水口山水稻土与菜地土中砷的有效性

对湖南省水口山矿冶周边土壤进行采样分析,以土壤砷总量与有效态砷含量以及土壤基本理化性质(pH、有机质含量、土壤粘粒含量)为参数,研究各参数在两种土地利用类型(菜地土和水稻土)间的差异以及有效态砷与土壤理化性质之间的关系。结果表明,水口山水稻土与菜地土平均砷含量分别达72.01和30.71mg.kg-1,接近或已超过国家土壤环境质量二级标准;两种土地利用类型的土壤基本理化性质差异显著,水稻土粘粒含量、有机质含量显著高于菜地土,pH则显著低于菜地土,水稻土存在明显的酸化现象;不同土地利用类型显著影响土壤有效砷含量,尽管菜地土土壤砷总量大大低于水稻土,两者的有效态砷含量水平却基本相当;除总砷外,水稻土有效砷含量还与土壤有机质含量显著正相关,菜地土有效砷含量与土壤pH值显著正相关。水口山菜地土砷污染的危害程度高于水稻土,应采取必要的修复措施或调整土地利用方式以降低砷的健康风险。     

络合型含铁材料对砷胁迫下水稻生理生化特性及砷累积的影响

土壤重金属与农产品质量息息相关.本研究通过设置砷胁迫条件下水稻种植盆栽试验,分析络合型含铁材料不同施用时期和不同施用量对水稻SPAD值、抗氧化酶(SOD、POD、CAT)活性以及水稻砷吸收、累积的影响.结果表明,砷胁迫对水稻SOD、POD、CAT活性有着不同程度的抑制作用,添加络合型含铁材料可以降低水稻MDA含量,缓解砷对水稻光合作用和SOD、POD、CAT活性的抑制;同时能减少水稻对土壤砷的吸收和累积.与移栽前添加络合型含铁材料相比,选择水稻孕穗期前添加络合型含铁材料,水稻砷吸收的抑制效果较好;水稻植株地上部砷含量与络合型含铁材料的添加浓度呈显著负相关,孕穗期前添加0.2 g·kg-1络合型含铁材料对水稻植株砷的吸收抑制效果最好,水稻植株地上部砷含量降低59.22%.     

土壤溶液中的砷及其与水稻生长效应的关系

通过盆栽试验和土壤中砷的吸附试验,探讨了砷在土壤溶液中的氧化－还原行为和溶解行为,并初步揭示了不同价态砷对水稻毒性差异的机理,以及土壤ｐＨ对砷的吸附作用和毒害作用的影响。     

淹水-控温模式下砷污染水稻土溶液中砷形态的变化

以水稻种植区的砷污染土壤为研究对象,采用高效液相色谱(HPLC)-电感耦合等离子体质谱(ICP-MS)联用分析测试系统,研究了不同培养温度(5、27和50 ℃)对灭菌和不灭菌的土壤淹水后其溶液中砷赋存形态变化的影响.结果表明： 在土壤溶液中检测到的砷形态只有无机三价砷(As^Ⅲ)、无机五价砷(As^V)和有机的二甲基砷(DMA^V),未检测到单甲基砷(MMA^V)的存在;在不同控温条件下随淹水时间的延长,As^Ⅲ逐渐转变为砷的主要赋存形态,平均比例约为64%;As^V次之,约占35%,DMA^V的含量相对最低,约占1%;土壤灭菌与否对土壤溶液中五价砷的水平没有明显影响,但明显影响了五价砷的还原和促进了无机三价砷的甲基化,并且灭菌的促进效果随着淹水及培养时间的延长而逐渐降低;50 ℃、淹水23 d时,灭菌土壤溶液中DMA^V浓度最高,为23.7 ng·mL^-1,这说明灭菌土壤中残留的某些嗜热微生物成为优势菌群并促进了土壤溶液中砷的甲基化.结合水稻生长的实际环境条件对该研究结果进行分析,培养温度27 ℃淹水23 d后不灭菌的自然土壤溶液中砷浓度处于较低水平,因此在砷污染的水稻种植区建议采用短周期干湿交替的水分管理模式,在保障产量的情况下可尽量降低土壤溶液中砷的水平.     

