Accumulation and ecological effects of soil heavy metals in conventional and organic greenhouse vegetable production systems in Nanjing,China

The spatial variability of soil heavy metals in conventional and organic greenhouse vegetable production (CGVP and OGVP) systems can reveal the influence of different farming activities on their accumulation and plant uptake. This provides important basic data for soil utilization and pollution risk assessment. Based on horizontal and vertical spatial analysis, this paper presents the spatial variability and accumulation of soil heavy metals. The effects on plant uptake and factors influencing heavy metal accumulation are presented using the two typical greenhouse vegetable sites in Nanjing City, China as examples. Results showed that different greenhouse vegetable production systems had their own dominant heavy metal accumulation, specifically, Hg and Pb in CGVP system and Cd in OGVP system. The spatial analysis showed that horizontally, distribution of soil properties and heavy metal concentrations in the two sites showed decreases from specific regions to the periphery for organic matter (OM), Cd, Cu, Hg, Pb, and Zn in CGVP and OM, As, Cd, Cu, Hg, Pb, and Zn in OGVP. Vertically, soil properties and heavy metals mainly vary in the topsoil. The key factor for the accumulation was excess fertilizer input. Variation of soil properties and the accumulation of soil heavy metals significantly influenced heavy metal uptake by plants. However, accumulation risk varied according to different heavy metals and different plant species. Environmental management of these two kinds of production systems should pay more attention to fertilizer application, plant selection, and soil properties.     

湖州市不同土壤重金属的污染现状

湖州市是主要的农产品基地，其主要土壤类型有四种，即黄泥土、青紫泥、白泥土和湖松土。样品分析表明重金属元素在黄泥土和青紫泥中较高，白泥土和湖松土中较低。大多数重金属元素相对下蜀土是富集的，超过自然背景值的元素有Cu,Cd及部门土壤中的Pb和Hg。有机质、pH值和Eh值对重金属的含量和化学形态有影响，有机质愈高，重金属的含量愈高；pH值接近中性，重金属的含量亦高。土壤的氧化条件可使大多数重金属变为高价离子，它们的化合物活性较低，但Cr^6 易被植物吸收。湖州土壤中重金属的高值点与工业污水排放和大气沉降有关。土壤中对农作物有危害的重金属元素为Cd和Hg，局部地方为Pb。     

Removal of heavy metals from a contaminated soil using organic chelating acids

Changes in heavy metal speciation and uptake by maize in a soil before and after washing with chelating organic acids, citric acid, tartaric acid and ethylenediaminetetraacetic acid were assessed. A sandy loam was collected from the vicinity of the Benue industrial layout, Makurdi, Nigeria and spiked with a quinternary mixture of nickel, copper, zinc, cadmium and lead nitrates to achieve higher levels of contamination. Batch soil washing experiments performed on 1.0 g portions of the spiked soil using 0.05 M chelating agents at a solid:liquid ratio of 1:25 showed that washing efficiencies varied in the order: ethylenediaminetetraacetic acid> citric acid> tartaric acid with metal extraction yields typically following the sequence, copper> nickel> zinc> cadmium> lead. Sequential extractions proposed by the European Communities Bureau of Reference method used to assess the redistribution of heavy metal forms in the soil showed that apparent metal mobilities were reduced upon soil washing. Citric acid removed most of the metals hitherto associated with the exchangeable and reducible fractions; tartaric acid, the exchangeable metal pools; and ethylenediaminetetraacetic acid, the non-residual metal pools. Heavy metal assay of harvested biomass of maize grown on unwashed and washed soil samples indicated that metal transfer coefficients, decreased in the order of treatment: ethylenediaminetetraacetic acid <citric acid <tartaric acid <unwashed soil. Ethylenediaminetetraacetic acid and citric acid appeared to offer greater potentials as chelating agents to use in remediating the high permeability soil. Tartaric acid, however, is recommended in events of moderate contamination.     

