温泉宾馆室内PM_(10),PM_(2.5),CO_2和~(222)Rn的研究

对广东省 4座温泉宾馆室内外氡(222Rn)浓度和温泉水氡浓度进行研究,同时利用便携式探测器对室内外 PM10,PM2.5,CO2和CO 等污染物暴露水平进行直接测定.结果表明,温泉宾馆室内使用温泉水时氡浓度明显高于广东省室内平均氡浓度.除 CO 外,室内 PM10,PM2.5 和CO2 浓度都较高,其中 PM10 和 CO2 的超标率分别达到 67%和 89%.说明温泉宾馆室内不仅存在一般性污染物,而且存在高浓度的 Rn. 222     

感光胶片废水的水解酸化—好氧处理工艺试验

对感光胶片有机生产废水处理工艺进行了方法采用水解酸化－好氧串联工艺和传统活性污泥法两种方法并进行对照。结果经水解酸化处理，废水的ＢＯＤ５／ＣＯＤｃｒ可提高至０．５４－０．５６，平均增加了１７％左右，证实了水解酸化菌在该工艺条件下具有搞高效片废水可生化性的功能。     

海洋中有毒有机污染物的监测方法研究进展

以海洋中有毒有机污染物监测方法的发展为主线,系统介绍了这些方法的前处理和分析手段,简要概述了各监测方法的优缺点。发现了目前已有的监测方法大都仅停留在对各单一目标有机污染物进行化学监测的阶段,指出了需要发展不仅能获得有效的化学监测信息,而且能直接反映多种混合有机污染物对海洋生物的总生物有效性的新的监测方法,以推动我国海洋污染监测的进一步发展,为维护海洋生态系统的健康发展提供可靠的科学方法和理论依据。     

UV/TiO_2/H_2O_2法对高浓度有机废水降解的应用研究

用UV TiO2 H2 O2 法对高浓度有机废水降解的实验表明 ,当TiO2 、H2 O2 的投加量分别为 2 0g与 1% ,反应时间为3h时 ,CODCr、Oil、Ar OH、NH3 N、S2 - 的平均去除率分别达到 73 %、83 %、86%、5 0 %、10 0 %。此处理工艺具有除臭、除色、快速高效、不产生污泥等优势。实验过程探索了TiO2 、H2 O2 的用量对各污染物降解率的影响 ,并设计了有实用意义的反应器     

Dynamic fate modeling of γ-hexachlorocyclohexane in the lower reaches of the Liao River

A QWASI model dependent on temperature is parameterized to describe the long-term fate of persistent organic pollutants (POPs) in the Liao River. The model parameters, namely fugacity capacity, degradation rate, and transfer coefficient, are profoundly affected by temperature. This model is used to simulate the fate of γ-hexachlorocyclohexane (γ-HCH) in the lower reaches of the Liao River from 1998 to 2008. Modeling results show that γ-HCH fugacity capacities in air, water, and sediment increase as temperature decreases, and the transfer and transformation rate coefficients increase as temperature increases. The variations of transfer and transformation parameter D values depend on fugacity capacities, and transfer and transformation coefficients simultaneously. The performance of the model is evaluated by comparing the predicted and observed concentrations in the water and sediment of the Liao River. The predicted values agree well with the observed value in the order of magnitude, in most cases within the factor of 3. It is believed that the model is appropriate for simulating the long term fate of POPs in the Liao River. Translated from Environmental Science, 2006, 27(1): 121–125 [译自: 环境科学]     

生物滴滤器去除挥发性有机物的影响因素

生物滴滤器用于处理挥发性有机物,有机物的去除效率受到许多因素的影响。总结和讨论了填料、营养液、进气等诸多因素对生物滴滤器性能的影响。这些讨论结果有助于在生物滴滤器实际应用中选择合适的设计和操作条件,从而达到更佳的处理效果。     

重庆主城区大气总悬浮颗粒中有机碳和元素碳污染特征分析

在四个季节采样分析的基础上，本文报道了重庆市主城区江北区(商住区)和缙云山(清洁对照点)两个监测点总悬浮颗粒物质量浓度的空间分布和季节变化特征，同时利用热分解示差热导法元素分析仪测定了TSP中的OC和EC浓度，探讨了OC和EC含量并与北京相应功能区的TSP质量浓度及其OC和EC浓度进行了比较。结果表明：重庆市商住区和对照点TSP年均质量浓度均小于北京市商住区和对照点；重庆市商住区OC和EC年均质量浓度高于北京市商住区，北京市对照点OC和EC年均质量浓度高于重庆市对照点。两个城市的四个监测点OC／EC年均值均大于2．0，说明两城市城区二次污染比较严重。     

