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1.
溶液pH对自然水体中多种固相介质吸附铅、镉、铜影响的比较 总被引：1，自引：0，他引：1
采用实验室内模拟吸附方法,研究不同溶液pH下沉积物、悬浮颗粒物和生物膜吸附重金属的热力学特征。结果表明：在不同pH下,Langmuir方程均可以很好地描述自然水体三种固相介质吸附重金属的热力学过程。在相同pH条件下,三种固相介质对重金属的吸附能力从大到小依次为悬浮颗粒物、生物膜、沉积物,它们对重金属的吸附能力为铅>铜>镉;这三种固相介质对重金属的吸附能力都随着pH值的升高而增大,其中悬浮颗粒物对重金属的吸附能力受溶液pH影响最大;另外,相对于铜和镉,三种固相介质对铅的吸附受溶液pH影响较大。 相似文献
2.
湿地水环境中表层沉积物吸附铅、镉能力的研究 总被引：6，自引：2，他引：6
在选定的实验条件下,对向海自然保护区5个不同类型湿地水体的表层沉积物样品进行了铅、镉的热力学吸附实验.结果表明,沉积物样品吸附铅、镉的过程符合Langmuir和Freundlich(n=8,p= 0.01) 等温吸附曲线.在所讨论的范围内,沉积物样品吸附铅、镉的能力与样品中铁、锰氧化物及有机质含量存在着显著的相关性.表层沉积物吸附铅、镉的能力小于生物膜吸附铅、镉的能力,即在湿地水环境中,生物膜对重金属迁移转化的作用相对于表层沉积物而言更重要. 相似文献
3.
共存镉/铜对沉积物(生物膜)中主要组分吸附阿特拉津的影响 总被引：1，自引：0，他引：1
采用选择性萃取分离技术对沉积物(生物膜)中非残渣态组分(铁、锰氧化物和有机质)进行分离,研究阿特拉津(atrazine,AT)-Cd-Cu系中共存重金属对选择性萃取前后沉积物(生物膜)吸附AT的影响.研究结果表明:共存体系中,沉积物(生物膜)中铁氧化物对AT的吸附贡献最大,其次是有机质,而锰氧化物则抑制AT的吸附;共存镉促进了AT在沉积物(生物膜)原样及各非残渣态组分上的吸附,镉质量浓度为0.2 mg/L时,促进作用最显著,各组分对阿特拉津的吸附贡献增加了3.20%～32.31%(沉积物)和1.61%～17.10%(生物膜),但随镉质量浓度的增加,其促进作用减弱;共存铜抑制沉积物(生物膜)原样及铁氧化物、有机质对AT的吸附,铜质量浓度为75.0 mg/L时,其抑制作用最强,铁氧化物和有机质对阿特拉津的吸附贡献分别降低了29.21%、22.36%(沉积物)和9.46%、77.27%(生物膜),但同时减弱了锰氧化物对AT吸附的抑制作用,其吸附贡献分别提高了28.98%(沉积物)和17.46%(生物膜). 相似文献
4.
影响向海湿地草根层土壤吸附铅、镉能力的因素 总被引：9，自引：7，他引：2
利用向海湿地采集的草根层土壤进行吸附铅、镉的热力学实验,结果表明草根层土壤吸附铅、镉的过程符合Langmuir和Freundlich等温吸附曲线(n=8,p=0.01).吸附铅、镉存在干扰吸附现象,吸附铅的能力约是吸附镉的能力的3倍.而且草根层土壤吸附铅、镉的最大吸附量与土壤中的有机质和铁、锰氧化物含量存在着正相关性.土壤的理化性质是影响土壤吸附铅、镉能力的内在主要因素;pH等是影响草根层土壤吸附铅、镉能力的外部主要因素. 相似文献
5.
传统的固相萃取填料应用于环境样品的重金属处理过程中,存在pH不稳定和不同极性萃取物共同萃取较为困难等方面的不足,因此寻找新型固相萃取填料显得尤为重要。本文采用多壁碳纳米管填充固相萃取柱,萃取水中金属元素铅、镉、铜和铁,采用石墨炉原子吸收光谱法测定铅和镉,电感耦合等离子体发射光谱法测定铜和铁。实验考察了多壁碳纳米管的性质、溶液pH值、洗脱溶液、样品流速以及基体效应对测定结果的影响。结果显示:溶液pH=9,1 mol/L硝酸为洗脱溶液,样品流速为2 mL/min时,外径8 nm未修饰的多壁碳纳米管有较好的萃取效率,对溶液中铅、镉、铜和铁的最大吸附容量分别为44.91、42.31、54.68和49.07 mg/g,四种元素的吸附容量均衡;钾、钠、钙、镁离子以及苯和甲苯等基质对四种金属元素的萃取影响不大。方法回收率为95.3%~99.5%,精密度(RSD,n=7)为1.2%~3.2%。本方法采用外径8 nm的多壁碳纳米管固相萃取,与传统萃取方法相比,富集效果好、回收率较高,而且操作简便、准确度高;与前人采用外径20~30 nm的多壁碳纳米管的性能相比,镉和铜的吸附容量更高,还可实现对铁的吸附,且铅、镉、铜和铁四种元素的吸附容量均衡,更适合用于检测水样中的金属元素。 相似文献
6.