Effects of key components of <Emphasis Type="Italic">S. triqueter</Emphasis> root exudates on fractions and bioavailability of pyrene–lead co-contaminated soils

The key components of S. triqueter root exudates involved 4-oxo-pentanoic acid, succinic acid, glutaric acid, phthalate acid, citric acid, vanillic acid, myristic acid, pentadecanoic acid, decanoic acid, 14-methyl-pentadecanoic acid, hexadecanoic acid, octadecanoic acid and oleic acid, and the content of the water-soluble organic acids (citric acid, succinic acid and glutaric acid) significantly increased in pyrene and lead co-contaminated rhizosphere soil. These three water-soluble organic acids including citric acid, succinic acid and glutaric acid were detected as the specific root exudates of S. triqueter under stress of pollutants for pyrene and lead, so they were chosen as the research objects, and they were added into the bioremediation systems of pyrene and lead co-contaminated wetland soils. Compared with the control, the treatments added the three organic acids always improved the quantity of the bioavailable fraction of pyrene and lead in wetland soils and greatly influenced other chemical states of pyrene and lead fractions in the test concentration range. Under the 50 g kg^?1 of organic acids concentration, the amount of the bioavailable fraction of pyrene and lead increased 41.0 and 872.7 % by citric acid, respectively. The enhancement of bioavailability of pyrene and lead in the wetland soil by adding organic acids generally decreased in the following order: citric acid > succinic acid > glutaric acid. Enhancing effects of organic acids on the bioavailability improvement of pyrene and lead is remarkable.     

Co-contamination of water with chlorinated hydrocarbons and heavy metals: challenges and current bioremediation strategies

Chlorinated hydrocarbons can cause serious environmental and human health problems as a result of their bioaccumulation, persistence and toxicity. Improper disposal practices or accidental spills of these compounds have made them common contaminants of soil and groundwater. Bioremediation is a promising technology for remediation of sites contaminated with chlorinated hydrocarbons. However, sites co-contaminated with heavy metal pollutants can be a problem since heavy metals can adversely affect potentially important biodegradation processes of the microorganisms. These effects include extended acclimation periods, reduced biodegradation rates, and failure of target compound biodegradation. Remediation of sites co-contaminated with chlorinated organic compounds and toxic metals is challenging, as the two components often must be treated differently. Recent approaches to increasing biodegradation of organic compounds in the presence of heavy metals include the use of dual bioaugmentation; involving the utilization of heavy metal-resistant bacteria in conjunction with an organic-degrading bacterium. The use of zero-valent irons as a novel reductant, cyclodextrin as a complexing agent, renewable agricultural biosorbents as adsorbents, biosurfactants that act as chelators of the co-contaminants and phytoremediation approaches that utilize plants for the remediation of organic and inorganic compounds have also been reported. This review provides an overview of the problems associated with co-contamination of sites with chlorinated organics and heavy metals, the current strategies being employed to remediate such sites and the challenges involved.     

Comprehensive analysis of heavy metals in soils from Baoshan District, Shanghai: a heavily industrialized area in China

The potential for soil heavy metal contamination in high risk areas is a crucial issue that will impact the environment. Soil samples were collected in 2003 and 2007 to investigate heavy metal contamination characteristics and pollution changes in the industrialized district of Baoshan (Shanghai, China). Both multi-statistic and geostatistic approaches were used and proved to be useful in the interpretation of the analytical results. The potential for soil contamination in the high risk areas presents a crucial issue that will impact the environment. The results indicate that soil in the Baoshan District is alkaline. Additionally, the accumulation of heavy metals in the soil increased between 2003 and 2007. The study results indicated that the concentration of the metals lead (Pb), chromium (Cr), cadmium(Cd), mercury (Hg), arsenic (As), zinc (Zn) and copper (Cu) in the soil has great discrepancy, especially of Pb and Cr. The concentrations of Pb and Cr in the soil show significant difference between two observed years (p?<?0.05). The concentration of most of these metals was higher in 2007 than 2003. Only the concentrations of Cd and As were not higher in 2007. Traffic and industrial contaminants were the likely source of Pb and As; Hg largely came from agricultural contamination, household garbage and industrial contamination; Cd, Cr, Zn and Cu mainly originated from industrial activities. Multivariate statistical analyses showed that human activities mainly contributed to heavy metal contamination. Spatial distribution confirmed this by showing that areas with the highest metal concentrations occurred where there were high levels of industrial activity and traffic. Potential ecological risk assessment results showed that high risk zones were highly correlated with spatial analysis. The study estimated that in 2007, 85.2?% of the district could be categorized as high risk, which is 77.4 times more than that in 2003.     

