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261.
巢湖水体散射和后向散射特性研究   总被引:1,自引:3,他引:1  
湖泊水体散射特性的研究对湖泊水色要素遥感反演模型的发展具有重要的意义.本研究利用AC-S和ECO-BB9实测了巢湖水体的散射系数和后向散射系数,在分析光谱变化特性的基础上,构建了悬浮颗粒物散射系数和后向散射系数的幂函数光谱模型,获得的光谱指数分别为0.86和3.24.研究发现悬浮颗粒物散射系数与TSM和ISM都存在较好的线性函数关系,进而提出水体中总悬浮颗粒物的比散射系数为0.6364(10-3m2·mg-1),无机悬浮颗粒物的比散射系数为0.9108(10-3m2·mg-1).同时,分析了悬浮颗粒物后向散射率和折射指数的变化,其变化范围分别为0.003~0.026和1.02~1.06.  相似文献   
262.
外源铅在4种土壤中的老化特征及对土壤化学性质的影响   总被引:1,自引:0,他引:1  
采用化学提取和梯度薄膜扩散技术(DGT)探究外源铅(Pb)在不同类型土壤中老化的形态变化规律,考察了外源Pb添加对土壤pH、阳离子交换量(CEC)和可溶性有机质(DOC)等的影响,初步建立了土壤Pb生物有效性的预测模型.结果表明:EDTA提取态Pb含量随老化时间的延长而降低;准二级动力学方程可较好地表达有效态Pb在老化过程中的动力学特征,方程的参数反映了Pb处理浓度的增加延长了老化达平衡的时间,所有供试土壤的EDTA提取态Pb含量在3个月后基本达到老化平衡;不同提取态Pb含量和变化不同,CaCl_2提取态Pb含量最少、变化最大,HNO_3提取态Pb含量变化最小;外源Pb添加会降低土壤pH,但对CEC和DOC无明显影响;随着老化时间的延长,土壤pH升高,CEC无明显变化,DOC显著降低;土壤水溶态Pb和DOC可用来预测DGT测定的有效态Pb含量,预测效果较好.  相似文献   
263.
通过试验方法考察了2种不同底泥改良剂(铝和锆改性沸石)对太湖底泥-水系统中SRP(可溶解性磷酸盐)的固定作用. 改性沸石改良前后太湖底泥对水中较高浓度磷的吸附平衡数据可用Langmuir和Freundlich等温吸附方程进行描述,吸附动力学过程可用准二级动力学模型进行描述. 太湖底泥、铝和锆改性沸石改良太湖底泥的最大磷吸附量分别为395、613和1 009 mg/kg. 被改良太湖底泥中,铝改性沸石所吸附的磷主要以NaOH-rP(NaOH提取态磷)形态存在,锆改性沸石所吸附的磷主要以NaOH-rP和Res-P(残渣态磷)形态存在. 当水中初始ρ(SRP)很低时,太湖底泥和改性沸石改良太湖底泥均释放出磷,其中后者的释磷量较低. 改性沸石改良太湖底泥中的w(BAP)(BAP为生物有效磷)低于太湖底泥,w(liable-P)(liable-P为弱吸附态磷)也明显偏低. 铝改性沸石改良太湖底泥中的w(BD-P)(BD-P为氧化还原敏感态磷)与太湖底泥相比差异不显著,而锆改性沸石改良太湖底泥中的w(BD-P)明显低于太湖底泥. 可见,铝和锆改性沸石均可用于控制太湖底泥磷的释放,其中锆改性沸石的控制效果更好.   相似文献   
264.
阿特拉津在土壤中的降解途径及其对持留性的影响   总被引:16,自引:0,他引:16  
通过田间和实验室试验,研究了除草剂阿特拉津在土壤中的降解代谢规律及其与土壤特性的关系。试验表明,阿特拉津施用后、在作物生长期内可降解90%以上,土壤酸碱度对阿特拉津在土壤中的代谢有显著影响。在碱性土壤中阿特拉津主要经过微生物代谢而被降解;在酸性土壤中化学水解占优势地位。阿特拉津在强酸性土壤中的持留性(半衰期为63d)低于弱酸性土壤中的持留性(半衰期为84d),而在碱性土壤中由于较强的微生物降解作用,其持留性(半衰期为51d)最低。  相似文献   
265.