为揭示农药（晶体乐果、甲霜灵、阿特拉津、马拉硫磷、扑草净）与重金属（铜、锌、铅、镉、镍）10种污染物共存时的复合污染规律,以阿特拉津为目标污染物,采用分辨度为Ⅲ的210-6分式析因实验设计,并用完全折叠实验和区组设计进行辅助,通过多元线性回归的建模方法筛选并建立了以阿特拉津为因变量、10种污染物因子主效应和二阶交互效应为自变量的多元线性回归吸附模型。研究表明：共存体系中因子主效应项铅、铜、锌、镉、镍和农药晶体乐果显著抑制（显著性水平α=0.05）阿特拉津在沉积物上的吸附,与阿特拉津产生竞争吸附效应,因重金属主效应产生的拮抗作用占总拮抗作用的63.5%,其拮抗作用从大到小为镍、镉、晶体乐果、锌、铅、铜;在以镍为关键自变量的二阶交互效应项中,因二阶交互效应项产生的协同或拮抗作用占阿特拉津吸附能力的35.3%,其中,铅、镉和晶体乐果抑制镍与阿特拉津的竞争吸附,与阿特拉津在沉积物上的吸附发生协同作用,协同作用从大到小为镉×镍、铅×镍、镍×晶体乐果;而镍作为调节自变量的二阶交互效应项镍阿特拉津会促进阿特拉津的吸附,说明多种污染物共存体系中重金属镍对阿特拉津在沉积物上吸附影响作用的复杂性和重要性。 相似文献
7.
为揭示冲积与湖积成因土壤镉的吸附特征,以安徽省当涂县冲积成因的江心洲和冲积、湖积成因的大陇乡根际土壤为研究对象,开展土壤镉的等温吸附实验和吸附动力学实验.等温吸附实验结果表明,冲积土壤镉的吸附量（S）、等温吸附常数（K）和固液分配系数（Kd）均较湖积土壤明显偏大,显示冲积土壤对镉的吸附能力较湖积土壤强;吸附动力学实验表明,冲积土壤的最大吸附量、平衡吸附量均较湖积土壤大,吸附速率也明显偏大,尤其在吸附实验早期更为显著;等温吸附常数K和平衡吸附速率Vb与土壤理化性质的分析表明,土壤pH是造成研究区土壤镉吸附能力差异的主要原因,其次为物理性粘粒含量;土壤pH是影响研究区冲积土壤镉吸附能力的主要因素;湖积土壤镉的吸附能力受土壤pH、有机质含量、Cd含量、物理性粘粒含量等因素的综合影响.研究对于揭示Cd在水土系统的迁移转化规律以及土壤Cd的污染防治具有重要的指导意义. 相似文献
8.
不同粒级土壤中镉铅汞的吸附特性 总被引：2，自引：0，他引：2
将3种不同质地的土壤样品分为3种不同的粒级:自然状态、砂粒和粉黏粒,分别研究了这3种不同土壤在3种不同粒级时对镉、铅、汞的吸附特点。结果表明,镉、铅在粉黏粒土壤中的吸附大于在自然土壤和砂粒土壤中的吸附,而汞却表现出相反的结果,其在砂粒土壤中的吸附远远大于在粉黏粒土壤和自然土壤中的吸附。3种不同质地的土壤对镉、铅、汞的吸附与分粒级土壤的吸附表现出了相似的吸附特性。同时,镉在3种不同土壤不同粒级中的吸附符合Langmuir方程,铅在3种不同土壤不同粒级中的吸附符合Henry方程,而汞在3种不同土壤不同粒级中的吸附符合Freundlich方程。 相似文献
9.
