在正长石和黑云母单一矿物体系还是在二者共存体系中,正长石表面的单位面积吸附量始终大于黑云母;3)在正长石和黑云母共存体系中,硅酸盐细菌倾向于选择性吸附在正长石上,而且细菌浓度越大这种倾向越明显。实验结果有可能为研究矿物的微生物风化机理提供重要的信息。     

磷酸盐对纳米二氧化钛吸附水体中重金属离子行为的影响和机理分析

纳米二氧化钛(nTiO₂)被广泛应用于去除水体中的重金属。磷酸盐作为水体中普遍存在的无机阴离子,能够对重金属离子在nTiO₂上的吸附特征产生影响。本文聚焦磷酸盐存在条件下nTiO₂胶体颗粒对典型重金属离子(Zn²⁺和Cd²⁺)的吸附行为,以电感耦合等离子体发射光谱法(ICP-OES)测定吸附平衡后水相中重金属离子的浓度。通过批量吸附实验考察不同水化学条件下(离子强度和共存阴离子),磷酸盐对nTiO₂胶体颗粒吸附水体中Zn²⁺和Cd²⁺特征的影响规律。采用经典吸附等温线模型对实验数据进行拟合,并结合纳米颗粒的Zeta电位和粒径变化等表征手段揭示了相关吸附机制。研究发现：(1)磷酸盐的存在能有效地增强重金属在nTiO₂上的吸附,Zn²⁺和Cd²⁺的最大吸附量分别由121.1mg/g和84.7mg/g增加至588.3mg/g和434.8mg/g,增加了3...     

颗粒物与天然水体痕量有机物相互作用的动态模型

在颗粒物对水中邻苯二甲酸酯吸附、水解、生物降解和藻类富集实验的基础上,提出了颗粒物与天然水体中痕量有机物相互作用的动态数学模型.用该模型研究了邻苯二甲酸二甲酯和邻苯二甲酸二辛酯在水库中的各相浓度分布.结果表明,大多数的污染物存在于藻体和颗粒物上.     

泥沙颗粒形状对非均匀沙起动条件的影响

根据非均匀沙颗粒的不均匀性,引入颗粒形状系数,通过分析泥沙颗粒形状系数和相对暴露度的影响,建立了等效粒径表达式;并通过泥沙起动受力分析,推导得到泥沙起动临界条件表达式.实测资料验证表明,计算值与实测值符合较好.     

溶液离子强度对自然水体生物膜吸附Pb2+和Cd2+的影响

通过改变支持电解质(NaNO3)浓度的方法来探讨自然水体生物膜对Pb2 、Cd2 的吸附机制,研究了离子强度对生物膜吸附Pb2 、Cd2 的影响以及不同离子强度下生物膜吸附Pb2 、Cd2 的热力学特征.结果表明:当NaNO3浓度在0～0.4 mol·L-1之间,随着离子强度的增加,生物膜对Pb2 和Cd2 的吸附量和最大吸附量迅速降低;当NaNO3的浓度大于0.4 mol·L-1,生物膜对Pb2 和Cd2 的吸附量和最大吸附量变化趋于平缓,说明自然水体生物膜对Pb2 和Cd2 的吸附可能同时包括电性吸附和专性吸附.此外,研究还发现当Cd2 与Pb2 共存时,Pb2 对生物膜吸附Cd2 的能力有较大影响,而Cd2 对生物膜吸附Pb2 的能力的影响并不显著.     

重金属迁移转化模型研究

大量重金属污染物迁移转化的现象和研究成果都表明重金属以泥沙颗粒为载体迁移转化,描述重金属在天然水体中的迁移转化必须紧紧抓住泥沙颗粒运动及重金属与泥沙之间的转化关系进行.为此在对现有的重金属迁移转化数学模型进行概括分类的基础上,根据水沙运动与污染物相互作用关系,分析了泥沙颗粒运动及重金属吸附解吸不平衡过程,并结合水沙数学模型,建立了重金属迁移转化的耦合模型.同时在模型合理性分析的基础上,对模型进行了计算分析,分析表明模型能够合理地反映重金属污染物在水体中的迁移转化过程.     