济南市土壤重金属污染现状及其土壤生物学表征

以济南市区及郊区农田土壤为对象,研究土壤中重金属污染的特征,结果表明,土壤重金属污染不仅引起了生态环境的恶化,而且影响土壤生物多样性,降低了土壤活性。济南市土壤动物各类群的数量与土壤重金属元素含量的相关性统计结果显示:土壤原生动物数量与Co、Ni含量呈明显负相关;土壤线虫数量与Cu、Mo含量呈显著负相关;旱生土壤动物数量与Cu含量呈显著负相关;说明重金属元素对土壤动物多样性具有不利影响,土壤线虫是耐污种类,旱生动物多为不耐污种类,土壤线虫与旱生动物密度之比可以作为土壤重金属污染程度的生物学指标。通过对土壤地球化学元素含量与土壤生物学参数的相关性分析,找到了重金属的敏感生物指标:Pb污染的生物学指标为土壤线虫;As污染的生物学指标是真菌PLFA含量等,用土壤生物作为敏感、快速的重金属污染生物毒性的指示物,具有广阔的应用前景。     

Effects of humic acid on heavy metal uptake by herbaceous plants in soils simultaneously contaminated by petroleum hydrocarbons

The effects of humic acid (HA) on heavy metal uptake by herbaceous plants in soil simultaneously contaminated with heavy metals and petroleum hydrocarbons were investigated. The results showed that HA reduced readily soluble and exchangeable forms of heavy metals in the contaminated soil but increased their plant-available forms. Potential bioavailability and leachability factors became larger than 1 after adding HA to the soil, except for those of Ni, suggesting that more heavy metals could be potentially phytoavailable for plant uptake. Furthermore, HA increased the accumulation of Pb, Cu, Cd, and Ni in the shoots and roots of selected plants. The greatest increase in the accumulation of heavy metals was 264.7 % in the shoot of Festuca arundinacea, with the bioconcentration factor (BCF) increasing from 0.30 to 1.10. Humic acid also increased the BCFs of the roots of Brassica campestris for Ni and Pb. These results suggest that HA amendment could enhance plant uptake of heavy metals, while concurrently reducing heavy metal leachability and preventing subsurface contamination, even in soils simultaneously contaminated with petroleum hydrocarbons.     

Chelate enhanced phytoremediation of soil containing a mixed contaminant

Greenhouse tests were conducted to study the effect of chelates on the phytoextraction of cadmium and lead, and the rhizodegradation of used engine oil present as a mixed contaminant in a sandy soil. Indian mustard plants were grown in test pot soil for 30 days and chelates ethylenediamine tetraacetic acid (EDTA) and ethylenediaminedisuccinic acid (EDDS) were individually applied to the test soil. The soil was spiked earlier with 50 mg kg^?1 of CdCl₂, 500 mg kg^?1 of PbCl₂ and 500 mg kg^?1 of used engine oil to form the mixed soil contaminant. At the same concentration of chelates, EDTA was found to be more effective than EDDS in increasing the concentration of metal contaminants Cd and Pb in the plant. Compared to EDDS, EDTA was also more effective in promoting rhizodegradation of the organic contaminant formed by used engine oil. The study demonstrated that the application of chelates to soils containing mixed contaminants such as heavy metals (Cd and Pb) and organics (used engine oil) can simultaneously assist metal accumulation at higher concentrations in the biomass of Indian mustard plant and also reduce the amount of used engine oil in the soil through rhizodegradation.     

Lead contamination of soil along road and its remediation

With a rapid development of road systems and an associated drastic increase in number of automobiles, the traffic has induced more and more obvious environmental pollution such as noise, dust, emission and heavy metal contamination. Lead, as one of the most harmful heavy metal contaminants, can execute a significant impact on soil quality and plant growth, depending on its form, as well as its transport and accumulation in soil. This paper describes the source and characteristics of Pb contaminant in soil along a road, and reviews the results of research on remediation of Pb-contaminated soils, aiming at identifying promising approaches to soil remediation along roads.     

