有机肥施用对土壤环境潜在风险研究进展

施用有机肥是培肥地力、改良土壤的重要方式, 有机肥在提高土壤供肥能力和作物产量、改良作物根际生态环境、改善作物的营养品质及抑制病虫害发生等方面具有重要作用, 但施用有机肥也会带来一定的土壤环境风险。对规模化养殖来源为主的有机肥施用带来的土壤环境的风险进行了综述。未腐熟的有机肥施入农田易出现烧苗、病虫害等问题, 对农田作物环境造成不利的影响; 规模化养殖场畜禽粪便生产的有机肥存在重金属、抗生素和激素残留的现象, 施入农田具有一定的重金属和有机污染物污染的风险; 此外, 有机肥的不合理的施用还存在农田氮磷流失, 可能会对水体造成富营养化的风险。通过分析有机肥对土壤肥力及环境风险的影响, 为农业生产中有机肥的合理施用提供借鉴, 在降低环境风险的同时达到培肥土壤与提高作物产量和品质的目的。     

我国农田生态系统土壤动物生态学研究进展

综述了我国近30年来农田生态系统土壤动物生态学研究进展,概述了我国农田土壤动物的群落多样性及其地理分布,总结了农田生态系统中土壤动物对不同耕作方式、施肥和喷洒农药等农业措施、不同土地利用方式以及工业污染的响应,并就土壤动物对农田生态系统健康状况的指示作用等研究的相关进展进行了讨论.通过与国外相关领域的研究进行比较,指出目前研究中存在的问题,提出农田生态系统未来研究的一些热点问题及展望.     

天津市武清区农田土壤和蔬菜中重金属污染特征及来源解析

为评价中国北方典型农田土壤和蔬菜重金属污染特征,从天津市武清区分别采集45个农田表层土壤及对应的叶类蔬菜、32个农用畜禽粪便样品和4组土壤剖面,测定了Cd、Cr、Cu、Ni、Pb和Zn共6种重金属的含量和形态,并利用相关性分析和主成分分析判断土壤中重金属污染的可能来源。结果表明:表层土壤6种重金属的累积程度依次为CdCrCuZnPbNi,其中26.7%的Cd超过了土壤环境质量二级标准(GB 15618—2018);叶类蔬菜根部存在重金属累积(尤其是Cd),但蔬菜叶片中并不存在重金属超标;研究区所施用的畜禽粪便中Cd的超标率为16%(参照NY 525—2012),其长期施用会造成表层土壤中重金属的累积;同时,表层土壤中高的可交换态Cd、Cu和Zn会增加作物吸收土壤中重金属的风险,是造成当地叶类蔬菜根部和叶片中重金属累积的原因之一。结合主成分分析结果:Cr和Ni主要来自于成土母质; Zn主要受农业活动影响,如畜禽粪便的施用; Cd和Pb主要受工业活动影响; Cu为复合污染,受工业和农业活动共同影响。综上所述,研究区土壤和畜禽粪便中存在Cd超标现象,虽然目前蔬菜叶片中重金属未超标,但应该注意控制或减少农业和工业污染对蔬菜地重金属的影响,以确保农田土壤和蔬菜的安全。     

基于序贯指示模拟的农田土壤重金属风险区域识别

农田土壤重金属的日益累积已对农作物安全、生态环境和人类健康造成严重威胁,高效、精确地识别农田土壤重金属风险区对农田的环境保护、污染预警和风险管控等有重要意义.以广州市增城区为研究对象,共采集204个农田土壤样点,测定了铜(Cu)、锌(Zn)、铅(Pb)、镉(Cd)、铬(Cr)、砷(As)和汞(Hg)7种重金属含量.针对实际采样数据中存在异常值与偏态分布,以及传统克里格法存在的平滑效应等问题,将序贯指示模拟引入农田土壤重金属的风险识别中,与常用识别方法进行比较,并根据Hakanson风险指数评价进行风险区划.结果表明:(1)对比普通克里格法,在精度相似情况下,序贯指示模拟法较为精细地模拟了重金属的空间分布,平滑效应低,预测的细节表现好;对比指示克里格法,其在划分风险区域时的不确定评估中准确度较高,其误判率仅为4.9%~17.1%,表明其能更好地适用于模拟农田土壤重金属的空间分布和风险识别;(2)增城区的农田土壤重金属均未超标,但在南部的极少数区域存在潜在中等风险,主要成因是包括企业生产、人类活动和河流沉积物等.本研究以序贯指示模拟为基础,有效克服了传统克里格法存在的异常值信息丢失和平滑效应问题,结合Hakanson风险指数法,为非均匀采样的土壤重金属空间风险的识别提供一种新的尝试.     