坡缕石粘土的磷吸附机制及其铁负载效果研究

比较了3种天然坡缕石粘土对不同程度磷污染水体的吸附净化能力,通过等温吸附实验和吸附动力学实验探讨了坡缕石粘土的磷吸附机制,并研究了不同形态铁负载对坡缕石粘土吸附净化磷污染水体性能和机制的影响.结果发现,3种天然坡缕石粘土对不同程度磷污染水体均有一定的吸附净化能力,其中含白云石较多的坡缕石粘土的磷吸附能力最强,吸附等温曲线呈S型,且Freundlich方程(R2=0.977 6)比Langmuir方程(R2=0.924 9)拟合效果更好;准一级方程、冥函数方程、抛物线扩散方程、准二级方程均能较好地模拟坡缕石粘土对磷的吸附动力学过程,说明坡缕石粘土对磷的吸附可能属于不均匀介质的多分子层吸附.此外,不同形态铁负载均能显著增强坡缕石粘土对不同程度磷污染水体的吸附净化能力,吸附等温曲线呈L型,Langmnir方程(Fe2 :R2=0.96,Fe3 :R2=0.967 7)比Freundlich方程(Fe2 :R2=0.965 7,Fe3 :R2=0.936 1)能略好地拟合铁负载坡缕石粘土的磷吸附等温结果,说明铁负载坡缕石粘土的磷吸附过程可能是均匀介质的单分子吸附.适量白云石有助于提高坡缕石粘土的磷吸附净化性能,铁负载可能通过改变坡缕石的表面电荷和吸附活性位点来改变其磷吸附机制,从而提高其磷吸附性能.     

长江悬浮颗粒物中磷的赋存形态

2006年9~10月在长江采集悬浮颗粒物样品,应用改进后的SEDEX法对磷的赋存形态进行了分析.结果表明,自生磷灰石磷是长江悬浮颗粒物中磷的主要赋存形态.涪陵至万州江段,碎屑磷灰石磷的含量较高,弱吸附态磷和有机磷含量较低,磷的赋存形态主要受悬浮颗粒物含量的影响;香溪至葛洲坝下江段,弱吸附态磷和有机磷含量较高,碎屑磷灰石磷含量较低,磷的赋存形态主要受浮游植物生长及泥沙粒径的影响;城陵矶至大通江段,有机磷、碎屑磷灰石磷和铁结合态磷含量较高,弱吸附态磷含量较低,磷的赋存形态主要受泥沙粒径和洞庭湖输入的影响.长江悬浮颗粒物中生物可利用磷占颗粒态磷的45.6%,长江上游水体中生物可利用磷含量较低,下游含量较高.     

长江与黄河沉积物稀土元素随粒度变化对比研究

依据Stoke定律将长江小于63 μm的沉积物分成4个粒级.将黄河小于63 μm的沉积物分成6个粒级.采用ICP-MS法分别测试了分粒级沉积物的REE含量,结果显示：相同粒级中长江沉积物的∑REE均高于黄河沉积物.长江沉积物REE的丰度遵循元素的“粒度控制律”,即随粒度变细∑REE含量依次增高;黄河沉积物∑REE呈“高-低-高”的不对称马鞍型分布;北美页岩标准化分布曲线均呈右倾状,轻重稀土分馏明显,相对富集LREE,具弱Ce亏损,明显的Eu正异常.长江与黄河沉积物REE组成特征差异与两条河流流域的风化作用及沉积物的矿物组成密切相关,黄河∑REE的马鞍型分布是细粒级中黏土矿物吸附及粗粒级中相对高含量的重矿物富集作用的结果,而长江沉积物随粒级增大∑REE的衰减趋势主要是随粒级增大逐步增加的石英和长石含量的稀释作用所造成.     

黄河包头段不同粒级沉积物中重金属形态分布特征

以黄河包头段为研究对象,探讨了该河段不同粒级沉积物中重金属的形态分布特征,并估算了各粒级沉积物对各形态重金属的贡献率。结果表明,铁锰氧化物结合态是黄河干流各粒级沉积物中Cu、Pb和Zn非稳定态的主导形态;总体上,黄河干支流沉积物中3种重金属各形态含量均随粒级增大而减小,表现明显的粒度效应;重金属形态分布的粒度效应是沉积...     

