普萘洛尔在太湖沉积物上的吸附特征

主要研究了pH、离子强度、腐殖酸和沉积物有机质对普萘洛尔在太湖沉积物上吸附行为的影响.结果表明,沉积物对普萘洛尔具有一定的吸附能力.在强酸环境下,由于H+与带正电荷的普萘洛尔之间的竞争作用使得普萘洛尔的吸附量较小,随着pH的增大,吸附量逐渐增大至基本稳定,但当pH＞9时,吸附量明显下降.K+、Na+和Ca2+的存在会减...     

不同粒径沉积物对1,2,4,5-四氯苯的吸附/解吸特性

采用静态吸附实验,研究不同粒径沉积物的基本性质及其对1,2,4,5-四氯苯吸附/解吸性能的影响.结果表明,不同粒径沉积物所含天然有机质(NOM)质和量的不同,导致其对1,2,4,5-四氯苯吸附性能的不同.颗粒最细的沉积物因其主要结合聚合度较低的无定型腐殖物质,导致1,2,4,5-四氯苯吸附等温线的非线性程度最低,在沉积物上的吸附亲和力和吸附.解吸滞后现象也最弱.而颗粒最粗的沉积物因为含有一些煤炭和木炭等高比表面积的碳黑类物质,NOM聚合度较高,导致1,2,4,5-四氯苯吸附等温线的非线性程度最高,在沉积物上的吸附亲和力和吸附-解吸滞后现象也最强.而粒径中等的沉积物本身的性质和吸附性能介于颗粒最粗和最细的两种组分之间.     

黄河中下游沉积物对磷酸盐的吸附动力学研究

研究了黄河中下游10个不同表层沉积物在黄河水体中对磷酸盐（P）的吸附动力学及其影响因素和吸附机理。结果表明：（1）不同黄河沉积物对P的吸附能力各不相同,但吸附量随时间的变化具有相同的变化趋势,吸附速率均在前8h内较快,以后逐渐趋缓,在48h时基本达到吸附平衡。不同黄河沉积物对P的吸附量均随P初始质量浓度的增加而增大,随沉积物含量增大而减小;（2）不同沉积物在不同P初始质量浓度下对P的吸附动力学均符合Lagergren二级吸附动力学模型及Weber-Morris扩散方程,求得二级吸附速率常数和扩散速率常数分别在11.9866～157.55g·mg^-1·h^-1和0.0005～0.0119mg·g^-1·h^-1/2之间,吸附过程由P在沉积物内扩散控制。     

黄河上游沉积物对磷酸盐的吸附动力学研究

研究了黄河上游10个不同表层沉积物在黄河水体中对磷酸盐（P）的吸附动力学及其影响因素和吸附机理。结果表明：不同黄河沉积物对P的吸附能力各不相同,但吸附量随时间的变化具有相同的趋势,吸附速率均在前8 h内较快,以后逐渐趋缓,在48 h时基本达到吸附平衡。不同黄河沉积物对P的吸附量均随P初始质量浓度的增加而增大,随沉积物质量浓度增大而减小,且也受水体pH值的影响,在pH为6.0~9.0范围内吸附量比较大。不同沉积物在不同P起始质量浓度下对P的吸附动力学均符合Lagergren二级吸附动力学模型及Weber–Morris扩散方程,求得二级吸附速率常数和扩散速率常数分别在10.85~229.29 g.mg-1.h-1和0.7×10-3~5.2×10-3 mg.g-1？h-1/2）之间,吸附过程由P在沉积物内的扩散控制。     

沉积物不同天然有机组分对氨氮吸附特征的影响

为估算沉积物不同天然有机组分吸附态氨氮携载量．采用平衡吸附法研究西辽河沉积物不同天然有机组分对氨氮吸附特征的影响。结果表明,去除有机质后的沉积物对氨氮的吸附能力大大降低,其碳标化饱和吸附量（Гmoc）和吸附分配系数（Koc）分别为重组的55．30％和69．49％,说明有机质是影响氨氮在沉积物上吸附特征的主要因素。氨氮在轻组有机组分上的吸附以分配作用为主（Koc=85．57）;稳结态和紧结态腐殖质是形成沉积物疏松多孔团聚体结构的重要胶结物质,氨氮在重组有机组分上的吸附除分配作用外,还存在孔隙填充方式的吸附;重组有机组分中的紧结态腐殖质（胡敏素）对氨氮吸附起关键作用（Гmoc,=5857．78mg·kg-1）。轻组有机质、稳结态腐殖质和紧结态腐殖质携载的吸附态氨氮可分别按重组（Гmoc=3477．81mg·kg-1）的0．32、1．21和1．68倍估算。关键词：沉积物;天然有机组分;氨氮;吸附;碳标化吸附分配系数;碳标化饱和吸附量     