不同超富集、富集植物-玉米间作模式对玉米中镉吸收、转运的影响研究

为了研究Cd污染条件下,玉米分别与苋菜、黑麦草、龙葵间作对重金属Cd吸收和转运的特点,从而选择适宜与玉米间作的富集植物,同时达到修复重金属Cd污染土壤的目的。该文以镉(Cd)污染的河南棕壤黏土为供试土壤,通过盆栽试验,基于玉米各器官中Cd含量、富集系数、转运系数、土壤有效态Cd含量的变化,研究了间作苋菜、黑麦草、龙葵对玉米各器官Cd的积累特性的影响及其迁移转运机制。结果表明：(1)龙葵、苋菜、黑麦草间作使得玉米地上部Cd含量显著性降低(P<0.05),其中以籽粒中Cd含量的下降最为显著。间作苋菜、黑麦草、龙葵,玉米籽粒中Cd含量分别下降了67.6%、75.7%和79.9%。(2)间作苋菜、黑麦草、龙葵使得玉米的富集系数较单作处理下玉米的富集系数分别下降了49.3%、39.7%和68.5%,且差异达到显著水平。(3)与苋菜、黑麦草间作相比,间作龙葵的玉米转运系数分别下降了27.5%、24.2%,且差异均达到显著水平。通过对人体每天摄入Cd量的安全值计算得出间作后土壤中Cd全量应低于2.26 mg·kg-1,土壤有效态Cd含量低于0.88 mg·kg-1。该污染农田在间作模式下,食用玉米Cd暴露对居民健康不存在风险。间作苋菜、黑麦草、龙葵能够抑制玉米对Cd的吸收,同时阻控玉米地上部Cd向地上部的转移,尤其是向籽粒转移。通过间作苋菜、黑麦草、龙葵,不仅降低了主栽作物玉米的Cd累积量,实现玉米安全、优质种植,同时也达到了修复污染土壤的目的。     

Evaluation of fertility indicators associated with arsenic-contaminated paddy fields soil

Emerging environmental issues related to heavy metal contamination in rice draw great concern about the soil quality of paddy farming lands irrigated with groundwater. Investigating the functioning of soil microorganisms exposed to heavy metal contamination is imperative for agricultural soil manipulations. The current study accentuates the influence of heavy metals on microbial activity and community composition in arable soil of West Bengal State of India. The result revealed that the fertility indicators (activity of all soil enzymes) and growth-limiting factors (soil N and P) were negatively correlated with the heavy metal stress except the soil total organic content which demonstrated significant positive correlation with the heavy metals. In case of functional diversity of soil, all the considered diversity indices exhibited no specific pattern along with the availability of heavy metals. Further, despite the heavy metal contamination, we observed a very complex and indifferent pattern of bacterial community composition along the heavy metal contamination sites. Overall, we found that γ-Proteobacteria had been the most abundant bacterial community followed by Actinobacteria, Firmicutes, β-Proteobacteria and α-Proteobacteria. Commemorating all the results, we can infer that arsenic and other heavy metal contamination is deteriorating the soil quality and hence warrants immediate attention of concerned soil scientist and agronomists.     

福建沿海地区土壤-稻谷重金属含量关系与影响因素研究

福建沿海地区土壤Pb含量远高于我国其他地区及全国背景值,其对农产品安全、生态环境的影响值得关注。本文采集该地区典型耕作区58套土壤-水稻样品,查明Pb、Cd等重金属元素含量特征及其关键控制因素。研究表明从水稻根→茎叶→稻谷,重金属元素含量和富集系数呈现明显的下降趋势,有害重金属As、Pb等的递减速率远大于植物营养元素Cu、Zn,指示水稻根部对重金属元素具有一定的阻截作用。土壤-稻谷间Pb具有显著正相关性,显示土壤Pb是稻谷Pb的重要来源;稻谷Pb含量与土壤有机碳呈显著负相关关系,与土壤pH呈弱负相关关系,说明富含有机碳、相对碱性的土壤环境可降低土壤Pb的生物有效性,减少稻谷对土壤Pb的吸收富集。土壤理化条件对稻谷Cd富集系数有显著影响,富含有机碳、Al₂O₃、Fe₂O₃、CaO、MgO、S的土壤条件有利于阻断稻谷对土壤Cd的吸收,降低土壤Cd污染的生态风险。本项研究为开展水田土壤重金属污染治理修复、预测稻谷食用安全提供了重要的依据。     

Investigation of potential accumulation and spatial distribution of heavy metals in topsoil surrounding the cement plant of Meftah (southeastern Algiers region,Algeria)