南黄海表层沉积物的碎屑矿物、地球化学特征及物源分析 总被引：1，自引：0，他引：1
以南黄海中、西部表层沉积物的测试数据为基础,分析了表层沉积物的碎屑矿物组合特征、分布规律和能灵敏指示物源的CaCO3、TiO2、Cu、Sr和Ba的含量特征、分布规律,将这些特征分别与黄河和长江沉积物、黄土进行对比,探讨了南黄海中、西部的物质来源。南黄海西北部主要来源于现代黄河物质和山东半岛及邻近海域的侵蚀基岩;苏北黄河三角洲沉积物主要来源于全新世海侵期海水对古黄河沉积物的改造,其次为海水对基岩的侵蚀,现代黄河物质的影响较小;中部表现出多源性,沉积物部分来源于海侵期海水对海底基岩的侵蚀、改造、再沉积,部分来源于长江物质、黑潮物质及古黄河物质,长江物质影响大于古黄河物质;南部主要来源于长江物质。研究结果表明,现代黄河物质影响的范围小于长江物质;古黄河曾于晚更新世在苏北入海。 相似文献
10.
中太平洋CC区表层沉积物的地球化学 总被引：1，自引：0，他引：1
根据对中太平洋CC区表层沉积物常量、微量元素的测试结果,采用多元统计分析的方法,研究了该地区表层沉积物中元素含量的空间分布和组合特征,探讨了其物质来源及沉积环境的横向演变规律.元素的相关性分析和R型因子分析表明,SiO2、Al2O3、Fe2O3、MgO、K2O、Na2O等常量元素氧化物之间存在明显的正相关关系,说明这些元素氧化物内在关系较为密切,在沉积物中所起的作用相近,元素的地球化学行为相似,尤其在成因方面专属性较强,主要受陆源碎屑沉积及火山活动的影响.它们与CaO、CaCO3、Sr为明显的负相关关系,说明二者内在关系比较疏远,相关性差,沉积物源不同,后者主要与生物作用有关.由SiO2、Fe2O3、TiO2与Al2O3的比值与Ba/Sr标准值对比显见,中太平洋CC区表层沉积物主要来源于深海黏土、生物源和火山热液活动的产物.沉积相主要为硅质软泥相、硅质黏土相、钙质软泥相、沸石黏土相. 相似文献
11.
Comparison of trace metal adsorption onto different solid materials and their chemical components in a natural aquatic environment 总被引：1，自引：0，他引：1
Solid materials such as suspended particulate matter (SPM), deposited sediment (DS) and natural surface coatings (NSC, composed of biofilms and associated minerals) are important sinks and potential sources of pollutants in natural aquatic environments. Although these materials can exist in the same water body, few studies have been conducted to compare their ability to adsorb trace metals. In this study, the adsorption of Pb, Cu and Cd by these solids, collected from an urban lake, was investigated. In addition, the metal adsorption properties of the main components of these solids, namely Mn and Fe oxides and organics, were also investigated using the method of selective extraction followed by metal adsorption. The solids that co-existed in water showed similarities and differences in their compositions. For each metal, adsorption to the solids occurred in the same order: NSC > SPM > DS. For Pb and Cd, Fe and Mn oxides and organics contributed to the adsorption by NSC and SPM, and the adsorption by DS was dominated by Fe oxides. For Cu, the organics were the main adsorptive phase. The specific adsorption capability of these components decreases in the following order: Mn oxides > Fe oxides > organics. Overall, the results presented herein indicate that different solids and their components played important roles in the adsorption of trace metals. 相似文献
12.
Competitive adsorption,release and speciation of heavy metals in the Yellow River sediments,China 总被引：2，自引：0，他引：2
Qingyun Fan Jiang He Hongxi Xue Changwei LÜ Ying Liang Saruli Ying Sun Lili Shen 《Environmental Geology》2007,53(2):239-251
The competitive adsorption and the release of selected heavy metals and their speciation distribution before and after adsorption
in the Yellow River sediments are discussed. The adsorption of metals onto sediments increases with increasing pH value and
decreases with increasing ionic strength. The competitive coefficient K
c and the distribution coefficient K
d are obtained to analyze the competitive abilities of selected heavy metals, which are ranked as Pb > Cu >> Zn > Cd. The competition
among selected heavy metals becomes more impetuous with increasing ion concentration in water. Speciation analysis was done
by an improved analytical procedure involving five steps of sequential extraction. Cu, Pb and Zn were mainly transformed into
the carbonate-bound form (50.8–87.7%) in adsorption. Most of (60.7–77.3%) Cd was transformed into the exchangeable form, and
the percentage of carbonate-bound Cd was 19.7–30.4%. The release reaction was so quick that the release capacity of selected
heavy metals from sediments to aqueous solution reached half of the maximum value only in 30 s. As opposed to adsorption,
the release capacities of selected heavy metals were ranked as Cd > Zn >> Cu > Pb. In this study, Cd produces the most severe
environmental hazards, because its concentration in the release solution is 85.8 times more than the human health criteria
of US EPA. 相似文献
13.