香港河流沉积物中有机碳对铜的吸附特性

采用厌氧序列分批滴定装置（ＡＳＢＴ）研究了香港青山湾避风塘和屯门河、城门河、林村河感潮河段沉积物中有机碳对铜的吸附特性。结果表明,在ｐＨ１６和ｐＨ７的条件下,沉积物中有机碳对铜的吸附特性可用Ｌａｎｇｍｕｉｒ等温式描述,铜在不同河流沉积物有机碳中的分配系数差别较大,吸附容量差别较小,Ｈ＾＋可以结合沉积物有机碳的重金属结合位点,导致吸附容量和分配系数随ｐＨ增大而增大。     

芘在不同粒径红树林沉积物团聚体上的吸附/解吸行为

采用海藻酸钙凝胶包覆的方法,研究了芘在九龙江河口红树林区不同粒径沉积物团聚体上的吸附/解吸行为.结果表明,海藻酸钙凝胶包覆可有效减少沉积物团聚体粒径的改变,其等温吸附、吸附/解吸速率情况与未包覆沉积物团聚体存在明显差异.包覆后等温吸附曲线中吸附容量Kf值取决于总有机碳(TOC)的含量,非线性吸附常数n不仅与其硬碳和软碳的比值有关,还与团聚体复杂的孔隙结构存在着一定的关系.包覆后沉积物团聚体的快吸附速率常数值与沉积物团聚体的比表面积值正相关(krap=0.041S-0.0146,R2=0.9923).小粒径沉积物团聚体的"老化"现象较大粒径更为显著,使得其解吸量较小.     

珠江(广州河段)表层沉积物粒度分布特征

沉积物的粒度是控制沉积物中污染物分布的主要因素之一。在珠江(广州河段)表层沉积物粒度组分监测结果的基础上,运用矩法计算公式对各粒度分布参数(平均值、标准差、偏度和尖度)进行了计算,并对沉积物粒度分布特征进行了全面的分析。结果表明:全河段沉积物中砂的平均含量最高,粉砂其次,粘土的含量普遍较低。平均粒径的平均值为0.50 mm,属于砂的粒级范围。在22个断面中,有5个断面的分选系数超过0.5,属于分选中等级别;其余17个断面的分选系数均小于0.5,属于分选好的级别。在22个断面中,出现正偏度和负偏度的断面各占一半。各断面的尖度值在1.00～13.70之间,除1个断面为正态曲线外,其余均为窄峰型。     

沉积物对重质燃料油的吸附研究

在静态条件下,温度为30℃时,研究了沉积物对重质燃料油吸附的影响.结果表明:沉积物对重质燃料油的吸附平衡时间约为24h,平衡吸附量约为919.26μg·g-1;在吸附达到平衡时,沉积物对重质燃料油的吸附总量随沉积物质量的增加而增加,当沉积物质量约为1.5g时,对油的吸附量趋于平衡;沉积物粒径对油吸附量的影响明显,沉积物对油的吸附量为Ⅱ号＜Ⅲ号＜Ⅳ号,小粒度沉积物具有更强的吸附能力.沉积物对油的吸附量随pH值的增加迅速降低,当pH值大约为9.75时达到最低点;沉积物对重质燃料油的吸附符合Freundlich吸附等温方程.     

海泡石黏土矿物对Cu2+的吸附动力学研究

研究分析了海泡石黏土矿物对铜离子的吸附性能和动力学特征,结果表明,海泡石黏土矿物对Cu~(2 )吸附的最佳pH值为6.0左右,随着pH值的增大,吸附作用减弱;在[Cu~(2 )]=100mg·l~(-1),溶液pH值为6,吸附时间为2h时,添加0.1 g海泡石,海泡石对Cu~(2 )的吸附去除率仅为39.5%,当海泡石用量提高至0.4 g时,其对Cu~(2 )的吸附去除率提高到94.8%;实验结果同样显示,18min内有90%的Cu~(2 )被海泡石吸附,随着吸附时间的增加,吸附作用趋于稳定,2h可达到吸附平衡。该吸附过程符合Langmuir和Freundlich等温吸附方程.同时,分别采用拟一级模型和拟二级模型考察了吸附动力学,并计算了这些动力学模型的速率常数.实验数据和拟二级模型计算结果之间有较好的相关性.     