• Simultaneous removal of organic contaminants and Pb(II) was achieved by Mn(VII). • Pb(II) enhanced Mn(VII) oxidation performance over a wide pH range. • Pb(II) did not alter the pH-rate profile for contaminants oxidation by Mn(VII). • Mn(VII) alone cannot oxidize Pb(II) effectively at pH below 5.0. • Pb(III) plays important roles on enhancing Mn(VII) decontamination process. The permanganate (Mn(VII)) oxidation has emerged as a promising technology for the remediation and treatment of the groundwater and surface water contaminated with the organic compounds. Nonetheless, only a few studies have been conducted to explore the role of the heavy metals (especially the redox-active ones) during the Mn(VII) oxidation process. In this study, taking Pb(II) as an example, its influence on the Mn(VII) decontamination performance has been extensively investigated. It was found that, with the presence of Pb(II), Mn(VII) could degrade diclofenac (DCF), 2,4-dichlorophenol, and aniline more effectively than without. For instance, over a wide pH range of 4.5–8.0, the dosing of 10 μmol/L Pb(II) accelerated the DCF removal rate from 0.006–0.25 min−1 to 0.05–0.46 min−1 with a promotion factor of 1.9–9.4. Although the UV-vis spectroscopic and high resolution transmission electron microscopy analyses suggested that Mn(VII) could react with Pb(II) to produce Mn(IV) and Pb(IV) at pH 6.0–8.0, further experiments revealed that Pb(II) did not exert its enhancing effect through promoting the generation of MnO2, as the reactivity of MnO2 was poor under the employed pH range. At pH below 5.0, it was interesting to find that, a negligible amount of MnO2 was formed in the Mn(VII)/Pb(II) system in the absence of contaminants, while once MnO2 was generated in the presence of contaminants, it could catalyze the Pb(II) oxidation to Pb(IV) by Mn(VII). Collectively, by highlighting the conversion process of Pb(II) to Pb(IV) by either Mn(VII) or MnO2, the reactive Pb(III) intermediates were proposed to account for the Pb(II) enhancement effect.  相似文献   
266.
The pollution levels of typical semivolatile organic compounds (SVOCs) consisting of 15 polycyclic aromatic hydrocarbons (PAHs), 20 organic chlorinated pesticides (OCPs), and 15 phthalate esters (PAEs) were investigated in small rivers running through the flourishing cities in Pearl River Delta region, China. The concentrations of ∑15PAHs were 2.0–48 ng/L and 29–1.2?×?103 ng/g in the water and sediment samples, respectively. The ∑20OCPs were 6.6–57 ng/L and 9.3–6.0?×?102 ng/g in the water and sediment samples, respectively. The concentrations of ∑15PAEs were much higher both in the water and sediments. The partition process of the detected SVOCs between the water and sediment did not reach the equilibrium state at most of the sites when sampling. The combustion of petroleum products and coal was the major source of the detected PAHs. The OCPs were mainly historical residue, whereas the new inputs of dichlorodiphenyltrichloroethane (DDT), chlordane, and endosulfan were possible at several sites. The industrial and domestic sewage were the major source for the PAEs; storm water runoff accelerated the input of PAEs. No chronic risk of the SVOCs was identified by a health risk assessment through daily water consumption, except for the ∑20OCPs that might cause cancer at several sites. Nevertheless, the integrated health risk of the SVOCs should not be neglected and need intensive investigations.  相似文献   
267.
