不同措施对土壤-植物系统植物地上部产量及氟含量的影响

盆栽试验研究不同措施对土壤-植物系统植物地上部产量及F含量的影响结果表明,F对黑麦草发芽有抑制作用,干旱下植物易受F中毒,黑麦草地上部鲜物质量、干物质量及F含量在2种土壤(黄壤、石灰土)间呈相同变化趋势,试验所选4种物质不利于黑麦草干物质量的积累。硅钙肥、石灰对黑麦草F含量均为负效应,有利于降低F含量,粉煤灰对2种土壤黑麦草F含量均为正效应,风化煤对黄壤黑麦草F含量表现为正效应,而对石灰土黑麦草F含量则表现为负效应;硅钙肥和风化煤对2种土壤黑麦草F含量均表现为负交互作用,而石灰和粉煤灰对黑麦草F含量均为正交互作用。     

石油污染土壤的生物修复研究进展

对于石油污染土壤的修复,其生物修复具有环境友好、费用较低等特点,是最具应用前景的土壤修复技术。本文较全面地介绍了石油污染土壤生物修复的影响因素、石油污染土壤的生物修复技术,并对该领域今后的研究重点进行了展望。     

重庆市主城区街道地表物中重金属的污染特征

分析了重庆市主城区街道地表物的基本性质及As、Cd、Cr、Cu、Hg，Ni、Pb，Zn等元索的全置、模拟酸雨（pH4．5）的浸出量。结果表明：各功能区中街道地表物的自然组成均以中等粒径的为主；就元素而言，粒径越细对重金属的贡献率越高；就功能区而言．细粒径与中等粒径的颗粒对重金属贡献率较为接近。街道地表物呈碱性，有潜在的有机物污染。重庆市主城区街道地表物重金属元素含量有较大的差异，受人为活动干扰严重的重金属种类为Cr、Cd、Hg、Cu。内梅罗指数评价结果显示除Ni外，其他元素均有不同程度的污染，各功能区均受到重金属的严重污染。重庆市主城区街道地表物中的重金属只与其中的磷素含量显著正相关。     

1种食用菌细菌隐性污染栽培种的菌种分离研究

研究1种以木屑为主要配方的食用菌细菌隐性污染栽培种的菌种分离。稀释涂布平板法分析细菌总数。栽培种捣碎后悬于无菌水,分别以短时(5 min)涡漩振荡、摇床振荡(180 r/min)、低温静置(4℃) 3种方式处理;灭菌纱布过滤收集、无菌水淋洗木屑接种至PDA斜面,培养使其生长。以未经处理木屑为接种物作为对照。结果显示栽培种细菌数为15500 cfu/g;对照（30支）以及采用短时涡漩振荡处理所接30支斜面全部细菌污染;摇床振荡1、2、3、4天纯化率分别为20%、30%、46.67%及63.3%;低温静置1、2、3、4天纯化率分别为3.3%、10%、46.67%和60%。以木屑为主要配方的细菌隐性污染栽培种悬于无菌水经1~4天振荡或浸湿再分离的基内菌丝分离法可有效分离纯化菌种。     

焉耆盆地绿洲区地下水硝态氮污染空间变异性研究及成因分析

为了研究焉耆盆地绿洲区地下水硝态氮污染状况,通过野外采样及室内分析,运用地统计学方法中的普通克里金(Or-Kriging)法对绿洲农区207个地下水进行了硝态氮空间变异分析,并以河流、农田排渠水中的硝态氮量分析了硝态氮污染的原因。结果表明,绿洲区地下水体硝态氮量总体水平较低,平均值为3.32mg/L,属国家地下水Ⅱ类质量标准,但不同区域地下水的硝态氮量差异明显;采用普通克里金插值对绿洲区未测区域进行估值并按照国家地下水质量标准进行分区表明,绿洲农区大部分区域地下水硝态氮量已接近世界卫生组织(WHO)的最大允许质量浓度(10.0mg/L),个别地区已处于污染警戒状态(20.0mg/L),需尽早采取有效措施防治。随着近些年集约化农业的发展,氮肥施用量的增加及利用率偏低是盆地绿洲区地下水硝态氮污染的根本原因。     