黄泥土微团聚体颗粒组对Cu2+的吸附与解吸研究

采用低能量超声波分散和冷冻机干燥法提取太湖地区黄泥土不同粒径微团聚体颗粒组样品,用平衡液吸附法和CaCl2与HCl溶液的连续解吸法研究原土和不同粒径微团聚体颗粒组对重金属Cu2 的吸附和解吸特征。结果表明,对于Cu2 的吸附,原土用Langmuir方程拟合最佳,而不同粒径微团聚体颗粒组用Freundlich方程拟合最佳。原土和不同粒径微团聚体颗粒组吸附量大小顺序为粘粒级>砂粒级>原土>粉砂级>粗粉砂级,这与其游离氧化铁和有机质含量呈显著正相关。原土和不同粒径微团聚体颗粒组对Cu2 的专性吸附质量分数随吸附量增加而减少,而非专性吸附质量分数则相反。不同粒径微团聚体颗粒组吸附总量小于原土,所以传统风干磨细的研究方法可能高估了土壤对铜固持能力。     

生物炭-锰氧化物复合材料对红壤吸附铜特性的影响

锰氧化物作为改性材料应用于制造复合材料一直是环境领域的研究热点,锰氧化物改性的复合材料在水处理、空气清新剂等领域应用广泛。但目前,将生物炭-锰氧化物复合材料作为吸附材料改变土壤对铜吸持能力的研究还不多见。采用等温平衡吸附法,测定生物炭-锰氧化物复合材料对红壤吸附铜的能力影响,并应用Freundlich方程Cs=KfCen分析红壤对铜的吸附特征。结果表明：不同用量的生物炭-锰氧化物复合材料加入后,均会明显提高红壤对铜的吸附量。添加0.5%、1.0%、2.0%和4.0%生物炭-锰氧化物复合材料的红壤处理,其铜的吸附量较未添加处理分别增加了63.1%、130%,310%和509%。Freundlich吸附方程能较好的描述不同用量生物炭-锰氧化物复合材料影响红壤对铜的吸附特征。添加0.5%、1.0%、2.0%和4.0%炭-锰材料处理的分配系数（Kf值）分别为0.176、0.286、0.653和0.800。生物炭-锰氧化物复合材料用量为4.0%时,分配系数（Kf值）较对照红壤提高了5倍,生物炭-锰氧化物复合材料加入红壤后对红壤pH值影响不大,对CEC（阳离子交换量）有较大的影响;生物炭-锰氧化物复合材料用量为4.0%时,CEC为5.59 cmol·kg-1,较对照增加了14.1%,温度升高,有利于提高红壤对铜的吸附能力。生物炭-锰氧化物复合材料加入红壤后,红壤在1034.63、537.22、471.45 cm-1处有吸收峰出现,红壤表面-OH、Mg-O、Si-O等活性官能团数量明显增加。生物炭-锰氧化物复合材料增加红壤对铜的吸附机制可能是红壤表面Mg-O、Si-O等官能团与铜形成了Mg-O-Cu-、Si-O-Cu-络合物,提高了红壤对铜的吸持能力。从土壤化学与土壤修复的角度出发,生物炭-锰氧化物复合材料可用于铜污染红壤修复。     

腐殖酸对铜的吸附与解吸特征

采用铜离子选择电极研究了铜在腐殖酸两组分(富里酸FA、胡敏酸HA)中的吸附-解吸特征,以及介质pH对这种吸附-解吸的影响。结果表明,腐殖酸对铜的吸附量为FA>HA,吸附强度为HA>FA,解吸量FA-Cu>HA-Cu。腐殖酸两组分对铜的吸附,当介质pH为4.00～7.00时,很好地符合Langmuir等温吸附方程;当pH<4.0时,符合Freundlich方程。FA、HA与铜作用的条件稳定常数与介质pH有关,pH提高则条件稳定常数增大;但在低pH段和高pH段,其增长规律不一致,当4.00相似文献   

几种土壤的基本理化性质与Cu2+吸附的关系

研究了大冶市几种类型土壤的基本性质及与Cu2+吸附的关系,结果表明,土壤对Cu2+的吸附量随其CEC值(记为CEC)而变化,供试土壤的Cu2+吸附量由大到小的顺序为石灰土→水稻土→潮土→棕红壤.加入铜浓度为5 mmol·L-1时11个土壤对铜的吸附量x((mol·g-1)与CEC的直线相关方程为x(Cu2+) = 2.018×CEC + 24.4 (r=0.7066).而影响CEC的因素,如Ph、粘粒含量及其组成、有机质、比表面等,也是决定Cu2+吸附量的重要因素.     