淹水-控温模式下砷污染水稻土溶液中砷形态的变化

以水稻种植区的砷污染土壤为研究对象,采用高效液相色谱(HPLC)-电感耦合等离子体质谱(ICP-MS)联用分析测试系统,研究了不同培养温度(5、27和50℃)对灭菌和不灭菌的土壤淹水后其溶液中砷赋存形态变化的影响.结果表明:在土壤溶液中检测到的砷形态只有无机三价砷(AsⅢ)、无机五价砷(Asv)和有机的二甲基砷(DMAv),未检测到单甲基砷(MMAv)的存在;在不同控温条件下随淹水时间的延长,AsⅢ逐渐转变为砷的主要赋存形态,平均比例约为64％;Asv次之,约占35％,DMAv的含量相对最低,约占1％;土壤灭菌与否对土壤溶液中五价砷的水平没有明显影响,但明显影响了五价砷的还原和促进了无机三价砷的甲基化,并且灭菌的促进效果随着淹水及培养时间的延长而逐渐降低;50℃、淹水23 d时,灭菌土壤溶液中DMAv浓度最高,为23.7 ng·mL-1,这说明灭菌土壤中残留的某些嗜热微生物成为优势菌群并促进了土壤溶液中砷的甲基化.结合水稻生长的实际环境条件对该研究结果进行分析,培养温度27℃淹水23 d后不灭菌的自然土壤溶液中砷浓度处于较低水平,因此在砷污染的水稻种植区建议采用短周期干湿交替的水分管理模式,在保障产量的情况下可尽量降低土壤溶液中砷的水平.     

砷对农田生态系统污染效应的试验研究

本文通过盆栽及模拟试验,研究了砷对农田生态系统中农作物、土壤微生物、土壤动物的污染效应。结果表明,砷对农作物生长发育有明显不良影响,浓度过高,产量下降并造成农作物体内砷的残留累积;不同种类农作物对砷的敏感程度不同,以对水稻的危害最严重,其次为春小麦、玉米;不同形态砷化物的污染效应有显著差别,亚砷酸盐的毒性最强,砷酸盐次之,硫化砷的影响最小。 砷对土壤微生物具有明显抑制作用,使土壤细菌总数降低,投加亚砷酸钠5ppm,砷酸氢二钠10ppm时,细菌总数开始减少。对土壤固氮菌、解磷细菌、纤维分解细菌等土壤有益微生物有明显抑制作用,使存活率下降。砷污染土壤活性降低,土壤呼吸强度下降。 砷污染影响土壤中蚯蚓的数量与分布,当砷在100—300ppm时,可使蚯蚓致死,死亡率达50—80％。砷在蚯蚓体内明显富集,富集系数为1.32—7.44。     

污水灌溉中砷对作物的影响

用低浓度(1毫克/升以下)含砷污水灌溉农田,作物生长发育正常,作物和土壤中含砷量与清水灌溉的相似。当砷的灌溉浓度为5、20毫克/升时,可使小麦、水稻产量下降。浓度5毫克/升的砷溶液,使水稻体内含砷量显著增高。该浓度可作为作物的危害浓度。土壤中加入一定量的 Feso_4,有降低水稻对砷的吸收作用。     

土壤砷植物暴露途径的土壤因子模拟

确定土壤中重金属生物有效性是评价土壤重金属污染生态风险的关键,然而在生态风险评价实际应用中,测定土壤重金属生物有效性耗时且高成本,限制了生物有效性评价法的应用。通过对模式植物的文献搜集,总结了影响植物富集土壤砷的7个土壤因子,揭示了土壤砷植物暴露的影响机制。运用SPSS 18.0对文献数据集各个土壤因子进行了回归分析、相关性分析和共线性分析。单因子回归分析表明营养盐类对植物富集砷影响很小,可以忽略不计;相关性分析和共线性分析结果表明土壤因子之间存在多元共线性;主成分分析结果表明,植物富集砷浓度主要受土壤质地的物理综合指标以及土壤总砷含量和土壤酸碱度等化学综合指标影响。其中植物富集浓度受土壤中总砷浓度影响最大,受土壤质地中砂粒含量影响其次;土壤粉粒、粘粒、有机质含量和阳离子交换量对富集也有一定影响;而土壤酸碱度对植物富集浓度的影响相对较小。最终通过数学模型解释植物富集砷浓度随土壤性质变化的规律,建立了土壤性质与土壤砷植物暴露的相关关系,为土壤重金属生物有效性风险评价法提供理论依据。     

接种AM真菌和施加铁可协同降低水稻砷累积

采用外源添加砷(As)的土培模拟试验探究了接种丛枝菌根真菌(AMF)异形根孢囊霉Rhizophagus irregularis和外源添加铁(Fe)对水稻Oryza sativa根表铁膜形成以及水稻累积砷的影响。结果表明,根表铁膜能够吸附大量的磷和砷。添加砷促进了根表铁膜的形成,而接种AMF后铁膜厚度显著降低。接种AMF改善了植物的磷营养状况,显著提高了水稻根系砷浓度,但降低了地上部砷浓度;砷污染情况下施加铁显著降低了接种处理水稻地上部的砷浓度。接种AMF+施加铁处理降低水稻地上部砷浓度的效果最大。这表明AMF+施加铁可协同抑制水稻地上部砷积累。该研究结果为在高砷背景值土壤中种植粮食作物并保障食品安全提供了一条可供选择的技术途径。     