中国农田生态系统土壤呼吸作用研究与展望

 农田生态系统是陆地生态系统的重要组成部分,占全球陆地面积的10.5%,其CO₂排放量占人为温室气体排放量的21%～25%;由于农田生态系统 受到强烈的人为干扰,因此农田生态系统土壤呼吸作用及其影响因素对准确评估陆地生态系统碳收支具有重要的意义。中国是个有悠久历史的 农业大国,不仅为农田土壤作用的研究提供了天然的实验室, 而且中国农田土壤呼吸作用的研究对全球的碳循环研究及碳收支准确评估具有非 常重要的示范与指导意义。该文综述了近10年来中国农田生态系统土壤呼吸作用研究进展,指出水热因子、作物生物学特性和农业管理活动是 造成中国农田生态系统土壤呼吸作用时空变异 的主要因素;作物根系呼吸作用占土壤作用的比例在13%～77.2%之间,存在极大的不确定性;合 理施肥、秸秆还田和免耕有助于农田生态系统土壤呼吸作用减排和固碳。指出了中国农田生态系统土壤呼吸作用拟重点加强不同区域典型农田 生态系统土壤呼吸作用的比较、空间异质性、影响因素模拟及减排对策等方面的研究。     

湖北江汉平原农田生态系统Mn的循环及平衡分析

农田生态系统中 ,营养元素循环与平衡的研究已经受到许多学者的广泛关注 ,主要集中于Ｎ ,Ｐ ,Ｋ三要素的研究[1 ,2 ] 。微量元素养分循环的研究虽有一些报道[3 ,4] ,但主要集中于Ｂ和Ｚｎ元素 ,而对Ｍｎ的研究尚未见报道。微量元素Ｍｎ具有植物营养和污染危害双重作用。在我国 ,Ｍｎ肥的应用研究 ,包括肥效、施肥技术、丰缺诊断等已取得较大进展 ,Ｍｎ对环境污染及危害影响研究也取得了一些成果。随着Ｍｎ肥应用面积日益扩大 ,研究其在土壤 植物系统中循环与平衡 ,以维持Ｍｎ肥对作物适量供应 ,促进农田生态系统Ｍｎ肥的良性循环以及控制土…     

易旱农田生态系统养分循环的研究

对多熟制农田生态系统的养分循环研究表明,小麦后稻-稻(农田Ⅰ)、大麦后稻-豆(农田-Ⅱ)和油菜后稻-稻(农田-Ⅲ)复种制Ca、Mg有盈余。P、K、Fe、Mn均表现亏缺,N素有较大的浪费。N、P、K主要通过肥料输入农田生态系统,而随农产品输出系统外,Ca、Mg主要受水循环控制,作物残留部分中,N的残留量最大,为23—71kg·ha~(-1),Fe的残留率最高,为64—87％。     

我国主要类型农业地区农田生态系统多样性的研究

通过对我国 5个典型农业类型区农田生态系统多样性现状的调查 ,建立了农田生态系统多样性数据库 ,在分析了各典型调查地区的土地利用、作物接续、作物搭配、系统类型单元等多样性特征的基础上 ,计算出各农田生态系统多样性指标 .结果表明 ,我国主要类型农业地区的最大丰富度相差不大且普遍偏低 ;各地区间平均丰富度 ( Ta)差异明显 ,且总体上丘陵地区高于平原 ,平原地区自南向北递减 ;各地区间的均匀度 ( E)和优势度( D)无明显差异 ,丘陵地区的 E相对高于平原地区 ,而 D与 E相反 .据此提出了建设多样化的农田生态系统结构、改进当前农田生态系统多样性的建议 .     

阜新市农田土壤重金属含量及其分布特征

通过对辽宁省阜新市城郊区县180处农田土壤的取样调查分析,初步了解了农田土壤重金属As、Cu、Zn、Ni的含量特征及其空间分布,并探讨了当地矿业开采活动对农田土壤重金属积累及空间分布的影响.结果表明,研究区域内农田土壤Cu、Zn和Ni的几何平均含量均高于背景值,且这3种重金属存在普遍累积的现象;不同种植类型土壤中,菜地土壤Cu、Zn、As含量显著高于粮田,且重金属积累更为明显;4种重金属的空间分布均呈城区高于郊县的趋势;重金属含量较高的区域与矿山开采区域基本重叠.研究区域内采矿活动是农田重金属的重要来源,同时畜禽养殖业所产生的畜禽粪便可能对农田土壤中Cu、Zn和As的增加有一定作用.当地农牧业生产和布局应适当考虑土壤污染的风险.     