Cement’s dust particles contamination on soil has received a good amount of attention due to toxicity persistence in the environment. It must be noted that cement dust falls are enriched in toxic heavy metals, which can spread throughout a large area by wind and rain then accumulate on plants, animals, and soils, thus ultimately affecting human health. For this purpose, a study was achieved to evaluate the potential accumulation and spatial distribution of heavy metals in topsoils surrounding the Meftah cement factory, situated at the southeastern of Algiers region. Sixty six soil samples were collected following six directions (east, northeast, north, northwest, west, and southwest) from cement factory on a radius of 3.5 km approximately. The physicochemical parameters, such as the pH, the conductivity, and the organic matter of these samples were determined. The concentration of the Cd, Cu, Pb, and Zn elements, in soil samples, were determined with flame atomic absorption spectrophotometry (FAAS) method and the data generated were analyzed statistically. Thus, the enrichment factor (EF), pollution index (PI), contamination factor (CF), pollution load index (PLI), geoaccumulation index (Igeo), and principal component analysis (PCA) was performed to the dataset in order to calculate and estimate the enrichment of metal concentrations in soils. Moreover, mapping of the spatial distribution of heavy metals was carried out using geographic information system (GIS), to determine more polluted areas and accomplish the objectives of the study. The results of our analysis indicate that soils were polluted most significantly by metals such as lead, zinc, copper, and cadmium. It is thus important to keep systematic and continuous monitoring of the bag filter to reduce the cement dust emission. As possible, remediation activities be carried out on the soil of heavy metals and their derivatives to manage and suppress such pollution.     

基于可见—近红外反射光谱的典型农田重金属污染风险分类研究

对于人为因素或自然因素造成的农田土壤重金属元素污染,需要进行大面积的土壤环境质量调查和分类管控,然而传统的采样测试方法存在工作量大、代价高等问题。可见—近红外（Vis-NIR）反射光谱是一种快速低成本获取土壤理化信息的手段。为研究Vis-NIR反射光谱预测模型划分土壤重金属污染风险类别的能力,文章以典型人为污染地区（浙江温岭）和典型地质高背景地区（广西横县）的390份农田土壤为样本,测定8种重金属元素（As、Cd、Cr、Cu、Hg、Ni、Pb和Zn）的含量和pH值,并测定土壤Vis-NIR光谱。使用偏最小二乘（PLS）和支持向量机（SVM）算法建立回归模型,对土壤重金属含量和pH值进行预测,并基于预测值进行土壤重金属污染风险分类。结果显示,温岭土壤主要污染元素Cd和Cu的光谱模型回归预测偏差（RPD）分别为1.23和1.19,预测机制与有机质有关。横县土壤主要污染元素As和Cd的RPD分别为1.98和1.93,预测机制与铁氧化物和粘土矿物有关。地质高背景土壤重金属与铁氧化物的正相关性普遍较强,使得光谱模型对重金属含量预测准确度较高。温岭和横县土壤pH值的光谱模型RPD分别为1.76和1.68。土壤重金属污染风险光谱分类的总体 准确度分别为75.0%~100%（温岭）和80.0%~100％（横县）。将Vis-NIR光谱与遥感技术相结合,对农田土壤重金属污染风险进行快速分类总体是可行的。     

磁化率对土壤重金属污染的指示性研究——以沈阳新城子区为例

通过对399件表层土壤磁化率参数与化学组成的分析测试,较系统地总结了沈阳新城子区土壤磁化率特征,并初步进行了磁化率对土壤重金属污染的指示研究。结果表明:(1)不同土壤类型中磁化率差异较大,棕壤中由于人为作用较大,其均值最高。不同堆积类型中磁化率差别较大,洪积物和残坡积物中平均值最高,冲积物中最低。不同农作物对元素的需求不一样导致磁化率的含量变化范围存在着区别。(2)土壤的磁化率与土壤中Cd、Pb、Hg、Cu、Zn等重金属元素含量呈显著正相关,且与土壤pH值呈显著负相关关系,能反映出土壤酸化的状况,对土壤污染程度有较好的指示性。(3)利用磁化率可以快捷地划分污染区。     