Using the soil gas radon as an indicator for ground contamination by non-aqueous phase-liquids

1 The Problem  One of the major problems facing risk assessment at polluted industrial sites and military bases is subsurface contamination by non-aqueous phase-liquids (NAPLs), since tracing the extent of a NAPL plume using conventional methods (drive point profiling) is usually associated with difficulties. In an effort to trace subsurface contamination as precisely as possible, monitoring points are placed in the area that might be affected by contaminants, and groundwater and soil samples are taken to the laboratory for analysis. However, the final number of monitoring points is hardly ever sufficient for distinctive contamination mapping, and this may ultimately result in an unsuitable remediation action being taken. 2 Objectives  To obtain a more detailed image of a subsurface NAPL plume and, hence, to facilitate remediation measures that are best suited for the site in question, a denser network of monitoring points is desirable. The aim of the investigation described in this paper was therefore to develop a new detection method for subsurface NAPL contamination, which is based on an easily accessibleindicator for NAPLs rather than on the analysis of soil and groundwater samples taken at the site. Based on the good solubility of radon in NAPLs, the idea was put forward that subsurface NAPL contamination should have an influence on the natural radon concentration of the soil gas. Provided this effect is significant, it would be possible to carry out a straightforward radon survey on an appropriate sampling grid covering the suspected site and thus enabling the NAPL contamination to be detected by the localization of anomalous low radon concentrations in the soil. The overall aim of the investigation was to assess the general suitability of the soil-gas radon concentration as an indirect tracer for NAPL contamination in the ground. 3 Methods  The partitioning coefficient K_NAPL/air is one of the most influential parameters governing the decrease of the radon concentration in the soil gas in the presence of a subsurface NAPL contamination. Since NAPL mixtures such as gasoline, diesel fuel and paraffin are among the most important NAPLs regarding remediation activities, laboratory experiments were performed to determine the radon-partitioning coefficient for these three NAPL mixtures. Field experiments were carried out as well. The aim of the field experiments was to test the use of the soil-gas radon concentration as a tracer for NAPL contamination on-site. For the field experiments, each site was covered with a suitable grid of soil gas sampling points. Finally, the lateral radon distribution pattern achieved on each of the sites was compared to the respective findings of the earlier research performed by conventional means. 4 Results and Discussion  The results of the laboratory experiments clearly show a very strong affinity of radon to the NAPL mixtures examined. The partitioning coefficients achieved correspond to those published for pure NAPLs (Clever 1979) and are thus in the expected range. The results of the field experiments showed that the minimum radon concentrations detected match the respective NAPL plumes traced previously. 5 Conclusions  Both the results of the lab experiments and the on-site findings demonstrate that the soil-gas radon concentration can be used as an indicator for subsurface NAPL contamination. The investigation showed that NAPL-contaminated soil volumes give rise to anomalous low soil-gas radon concentrations in the close vicinity of the contamination. The reason for this decrease in the soil-gas radon concentration is the good solubility of radon in NAPLs, which enables the NAPLs to accumulate and ‘trap’ part of the radon available in the soil pores. 6 Recommendations and Outlook  Further research is required into contamination with rather volatile NAPLs such as BTEX. Further research is also needed to examine whether it is possible to not only localize a NAPL plume, but also to obtain some quantitative information about the subsurface NAPL contamination. The authors also believe that additional investigations should be carried out to study the ability of the method to not just localize a NAPL contamination, but also to monitor on-site, clean-up measures.     