湖北江汉平原农田生态系统钢的循环与平衡

对湖北江汉平原农田生态系统8种种植模式中Cu的输入、输出和平衡进行了分析。结果表明,农田Cu的输出主要是作物收获,其输出量占总输出量的85.9%-95.1%,流失和淋溶输出很少,农田Cu的输入主要是有机肥输入和降雨输入,其次是降尘、作物自然归还和灌溉,而种子种苗和无机肥输入占很少的比例。农田Cu的平衡分析表明,按照当地施肥习惯,菜田和水田Cu盈余较多,而旱地4种种植模式基本平衡。     

EDTA-Enhanced Phytoremediation of Heavy Metals: A Review

The increase in heavy metal terrestrial ecosystems’ contamination through anthropogenic activities is a widespread and serious global problem due to their various environmental and human implications. For these reasons, several techniques, including phytoremediation of heavy metals, have been extensively studied. In spite of significant recent advancement, ethylene diamine tetraacetic acid (EDTA)-enhanced heavy metal phytoextraction as well as related ecological risks are still topical and remain an important area of research. In fact, EDTA favors the solubilization of metals and metalloids in soils, and was therefore extensively studied during the last two decades in order to improve phytoextraction efficiency and reduce treatment duration. This review highlights the recent findings (2010–2012) and mechanisms behind EDTA-enhanced (1) solubilization of heavy metals in soil, (2) mobilization/transport of soluble metals towards plant root zone, and (3) metal absorption by plant roots and translocation towards aerial parts. The review also presents potential risks associated with EDTA-enhanced phytoextraction: (1) environmental persistence of EDTA and/or metal-EDTA complex; (2) potential toxicity of EDTA and/or metal-EDTA complex to plants; and (3) leaching and contamination of groundwater. Moreover, field-scale cost of EDTA-enhanced remediation and the role of EDTA in time required for heavy metal remediation is discussed.     

Environmental Monitoring of Heavy Metal Status and Human Health Risk Assessment in the Agricultural Soils of the Jinxi River Area,China

Soil contamination with heavy metals is one of the main environmental concerns in China, mainly owing to rapid industrialization and mining activities in certain areas. The current study aimed at monitoring the levels of heavy metals in soils of the industrial areas along the Jinxi River and surrounding Lake Qingshan. In addition, a health risk assessment for humans in contact with these soils was also conducted. The results revealed that the soils of the studied areas were contaminated with Cr, Cu, As, Se, Cd, Pb, and Zn and that the industrial activities were the main source of soil contamination therein. Furthermore, soils of the sites adjacent to Lin’an city exhibited higher levels of heavy metals than the upstream and Lake Qingshan sites. Most of the studied heavy metals tended to concentrate in the fine soil fractions (PM100, PM10, and PM2.5). Calculation of the hazard index (HI) revealed that humans, especially children, have potential health risks. Moreover, As was found to contribute to more magnitude of cancer risks. Thus, we concluded that the unmanaged development negatively affects the Chinese environment and human health. Furthermore, fine fractions of soil particles should be considered for risk assessment.     

解磷微生物修复土壤重金属污染研究进展

土壤重金属污染问题日益严重,具有普遍性、隐蔽性、表聚性、不可逆性等特点,已经成为环境污染治理中的热点、难点问题。解磷微生物能够依靠自身的代谢产物或通过与其他生物的协同作用,将土壤中的难溶性磷转化为可供植物吸收利用的磷,具有多重植物促生长功能和重金属解毒能力,可在重金属毒害水平下,促进植物生长、提高植物抗病能力、克服重金属对植物生长的不利影响,从而增强重金属修复植物的生存竞争力。从解磷微生物的研究现状入手,介绍了解磷微生物对土壤重金属污染的修复能力,综述了解磷微生物对土壤重金属污染修复的作用机制,分析了目前解磷微生物在重金属修复过程中存在的问题,并提出了今后研究的方向,为重金属污染土壤的修复提供了新思路。     