有机胂饲料添加剂对猪场周围及农田环境污染的调查研究

对广东省长期使用阿散酸为饲料添加剂的15个大型猪场的周围环境及农田进行了调查,结果表明：猪场内长期施用猪粪为肥料的甘薯根内的总砷含量已为国家规定最高检出限（0．5mg／kg）的3—6倍;甘薯地土壤的砷含量介于25．83～55．54mg／kg,远远大于自然界最高砷含量的背景值（15mg／kg）;而且甘薯的各种组织的总砷含量与土壤砷含量成正比。绝大多数猪场鱼塘水的砷含量已超过渔业水质标准0．05mg／L;虽然鱼肌肉的总砷含量未超过国家规定标准0．5mg／kg,但是在鱼的可食性组织脂肪、脑的总砷含量却远远超标,约为肌肉组织中3-4倍。猪场排污口附近的土壤,砷污染范围介于200—500m之间;其中在距排污口约5m,50m的土壤,砷的含量远超过自然界的砷含量的最高背景值15mg／kg。长期施用猪粪作为肥料的稻田,大多数土壤砷含量已超过国家规定的最高标准;另外,水稻有一定的砷富集能力,而且水稻各种组织的砷含量与土壤的砷含量也存在明显的正相关。     

土壤重金属污染的酶学诊断:紫色土Cd、Cu、Pb和As对水稻根系脱氢酶的影响

本文通过酸性紫色土和石灰性紫色土中不同浓度Cd、Cu、Pb、As对水稻根系脱氢酶的影响研究,揭示了脱氢酶受抑制与产生抗性的过程。在低浓度时,土壤Cd、Cu、Pb、As对脱氢酶的影响较敏感,能因元素的不同性质反映土壤类型影响的差别。最后,以脱氢酶受抑制与初始抗性峰出现的转折点相应的土壤浓度为依据,确定了两种紫色土Cd、Cu、Pb、As的临界浓度。     

水稻－土壤生态系统对Cu、As污染的缓冲作用

通过对冶炼厂区周围水系、土壤和水稻中Ｃｕ、ＡＳ含量分析,探讨其对农田生态环境的影响．结果表明,各稻田耕作层渗出水和相邻塘水中的Ｃｕ平均浓度分别为０．０５９和０．０７ｂｍｇ·Ｌ（－１）,Ａｓ为３１．６８和４２．７９μｇ·Ｌ（－１）,稻田土壤中未出现Ｃｕ、Ａｓ明显的梯度累积变化以及水稻能吸收累积相当数量的Ｃｕ、Ａｓ,它们大部分累积在根部．可以认为,水稻一土壤生态系统本身对Ｃｕ、ＡＳ污染具有相当大的缓冲作用．     

改性措施对复合污染土壤重金属行为影响的研究

采用田间实验的方法,研究了在复合污染土壤上石灰＋Ｃａ、Ｍｇ、Ｐ肥处理对重金属迁移、积累的影响及重金属的作物效应．结果表明,在污染土壤上采用石灰＋Ｃａ、Ｍｇ、Ｐ肥处理可减少重金属向作物籽实的迁移和积累,特别是Ｃｄ、Ｐｈ、Ａｓ３元素;改性以后,水稻、小麦Ｃｄ吸收量比改性前降低了３１．５—５５％．４种作物对Ｐｈ的吸收量降低了２３．４－５７．８％,Ｃｕ、Ｚｎ吸收量略有降低．水稻Ａｓ吸收量增加了５６．８％,小麦、大豆Ａｓ吸收量减少６１．８－８１．１％．重金属在土壤中存在的形态发生了变化,Ｃｄ、Ｐｈ、Ｚｎ交换态百分含量不同程度地有所减少,而碳酸盐结合态有所增加,可被植物吸收利用的有效含量降低．     