The presence of heavy metal concentrations was examined in natural sediments from four sites along the Jajrood river in northeast
of Tehran, the capital of Iran. Besides determination of elemental concentrations (Pb, Cu, Zn, Cd, Ni and Cr), X-ray fluorescence
and X-ray diffraction tests were carried out to determine other chemical components in these adsorbents. Also the ability
of sediments to adsorb these heavy metal ions from aqueous solutions was investigated. Results show that the extent of adsorption
increases with increase in adsorbent concentration. The amount of adsorbed Pb, Cu and Zn in sediments was much greater than
that of the other metals, and Cr was adsorbed much less than others. The adsorbabilities of sediments to heavy metals increased
in the order of Pb > Cu > Zn > Cd > Ni > Cr. Based on the adsorption data, equilibrium isotherms were determined at selected
areas to characterize the adsorption process. The adsorption data followed Freundlich and Langmuir isotherms in most cases.
Correlation and cluster analysis was performed on heavy metals adsorption and sediment components at each site to evaluate
main adsorbing compounds in sediments for each metal. Results demonstrated that heavy metals sorption is mostly related to
load of organic matter in the Jajrood river sediments. 相似文献
14.
The island city of Bombay is surrounded by Thane creek in the east and Ulhas river on the north. These two aquatic regimes act as receptacles of industrial waste and sewage discharges from the city and also lithogenic fluxes from the adjacent basaltic terrain.
Two consecutive sets of pre-monsoon and post-monsoon samples of water, suspended solids and sediments were collected from the intertidal zone of Thane Creek and along the Ulhas River. These were analysed for toxic heavy metals such as Fe. Mn, Ni, Co, Pb, Zn, Cu, Cr, Hg and Cd and the degree of metal contamination was determined. Using this data the pattern and mechanism of distribution of heavy metals in water, suspended solids and sediments were investigated. These are closely related to discharges of industrial effluents and domestic sewage and largely controlled by basic geochemical processes. 相似文献
15.
水稻土中重金属元素Cd、Pb的竞争吸附
——以长株潭地区水稻土为例 总被引：3，自引：0，他引：3
对中国南方的3个水稻土样品进行了Cd、Pb单一离子和混合离子吸附特点的研究。结果表明,3个水稻土样品中Cd、Pb的吸附特点都相似,Langmuir等温方程可很好地描述Cd、Pb的吸附等温线。3个土壤样品中,有较高pH值和较低有机物、CEC浓度、粘土含量、高岭石含量的2个土壤样品对Cd、Pb有较大的吸附量,且其等温吸附拟合的最大吸附量(B)也较大。在两组分混合溶液中,尽管共存离子的存在影响了土壤对单一离子的吸附,同时土壤对Cd的吸附在一定程度上受影响的程度大,但3个土壤样品都表现出对Pb有强的吸附能力。在3个土壤样品中,Langmuir等温方程中Pb的健合能常数(K)都大于Cd的健合能常数(K),混合溶液中的K值高于单一溶液的K值,表明2种金属离子对吸附位点的竞争提高了特定吸附位点的保持力,使金属离子在土壤中特定位点的吸附更加坚固。 相似文献
16.
Samples of stream sediments were collected along two streams adjacent to a sanitary landfill. One of the streams drained the landfill directly. In addition, control of background samples were also analyzed from a stream not affected by the landfill. All samples were analyzed for Ag, Zn, Cu, Cd, and Pb content using atomic adsorption techniques. The pH of the three streams were monitored since pH differences in the streams may affect the quantities of metals adsorbed or precipitated on the sediments. The comparison between the content of Ag, Zn, and Cu in the sediments of the two study streams and the same metals in the control sediments indicated the landfill emitted these metals into the two adjacent streams. However, since the Cd and Pb contents in the sediments of both streams were similar to that of the control stream sediments, these metals may not be emitted into the two study streams from the landfill and they represent only background quantities. The comparisons of each metal in the sediments of each stream were made by the use of a metal trend chart, the individual calculated mean metal content values, and by the statistical two sample t-test. No decreasing trends of the quantities of Ag, Zn, or Cu as a function of increasing distance from the landfill was present in the sediments along the stream that drained the landfill directly. These sediments might have been affected by stream action and became mixed with other sediments downstream. 相似文献
17.
采用固定化技术将吸附重金属能力较强的优势细菌固定,然后将其对Cd2+进行吸附规律研究。结果表明：固定化细菌对Cd2+吸附是动态过程,120 min达到吸附平衡;随着重金属Cd2+浓度的增加,固定化细菌对其吸附量呈线性增加,而随着离子强度的增加,固定化细菌对其吸附量呈线性降低;当吸附体系pH=6时吸附量最大;环境温度对固定化细菌吸附影响不显著;共存Pb2+降低了固定化细菌对Cd2+的吸附量。 相似文献