山东省部分水岸带土壤重金属含量及污染评价

为了解山东省水岸带土壤重金属的含量特征和污染状况,于2010年9月—10月采集了39个水岸带土壤样品,分析了土壤中Cr、Co、Ni、Cu、Zn、Cd、Pb和Hg的含量以及土壤的pH值、粒度和有机质,采用单因子指数法、综合指数法和潜在生态危害指数法对水岸带土壤重金属污染进行了评价,并利用相关分析和聚类分析对其来源进行了初步的解析。结果表明：水岸带土壤的pH值为5.67—8.66,主要呈碱性;有机质的平均含量为9.39 g/kg,土壤粒度主要以砂粒和粉粒为主,其平均体积百分比分别为50.33%和38.48%,平均粒径为89.69 μm;Cr、Co、Ni、Cu、Zn、Cd、Pb和Hg的平均含量为53.03 mg/kg、10.33 mg/kg、24.96 mg/kg、18.38 mg/kg、56.13 mg/kg、0.142 mg/kg、22.48 mg/kg和0.020 mg/kg。各水岸带土壤重金属的含量均符合《土壤环境质量标准》（GB15618-1995）二级标准。以山东省土壤元素背景值为评价标准,水岸带土壤重金属总体表现为轻度污染和轻微生态风险,其中Cd和Hg是主要的污染因子,其对潜在生态危害指数的平均贡献率分别为46.8% 和33.6%。洙赵新河、廖河、门楼水库和东平湖水岸带土壤重金属污染及潜在生态危害明显高于其他水源地。源解析的结果表明：水岸带土壤重金属的含量受自然源和人为源的双重影响,人为源主要包括地表径流、工业废气、垃圾和交通运输等。     

Health Risk Assessment of Heavy Metals in Soils and Vegetables from a Typical Greenhouse Vegetable Production System in China

There is growing concern about food safety and environmental contamination due to potential health risks to consumers. The aims of this study are to elucidate the accumulation status, influencing factors, and potential risk of selected heavy metals in soils and vegetables from a typical greenhouse vegetable production system in China. The potential health risks of heavy metals through soil contact and vegetable consumption were evaluated for greenhouse and corresponding open field production. The results indicated that the mean concentrations of Hg, Pb, Cu, and Zn in greenhouse vegetable soils were greater than those in open field soils. Leaf vegetables had relatively higher concentrations and transfer factors of heavy metals than root and fruit vegetables, especially for Cd. The target hazard quotient of heavy metals through vegetable consumption was greater than 1 for leaf vegetables, and was also higher for greenhouse vegetables than those from open field. The risk of exposure to heavy metals through direct contact with soil and vegetable consumption was higher for children than for adults and seniors. Planting patterns with different vegetable types and soil properties can affect bioavailability and crop accumulation of heavy metals.     

硫对土壤重金属形态转化及植物有效性的影响研究进展

生源要素硫在土壤中的化学循环不仅会直接影响土壤重金属元素的环境行为,也可通过调控植物根际微环境间接影响植物对重金属元素的吸收累积.土壤中的硫被植物根吸收后在植株中合成的有机硫化合物如植物螯合素(PCs)和金属硫蛋白(MTs)可与重金属形成毒性较低的络合物,构成植物重金属解毒的重要机制之一.我国部分土壤缺硫现象严重,为保证作物高质高产,硫肥的使用逐渐被重视,而硫与重金属的交互作用机制也逐渐成为研究热点.本文综合相关研究,介绍了硫在土壤中的生物化学转化,探讨了土壤硫的化学转化对土壤重金属形态转化及植物有效性的影响,并对今后硫在土壤重金属控制的应用提出展望.
     

重庆溶溪锰矿区土壤重金属污染评价及植物吸收特征

对重庆溶溪锰矿尾渣堆积区土壤、优势植物以及周边农田土壤的重金属含量(Mn、Cd、Cu、Zn和Pb)进行测定分析,并以重庆市土壤背景值为评价标准,应用Hakanson潜在生态危害指数法对土壤中重金属的潜在生态危害进行了评价。结果表明:该锰矿尾渣堆积区土壤中Mn、Cd、Cu、Zn和Pb的平均含量分别为48382.5、3.91、79.97、131.23和80.68 mg/kg,受到Mn、Cd的严重污染,Mn为强或很强生态危害,Cd为极强生态危害,而Cu、Zn、Pb为轻微生态危害,各尾矿渣堆积区的综合潜在生态危害指数(RI)均远大于720,为极强生态危害。对优势植物重金属含量的分析显示,绝大部分植物地上部Mn、Cd含量都超出正常范围的上限值,而Cu、Zn和Pb含量基本都在正常范围内;根据植物对重金属的吸收特征,将植物分为三类:将重金属主要累积于地上部分的富集型,如垂序商陆(Phytolacca americana L.)和酸模叶蓼(Polygonum lapathifolium Linn.),适用于重金属复合污染土壤的植物修复;将重金属主要累积于根部的根部囤积型,如芒(Miscanthus sinensis Anderss.)和乌蕨(Stenoloma chusanum Ching);重金属含量较低的规避型,如黄花蒿(Artemisia annua L.)、长波叶山蚂蝗(Desmodium sequax Wall.)及钻形紫苑(Aster subulatus Michx.);后两种类型的植物可种植在重金属污染严重且使用价值相对较低的矿山废弃地上,同时规避型植物对于研究植物的重金属排斥机理具有重要价值。溶溪锰矿区周边农田土壤主要受到Cd的严重污染,Cd为很强或极强生态危害。     