臭氧—活性炭组合工艺对饮用水中AOC的去除

研究了以O3/GAC为主的饮用水深度处理工艺对AOC去除效果 ,结果表明 :原水 (某江水 )AOC浓度为 6 1 9μg乙酸碳 /L ;生物陶粒滤池对AOC的去除率为 54% ;O3 +GAC对AOC的去除率为 83.8% ;加氯消毒后AOC浓度增加 1 .38倍 ;常规水处理工艺对AOC的去除率为 4 3.7% ,不能保证饮用水的生物稳定性     

Phytoremediation and its models for organic contaminated soils

Soil pollution has been attracting considerable public attentions over the last decades.Sorts of traditional physiochemical methods have been used to remove th organic pollutants from soils.However,the enormous costs and low efficiencies associated with these remediation technologies limit their availabilities.Phytoremediation is an emerging technology that uses plants to cleanup pollutants in soils.As overwhelmingly positive results have been shown,phytoremediation is a most economical and effective remediation technique for organic contaminated soils.In this paper phytoremediation and its models for organic contaminated soils are viewed.The mechanisms of phytoremediation mainly include the direct plant uptake of organic pollutants,degradation by plant-derived degradative enzymes,and stimulated biodegradation in plat rhizosphere.Phytoremediation efficiency is close related to physicochemical properties of organic pollutants, environmental characteristics,and plant types.It is no doubt that soil amendments such as surfactants improve the solubilities and availabilities of organic pollutants in soils.However,little information is available about effects of soil amendments on phytoremediation efficiencies.Phytoremediation models have been developed to imulate and predict the environmental behavior of organic pollutants,and progress of models is illustrated.In many ways phytoremediation is still in its initial stage,and recommendations for the future for the future research on phytoremediation are presented.     

Effect of low-molecular weight organic acids on phosphorus release and phytoavailabilty of phosphorus in phosphate rocks added to soils

Phosphorus (P) is critically needed to improve soil fertility in many parts of the world. The use of water-soluble P fertilizers, e.g., single super-phosphate and triple super-phosphate in developing countries to improve crop production has been limited primarily by their high cost. The presence of indigenous phosphate deposits in some countries provides an incentive for direct application or local chemical treatment at low cost to improve the solubility of low reactive phosphate rocks (PRs). The use of naturally occurring low-molecular weight organic acids (LMWOAs) that are produced in soil as microbial metabolites or plant exudates from dead or living cells represents a new perspective in PR research. The LMWOAs contain various functional groups that may play a significant role in PR dissolution. Little information is available, however, about the potential of LMWOAs in releasing P from PRs. This study reports P release from 12 PRs, four each of low, medium, and high reactivity, obtained from various deposits (Kodjari, Tahoua, North Carolina, Gafsa, Khouribga, Tilemsi Valley, Central Florida, Sechura, Minjingu, North Florida, Hahotoe, and Parc W) using nine LMWOAs containing mono-, di-, and tri-carboxylic groups and a mineral acid (H₂SO₄). Laboratory studies showed that the organic acids are effective in releasing P from low and medium reactive PRs, but very ineffective in releasing P from high reactive PRs. The average amounts of P released by all the organic acids from the three types of PRs were 65.5 mmol kg⁻¹ PR from the low reactive PRs, 55.1 mmol kg⁻¹ from the medium, and 11.1 mmol kg⁻¹ from the high; those released from across all the PRs were 21.9 by the mono-carboxylic acid group, 54.2 by the di-carboxylic acid group, and 57.0 mmol P kg⁻¹ by the tri-carboxylic acid group. The P released was negatively correlated with the equilibrium pH, but positively correlated with Ca released from the PRs. Laboratory incubation studies on the release of P from PRs added to soils with or without organic acids and incubated at 25 °C for 15, 30, and 45 days showed that the percentage of plant-available P released varied considerably from 0.95 in the Kodjari PR to 40.1% in the North Carolina PR and was related to PR reactivity. A greenhouse study with corn (Zea mays L.) grown for 60 days on soils treated with PRs or with PRs mixed with organic acids showed that corn response to addition of oxalic or citric acid varied with P rates and PR sources, suggesting that organic acids have potential as amendments for increasing plant-available P in PR-treated soils.