Qiao XL  Luo YM  Christie P  Wong MH 《Chemosphere》2003,50(6):823-829
An incubation experiment was conducted to study the chemical speciation and extractability of three heavy metals in two contrasting biosolids-amended clay soils. One was a paddy soil of pH 7.8 and the other was a red soil of pH 4.7 collected from a fallow field. Anaerobically digested biosolids were mixed with each of the two soils at three rates: 20, 40 and 60 g kg(-1) soil (DM basis), and unamended controls were also prepared. The biosolids-amended and control soils were incubated at 70% of water holding capacity at 25 degrees C for 50 days. Separate subsamples were extracted with three single extractants and a three-step sequential extraction procedure representing acetic acid (HOAc)-soluble, reducible and oxidisable fractions to investigate the extractability and speciation of the heavy metals. As would be expected, there were good relationships between biosolids application rate and metal concentrations in the biosolids-amended soils. The three heavy metals had different extractabilities and chemical speciation in the two biosolids-amended soils. Ethylene diamine tetraacetic acid extracted more Cu, Zn and Cd than did the other two single extractants. The oxidisable fraction was the major fraction for Cu in both biosolids-amended soils and the HOAc-soluble and reducible fractions accounted for most of the Zn. In contrast, Cd was present mainly in the reducible fraction. The results are discussed in relation to the mobility and bioavailability of the metals in polluted soils.  相似文献   
268.
根据2009年6月巢湖32个样点的实测数据,分析巢湖水体各组分的吸收、后向散射特性以及水体漫衰减系数光谱特征,并通过Lee模型计算各影响因子对漫衰减系数的贡献率,在此基础上,进一步探讨巢湖水体漫衰减系数与各衰减因子浓度的关系.结果表明,非色素颗粒物、有色可溶性有机物(CDOM)吸收均随着波段增加呈现不断衰减趋势,400...  相似文献   
269.
基于2019年五指山背景点、海口市和三亚市的环境空气自动监测数据和气象观测资料,分析了海南省背景区域和重点城市O3及其前体物NO2污染特征;结合挥发性有机物(VOCs)在线监测数据,分析了五指山背景点VOCs的时间变化规律、O3浓度高值月份O3及其前体物VOCs和NOx的污染特征以及VOCs的臭氧生成潜势(OFP).结果表明,O3是影响五指山背景点空气质量的关键污染物,五指山背景点O3日最大8 h浓度平均值与海口市和三亚市显著相关.背景点NO2月均浓度水平显著低于城市点,然而背景点和城市点O3月均浓度水平和变化趋势高度一致.背景点O3变化与风向密切相关,春夏季偏南风频率较高,O3浓度相对较低;秋冬季以东北风为主,易受内陆污染输送影响,O3浓度较高.五指山背景点春夏季VOCs体积分数低于秋冬季,但对应的OFP高于秋冬季;其中异戊二烯夏季体积分数显著高于秋冬季,且其夏季体积分数占总挥发性有机物的比例最高,对应的OFP贡献率可达70%以上,O3则表现出秋冬季显著高于夏季的特征.11月O3高浓度时段乙炔和芳香烃的体积分数较清洁日出现较大上升,同时其对应的OFP显著上升.VOCs优势物种和OFP主要贡献物种的分析结果表明,O3高浓度时段机动车尾气和油气挥发排放源对五指山背景点VOCs的化学组成和OFP有重要贡献.  相似文献   
270.
取同质钼矿区土壤放于通风处自然风干,平行A、B两组盆栽实验。A组直接投放不同浓度的磷酸二氢钾-磷酸氢二钠缓冲溶液50 ml,B组做对照,种植白菜,待白菜生长50 d后再投加一次缓冲溶液50 ml,60 d后收割其地上部分及对应土壤进行消解。采用ICP-AES分析土壤及植物体中各种重金属元素的含量,研究了在磷酸二氢钾-磷酸氢二钠缓冲溶液在其不同浓度梯度下投加,白菜地上部分对钼矿区重金属污染土壤的修复潜力。结果表明:在投加磷酸二氢钾-磷酸氢二钠缓冲溶液的条件下均能显著提高白菜的地上部分富集土壤中重金属元素的能力(Cd除外),但缓冲溶液对白菜积累重金属能力的促进作用也存在重金属元素种类及浓度梯度之间的差异;投加pH=7.3磷酸二氢钾-磷酸氢二钠缓冲溶液可以较好地去除钼矿区污染土壤中的Cr、Mo、Ni、Pb;投加pH=7.7磷酸二氢钾-磷酸氢二钠缓冲溶液可以较好地去除钼矿区污染土壤中的As、Cu、Hg、Zn。  相似文献   
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