土壤重金属生物毒性研究进展

世界范围内土壤重金属污染不断加重,由污染所带来的问题以及如何治理污染已经受到人们越来越多的关注.土壤重金属将对土壤生物产生影响,而土壤生物在重金属的胁迫下也会产生不同的响应.综述了国内外近年来土壤重金属生物毒性的研究进展,介绍了土壤重金属污染对陆地生态系统中植物、动物和微生物生长的影响;土壤重金属生物毒性的影响因素;土壤重金属生物毒性的研究方法;土壤重金属生物毒性的预测模型,最后提出了问题和展望.     

In Vitro Health Risk Assessment of Ingesting Metal-Enriched Soils and Dusts in a Chinese Mining City

To evaluate the potential health hazards caused by extensive vanadium–titanium magnetite mining, bioavailability and bioaccessibility of metals were assessed in the pluralistic mining–agriculture–residential city of Panzhihua, China. Intensive mining and related heavy traffic may have contributed to Ni, Cr, and Zn contamination and Mn and V accumulation in soils and road dusts. The metal bioavailability estimated by water extraction was significantly lower than metal bioaccessibility on the basis of the simple bioaccessibility extraction test. The bioaccessible metal concentrations were significantly and positively correlated with soil/dust total metal concentrations (p < .05). However, bioavailable metal concentrations exhibited no relationship with total metal concentrations except for V. The bioaccessibility of metals significantly varied and exhibited the following order: Pb > Zn > Mn > Ni > V > Cr. Health risk assessment indicated that the carcinogenic and non-carcinogenic risks posed by these metals were at an acceptable level, but Cr in soils of the mining area and V in surface soils along the Jinsha River were close to the safe level for children. Therefore, the potential health risk attributed to the exposure of children to metals in surface soils and road dusts in such areas should not be overlooked.     

Heavy metal pollution in aquatic ecosystems and its phytoremediation using wetland plants: an ecosustainable approach

This review addresses the global problem of heavymetal pollution originating from increased industrialization and urbanization and its amelioration by using wetland plants both in a microcosm as well as natural/field condition. Heavymetal contamination in aquatic ecosystems due to discharge of industrial effluents may pose a serious threat to human health. Alkaline precipitation, ion exchange columns, electrochemical removal, filtration, and membrane technologies are the currently available technologies for heavy metal removal. These conventional technologies are not economical and may produce adverse impacts on aquatic ecosystems. Phytoremediation of metals is a cost-effective "green" technology based on the use of specially selected metal-accumulating plants to remove toxic metals from soils and water. Wetland plants are important tools for heavy metal removal. The Ramsar convention, one of the earlier modern global conservation treaties, was adopted at Ramsar, Iran, in 1971 and became effective in 1975. This convention emphasized the wise use of wetlands and their resources. This review mentions salient features of wetland ecosystems, their vegetation component, and the pros and cons involved in heavy metal removal. Wetland plants are preferred over other bio-agents due to their low cost, frequent abundance in aquatic ecosystems, and easy handling. The extensive rhizosphere of wetland plants provides an enriched culture zone for the microbes involved in degradation. The wetland sediment zone provides reducing conditions that are conducive to the metal removal pathway. Constructed wetlands proved to be effective for the abatement of heavymetal pollution from acid mine drainage; landfill leachate; thermal power; and municipal, agricultural, refinery, and chlor-alkali effluent. the physicochemical properties of wetlands provide many positive attributes for remediating heavy metals. Typha, Phragmites, Eichhornia, Azolla, Lemna, and other aquatic macrophytes are some of the potent wetland plants for heavy metal removal. Biomass disposal problem and seasonal growth of aquatic macrophytes are some limitations in the transfer of phytoremediation technology from the laboratory to the field. However, the disposed biomass of macrophytes may be used for various fruitful applications. An ecosustainable model has been developed through the author's various works, which may ameliorate some of the limitations. The creation of more areas for phytoremediation may also aid in wetlands conservation. Genetic engineering and biodiversity prospecting of endangered wetland plants are important future prospects in this regard.