Vermiculite bio-barriers for Cu and Zn remediation: an eco-friendly approach for freshwater and sediments protection

The increase in heavy metal contamination in freshwater systems causes serious environmental problems in most industrialized countries, and the effort to find eco-friendly techniques for reducing water and sediment contamination is fundamental for environmental protection. Permeable barriers made of natural clays can be used as low-cost and eco-friendly materials for adsorbing heavy metals from water solution and thus reducing the sediment contamination. This study discusses the application of permeable barriers made of vermiculite clay for heavy metals remediation at the interface between water and sediments and investigates the possibility to increase their efficiency by loading the vermiculite surface with a microbial biofilm of Pseudomonas putida, which is well known to be a heavy metal accumulator. Some batch assays were performed to verify the uptake capacity of two systems and their adsorption kinetics, and the results indicated that the vermiculite bio-barrier system had a higher removal capacity than the vermiculite barrier (+34.4 and 22.8 % for Cu and Zn, respectively). Moreover, the presence of P. putida biofilm strongly contributed to fasten the kinetics of metals adsorption onto vermiculite sheets. In open-system conditions, the presence of a vermiculite barrier at the interface between water and sediment could reduce the sediment contamination up to 20 and 23 % for Cu and Zn, respectively, highlighting the efficiency of these eco-friendly materials for environmental applications. Nevertheless, the contribution of microbial biofilm in open-system setup should be optimized, and some important considerations about biofilm attachment in a continuous-flow system have been discussed.     

Heavy metal accumulation in river sediments: A response to environmental pollutionSchwermetall-anreicherung in fluviatilen sedimenten als ausdruck der verschmutzung unserer umwelt

As evidenced by catastrophic cadmium and mercury poisonings in japan, heavy metals belong to the most toxic environmental pollutants. Through the investigation of sediments, the extent, distribution and provenance of heavy metal contamination in rivers and lakes can be determined and traced. Eight heavy metals from the clay fraction of sediments from major rivers within the Federal Republic of Germany were determined by means of atomic adsorption spectrometry. Heavy metals especially known for their high toxicity are enriched most: mercury, lead and zinc by a factor of 10; cadmium by a factor of 50, as compared with the natural background of these elements. A mobilisation of heavy metals from the suspended load and from the sediments, as to be observed in rivers approaching the marine enviromment, could endanger marine organisms, thus negatively influencing the acquatic food chain. With a further increase of heavy metal pollution, a threat to the drinking water supplied by rivers and lakes cannot be excluded.     

泥沙吸附重金属污染物室内静态试验研究

从吸附反应动力学方程和质量守恒方程出发,导得室内静态试验中泥沙吸附量和水相重金属浓度随时间变化的计算公式,并得出泥沙平衡吸附量和水相平衡浓度随泥沙吸附特性、水相重金属离子初始浓度和泥沙浓度变化的计算公式。结合室内试验,认为泥沙浓度不影响吸附特性参数,如饱和吸附量b、吸附-解吸速率常数k及吸附速率系数k1.     

Spatial distribution of heavy metals in surficial sediments from Guanabara Bay: Rio de Janeiro, Brazil

Ninety-two surface sediment samples were collected in Guanabara Bay, one of the most prominent urban bays in SE Brazil, to investigate the spatial distribution of anthropogenic pollutants. The concentrations of heavy metals, organic carbon and particle size were examined in all samples. Large spatial variations of heavy metals and particle size were observed. The highest concentrations of heavy metals were found in the muddy sediments from the north western region of the bay near the main outlets of the most polluted rivers, municipal waste drainage systems and one of the major oil refineries. Another anomalous concentration of metals was found adjacent to Rio de Janeiro Harbour. The heavy metal concentrations decrease to the northeast, due to intact rivers and the mangrove systems in this area, and to the south where the sand fraction and open-marine processes dominate. The geochemical normalization of metal data to Li or Al has also demonstrated that the anthropogenic input of heavy metals have altered the natural sediment heavy metal distribution.     