线虫群落结构对外源添加不同浓度铜污染物的响应

通过盆栽模拟试验的方法研究外源添加铜对土壤线虫群落结构的影响,试验添加Cu浓度分别为50 mg kg-1,100 mg kg-1,200 mg kg-1,400 mg kg-1干土和不施加污染物的对照处理,在小麦的生长关键期取样。试验结果表明:线虫不同营养类群对铜污染物的响应在小麦拔节期比较明显,拔节期捕食/杂食线虫的数量在外源添加400 mg kg-1Cu处理中显著低于对照,而不同浓度铜对食细菌线虫和食真菌线虫的影响则表现为低浓度促进高浓度抑制。线虫的生态指数对不同浓度铜污染物反映比较敏感,在小麦苗期和拔节期,与对照相比,不同浓度铜处理中线虫多样性降低,而优势度增加;自由生活线虫成熟度指数对不同浓度铜反映相对滞后,只在小麦成熟期表现出差异,即高浓度铜处理中线虫成熟度指数显著低于对照。     

粉煤灰和碳酸钙对As（Ⅲ）污染土壤上小麦产量性状及麦株As含量的影响

随着经济的发展,土壤As污染问题日益严重。采用露天盆栽试验方法,研究了在As（Ⅲ）污染土壤上,添加粉煤灰和碳酸钙对小麦成熟期产量及其性状、小麦根、茎叶和籽粒As含量的影响,并探讨了粉煤灰和碳酸钙对土壤As（Ⅲ）污染修复的有效方法。结果表明,在土壤中添加100g·kg^-1的粉煤灰或1．0g·kg^-1的碳酸钙能使小麦株高、结实小穗数、穗粒数、千粒重和产量增加。与对照相比,在As（Ⅲ）污染土壤上,100g·kg^-1的粉煤灰处理显著地增加了小麦产量（P〈0．05）,极显著地降低了小麦籽粒As含量（P〈0．01）;1．0g·kg^-1的碳酸钙处理极显著地增加了小麦的穗粒数、千粒重和产量（P〈0．01）,显著地降低了根中As含量（P〈0．05）,极显著地降低了籽粒As含量（P〈0．01）。因此,在As（Ⅲ）污染土壤上,添加100g·kg^-1的粉煤灰或1．0g·kg^-1的碳酸钙能使小麦产量升高,籽粒As含量下降,有效地缓解As（Ⅲ）对小麦的毒害。     

植物修复重金属污染土壤的研究进展

介绍了重金属污染土壤植物修复的概念，回顾了国内外植物修复金属污染土壤的发展状况，初步探讨了植物对重金属污染土壤的修复机理，并提出了植物修复未来的发展趋势。     

高砷煤矿周围旱作土壤重金属污染特征及农作物健康风险评价

为了掌握高砷煤矿周边旱作农田重金属污染状况,运用单因子污染指数法、内梅罗综合污染指数法和地积累指数法对高砷煤矿周边旱作土壤重金属（As、Cd、Hg、Cu、Zn）进行污染风险评价,并采用富集系数法、目标危害商数法和致癌风险指数法对农作物和人体健康风险进行评价。结果表明：调查区域土壤综合污染指数均值为2.12,属中度污染水平;土壤中As、Cd、Hg、Zn、Cu的含量均值分别为全国土壤背景值的7.91、2.57、5.26、1.53、3.44倍;As和Hg的污染等级高且范围广,Cu污染等级低但污染范围广,Cd的污染等级较低且范围较小,Zn基本无污染。富集系数法评价结果显示,作物对5种重金属的吸收能力表现为Cd>Zn>Cu>Hg>As。农作物健康风险评价结果显示,5种农作物的健康风险主要为非致癌风险,As是可食用农作物（除玉米外）的主要致癌风险因子和非致癌风险因子,Cd是烟草的主要致癌风险因子和非致癌风险因子。食用本地农作物对人体造成的健康风险依次为As>Cd>Hg>Cu>Zn。研究表明：研究区域土壤处于中度污染水平,As的风险较高;可食农作物中重...