烟台市土壤环境质量现状及重金属元素分布迁移规律

烟台市是山东半岛蓝色经济区核心城市之一。通过对山东省烟台市生态地球化学资料的系统整理,发现土壤主要污染因子是Cd、As、Hg、Cu、Pb、Zn等重金属元素,工矿三废排放是土壤重金属的主要来源;过量施用化肥和工矿污染形成的酸雨使区内土壤明显酸化,土壤根系土中镉等元素在酸性环境中活化迁移能力明显增强,有毒重金属镉等通过土壤-水-植物活化迁移量大,经食物链向人体中转移危险性增大。土壤重金属污染和土壤酸化成为烟台市域内两项重大的生态环境问题,为土地污染防治提供了科学依据。     

丛枝菌根影响土壤-植物系统中重金属迁移转化和累积过程的机制及其生态应用

丛枝菌根真菌(AMF)是在自然和农业生态系统中广泛存在的一类专性共生土壤微生物,能够与80%左右的陆地植物建立共生关系。AMF从宿主植物获取碳水化合物以维系自身生长;作为回报,AMF能够帮助植物从土壤中吸收矿质养分和水分。很多研究表明,AM共生体系对于植物适应各种逆境胁迫(如贫瘠、干旱、环境污染等)具有重要作用。在土壤重金属污染情况下,AMF能够通过多种途径影响植物对重金属的吸收、累积和解毒过程,并对植物产生保护效应。本文围绕AM对土壤-植物系统中重金属迁移、转化和累积过程的影响机制,系统评述了金属元素种类及污染程度、宿主植物和AMF种类,以及土壤理化性质等因素对AM植物吸收累积重金属的影响,并从AMF对土壤-植物系统中重金属行为的直接作用(包括菌丝吸收和固持,以及改变根际重金属形态等),及AMF改善植物矿质营养促进植物生长从而间接增强植物重金属耐性两方面讨论了AM增强植物重金属耐性的机理,系统总结了相关研究领域的前沿动态。最后,对菌根技术在农田和矿区重金属污染土壤生物修复中的应用前景进行了展望。     

Comparative analysis of heavy metal concentration in secondary treated wastewater irrigated soils cultivated by different crops

The use of treated urban wastewater for irrigation is a relatively recent innovation in Botswana and knowledge is still limited on its impact on soil heavy metal levels. The aim of this study is to analyze and compare heavy metal concentration in secondary wastewater irrigated soils being cultivated to different crops: olive, maize, spinach and tomato in the Glen Valley near Gaborone City, Botswana. The studied crop plots have been cultivated continuously under treated wastewater irrigation for at least 3 years. Most crop farms have sandy loam, loamy sand soils. Based on food and agriculture organization, heavy metal threshold values for crop production have been studied. Results showed that the wastewater irrigated soils in the Glen Valley have higher cadmium, nickel and copper than desirable levels, while the levels of mercury, lead and zinc are lower than the maximum threshold values recommended for crop production. The control sites show that the soils are naturally high in some of these heavy metals (e.g copper, zinc, nickel) and that crop cultivation under wastewater irrigation has actually lowered the heavy metal content. Comparing between the crops, mercury and cadmium levels are highest in soils under maize and decline linearly from maize to spinach to olive to tomato and control site. By contrast, concentrations of the other metals are at their lowest in maize and then increase from maize to spinach to olive to tomato and to control site.     

砷、镉复合污染土击实特性及微观结构试验研究

重金属污染土不仅破坏环境健康,同时威胁岩土工程安全。通过控制变量法对砷（As）、镉（Cd）单一污染土和复合污染土的土壤化学、土体微观结构和击实特性对比分析,研究了不同重金属污染源、不同重金属浓度对污染土的击实特性影响规律及作用机制。结果表明：单一污染土中,As使土壤扩散双电层变厚,土颗粒呈絮凝状,小孔隙增加,小颗粒含量先增后减,最优含水率升高5.90%,最大干密度降低1.02%;Cd的作用效应截然相反,Cd压缩土壤扩散双电层,土体呈堆积状,小孔隙减少,小颗粒含量减少,最优含水率降低8.03%,最大干密度增加1.00%。Cd对土体击实特性影响大于As。复合污染土中,As、Cd对土体最优含水率的影响呈协同作用,而对最大干密度无明显相互作用关系。污染土宏微观联系桥梁可以通过分形维数与最大干密度建立,二者拟合结果为二次函数关系。研究成果可为重金属污染土环境与工程灾害防控提供关键参数和理论支撑。