Particle size distribution and pollutants in road-deposited sediments in different areas of Zhenjiang,China

An understanding of road-deposited sediment (RDS) characteristics on an impervious surface is essential to estimate pollutant washoff characteristics and to minimise the impacts of pollutants on the water environment. A total of 62 RDS samples were collected from four different land-use types (commercial, residential, intense traffic and riverside park) in Zhenjiang City, China. The samples were fractionated into seven grain-size classes and analysed for particle size distribution and concentrations of pollutants. The samples are found to consist predominantly of fine particles (60–80%, <250 μm). The maximum mean concentrations of zinc, lead and copper were 686.93, 589.19 and 158.16 mg/kg, respectively, with the highest metal concentrations found in samples from the intense traffic area. The maximum mean contents of organic matter (12.55%), nitrogen (6.31 mg/g) and phosphorus (5.15 mg/g) were found in samples from the commercial area. The concentrations of heavy metals were highest in the smallest particle size fraction analysed (63 μm). The organic matter and nitrogen content generally increased with decreasing particle sizes in the <500-μm particle size range. The results also revealed that most of the total nitrogen (TN) is attached to the finer sediments and that to effectively reduce TN loads in particulates, treatment facilities must be able to remove the finer particles (down to 125 μm for TN).     

Mercury distribution,speciation and potential ecological risk assessment in sediments from Lake Taihu,China

Abstract

Twenty-one surface sediments collected from seven surroundings areas of Lake Taihu in two different years were analyzed for total mercury (THg) concentrations, physicochemical characteristics and speciation using a sequential extraction method to assess spatial distribution, sources, and potential ecological risk. Surface sediments from Lake Taihu contained elevated levels of Hg in two sampling years with THg levels ranging from 77 to 346?ng/g (mean 145?ng/g) in October 2010 and ranging from 122 to 573?ng/g (mean 266?ng/g) in November 2012, respectively. The mean THg concentrations in all studied surface sediments exhibited an increasing trend over time. The oxidizable fraction (F3) and residual fraction (F4) were the predominant Hg species in sediments, while more mobile Hg phases of acid-soluble fraction (F1) and reducible fraction (F2) made up less than 0.5% THg. Significant relationships were found between total organic carbon (TOC) and THg and geochemical speciation indicating an important role for organic matter in affecting distribution, mobility, and bioavailability of Hg in sediments. As evidenced by Hakanson’s potential risk index the total ecological risk of Hg was low in the entire Lake Taihu in 2010 but considered moderate in Zhushan Bay, West Coast, and Meiliang Bay in 2012. These findings provide conservation managers with information needed to more effectively regulate the environment of Lake Taihu.     

The cadmium adsorption capacity of contaminated marine sediments from Hong Kong

The binding capacity of Cd to the sediment particles determines the potential of Cd release from the sediments. An experiment was performed to evaluate the adsorption of Cd by contaminated sediments collected from three different locations in Hong Kong, i.e. Kwun Tong, North Point and Nam Tam Wan, having different degrees of pollution. Langmuir and Freundlich equations were used to evaluate the adsorption of Cd by the sediments. Adsorption isotherms obtained from the Freudlich and Langmuir equations were generally linear and the adsorption of Cd by the sediments was significantly correlated with the adsorption maximum and binding energy constant of the Langmuir equation, and equilibrium partition constant of the Freundlich equation. All sediments had a high Cd adsorption capacity and the highly organic contaminated sediments from Kwun Tong had the highest adsorption capacity of 24,272 mg kg^‐1 at pH8. The adsorption of Cd for all sediments increased with a rise in pH of the equilibrium solution and the total organic carbon content of the sediments. Therefore, a change in the sediment chemical equilibrium is likely to reduce the binding capacity.     

Phosphorus speciation and effects of environmental factors on release of phosphorus from sediments obtained from Taihu Lake,Tien Lake,and East Lake

Phosphorus is considered the primary nutrient limiting eutrophication. The release of phosphorus from sediments not only provides hydrophytes with essential nutrients, but can also produce entrophication in lakes. In this study, the sediment characteristics, phosphorus speciation, and environmental factors affecting phosphorus release from sediments from Taihu Lake, Tien Lake, and East Lake were investigated. The results indicated that phosphorus levels of sediments ranged from 647 ± 67 to 2343 ± 122 mg/kg. Inorganic phosphorus comprised the majority of total phosphorus. The main phosphorus speciation of sediments obtained from Taihu Lake and Tien Lake was Residual-P, and the main phosphorus speciation of sediment obtained from East Lake was NaOH-P. Phosphorus release occurred in acidic and alkaline conditions but more frequently under alkaline conditions. The amount of phosphorus released from the sediments increased as the disturbing intensity rose. In addition, less phosphorus was released in natural than anaerobic conditions. The amount of phosphorus released was elevated as temperature increased.