辽东湾周边河流沉积物碎屑矿物组成及其物源意义

对辽东湾周边七条河流下游段河漫滩沉积物的碎屑矿物进行了鉴定,分析了轻重矿物组分的差异、流域基岩类型和沉积物粒度对碎屑矿物组成的影响。轻矿物组成以石英和长石占绝对优势。由于辽东湾西侧河流（六股河、小凌河和大凌河）和东侧河流（双台子河、大辽河、复州河）位于两个构造块体之上,不同的基岩类型导致重矿物组合差别很大。湾西河流普通角闪石含量低、金属矿物含量高,湾东河流则相反,这两种组分能有效区分辽东湾东西两侧的河流,同时也可将滦河与上述河流区分开。石榴子石和普通辉石含量特征可区分湾西三条河流,特征为大凌河前者含量高,小凌河后者含量高,六股河两者含量都很低。绿帘石和阳起石的含量在湾东河流沉积物中差别较大,特征为双台子河前者含量高,大辽河后者含量高,复州河两者含量都很低。七条河流片状矿物和碳酸盐矿物含量低的特征有别于黄河沉积物。     

Heavy metal anomalies in the Tinto and Odiel River and estuary system,Spain

The Tinto and Odiel rivers drain 100 km from the Rio Tinto sulphide mining district, and join at a 20-km long estuary entering the Atlantic Ocean. A reconnaissance study of heavy metal anomalies in channel sand and overbank mud of the river and estuary by semi-quantitative emission dc-arc spectrographic analysis shows the following upstream to downstream ranges in ppm (μg g^?1): As 3,000 to <200, Cd 30 to <0.1, Cu 1,500 to 10, Pb 2,000 to <10, Sb 3000 to <150, and Zn 3,000 to <200. Organic-rich (1.3–2.6% total organic carbon, TOC), sandysilty overbank clay has been analyzed to represent suspended load materials. The high content of heavy metals in the overbank clay throughout the river and estuary systems indicates the importance of suspended sediment transport for dispersing heavy metals from natural erosion and anthropogenic mining activities of the sulfide deposit. The organic-poor (0.21–0.37% TOC) river bed sand has been analyzed to represent bedload transport of naturally-occurring sulfide minerals. The sand has high concentrations of metals upstream but these decrease an order of magnitude in the lower estuary. Although heavy metal contamination of estuary mouth beach sand has been diluted to background levels estuary mud exhibits increased contamination apparently related to finer grain size, higher organic carbon content, precipitation of river-borne dissolved solids, and input of anthropogenic heavy metals from industrial sources. The contaminated estuary mud disperses to the inner shelf mud belt and offshore suspended sediment, which exhibit metal anomalies from natural erosion and mining of upstream Rio Tinto sulphide lode sources (Pb, Cu, Zn) and industrial activities within the estuary (Fe, Cr, Ti). Because heavy metal contamination of Tinto-Odiel river sediment reaches or exceeds the highest levels encountered in other river sediments of Spain and Europe, a detailed analysis of metals in water and suspended sediment throughout the system, and epidemiological analysis of heavy metal effects in humans is appropriate.     

鸭绿江河口西岸潮间带柱状沉积物中重金属的分布特征及其对流域变化的响应

2010年和2011年在鸭绿江西水道和西岸潮间带共采集4根柱状样,通过对2mPb测年、粒度、总有机碳、重金属元素等多指标综合分析,探讨了：（1）鸭绿江河口西水道和西岸潮间带柱状沉积物中重金属的垂向分布及其来源：（2）重金属分布的粒度控制作用：（3）不同时期的粒度和重金属分布变化及其对流域变化的响应。结果表明：f1）Cu和zn可能来源于有机质降解的内源释放：Cr和Ni表征了岩石风化剥蚀形成陆源碎屑的自然来源：Cd和Pb反映了人类活动的影响。（2）除西岸潮间带的Cd和Pb含量可能部分受来源影响外,研究区的粒度效应是控制鸭绿江地区重金属含量分布的最主要因素。（3）粒度变化与流域演变密切相关,重金属含量对流域变化和人类活动响应明显,大致以1940年、1970年、1995年为界分为四个沉积阶段：1940年以前,自然演变对鸭绿江河口西岸潮间带的重金属分布控制明显,而1940年来至今,人类活动的控制作用日益凸显。