长期施用猪粪红壤稻田土壤Cu、Zn累积规律

为揭示长期施用猪粪红壤稻田土壤Cu、Zn累积规律,以设立于1981年的红壤稻田有机肥定位试验为载体,选取PM1(早稻施猪粪和紫云英)、PM2(早稻施紫云英+晚稻施猪粪)、GMS(早稻施紫云英+晚稻秸秆还田)和NPK(早稻施化肥)等处理为对象,分析了不同试验年限土壤全量和有效态Cu、Zn含量。结果表明:长期施用猪粪显著提高了土壤Cu、Zn含量;连续施用猪粪30 a后,土壤全量Cu、Zn含量分别增加了7.69—9.52 mg/kg和22.42—35.46 mg/kg;生物有效性显著增加,有效态Cu、Zn含量占全量Cu、Zn的比例分别由15%和5%增加到51%和27%。猪粪年度内的施用时间对土壤Cu的累积没有显著影响,早稻施用猪粪加剧了土壤Zn的累积。土壤铜、锌累积分为两个差异显著的阶段,1981—2002年为缓慢增长期,2002—2010年为快速增长期,这可能与2002年后施用的猪粪中Cu、Zn含量增高有关。以研究的结果推算,红壤稻田鲜猪粪施用量在9.5 t hm-2a-1以下,50 a内不会造成土壤Cu、Zn含量超标。     

Cadmium,copper, and zinc levels in the rice and rice field soil of Houston,Texas

Fifty-one pairs of hulled rice samples and the soil from which each rice sample was grown were analyzed for heavy metals in August, 1979, in order to estimate the background contamination of cadmium (Cd), copper (Cu), and zinc (Zn) in rice grown in the Houston, Texas area. Both samples were divided into three groups by soil types and colors. The cadmium concentration in Texas rice was only one-half to one-quarter lower than that of Asian rice. However, the levels of Cu and Zn in rice in Texas were similar to those reported. Soil heavy metals were lower than ever reported, but these values were consistent with the geochemical characteristics of the Texas Houston area. No particular relationship was found between the three metals in rice and the metals in soil where the sampled rice was grown.     

Changes in water and soil metals in a Mediterranean restored marsh subject to different water management schemes

Marsh restoration is an effective tool to remove water and soil metals via plant uptake and soil accumulation. However, few studies have attempted to quantify metal accumulation and removal in Mediterranean restored marshes. This study aimed to assess changes in water and soil metals in an oligohaline‐restored marsh experiment that was set in an abandoned rice field for 3 years. Two freshwater‐type treatments were tested: river irrigation water (IW) and rice field drainage water (DW), as well as three water level management schemes. Differences in water level schemes did not cause significant differences in metal removal and accumulation in soil marshes in either water type treatment. However, results showed that significantly higher Mn, Pb, and Zn input concentrations from DW allowed higher mean percentage of concentration reduction. Higher Cu concentration from IW also allowed higher Cu reduction (85%). Mean values of Co, Cr, Cu, Ni, Pb, V, and Zn in soil were higher in the IW treatment characterized by higher plant biomass, whereas mean accumulation rates of As, Ba, Cr, Cu, Ni, Pb, V, and Zn were higher in the DW treatment with higher accretion rates. Results suggest that wetland plants likely favored soil metal adsorption through soil oxygenation and highlight the utility of restored marshes as pollution filters in coastal wetlands with significant soil accretion and subject to relative sea level rise.     

Micronutrient availability to cereals from calcareous soils

Summary On several alkaline calcareous soils, Zn and Cu deficiency occurred mainly in lowland rice (Oryza sativa L.) and was rarely found in wheat (Triticum aestivum L.). Zinc and Cu requirement of plants was not responsible as the critical Zn and Cu contents in tops of the two plant species were almost similar i.e. 17.4, 6.5 and 14.5, 5.6 ppm respectively. Neither did rice absorb Zn and Cu less efficiently. On the contrary, their rates of absorption in rice were double than in wheat. They were 22.2, 6.3 and 10.2, 3.3 ng atoms/g fresh root/h respectively in the two plant species. Flooded soil conditions appeared to be responsible for Zn and Cu deficiency in rice as their deficiency was found mainly in plant samples collected from continuously flooded fields. The mechanism is not known.Both Zn and Cu inhibited uptake of each other in wheat on most of the soils. In rice, only applied Zn depressed Cu uptake but Cu had generally little effect on Zn uptake. Little Cu inhibition of Zn uptake in lowland rice seems to be related to flooded soil conditions. The mechanism is yet to be known. The antagonising element accentuated the deficiency of the other element both in wheat and rice and severely reduced their yields on soils marginal to deficient in Zn or Cu supplies. It is recommended that their soil availability status should be thoroughly considered before their fertilizers are applied. re]19750515     

Effects of Cadmium and Mixed Heavy Metals on Rice Growth in Liaoning,China

Joint effects of Cd and other heavy metals (Pb, Cu, Zn and As) on the growth and development of rice plants and the uptake of these heavy metals by rice were studied using the pot-culture method combined with chemical and statistical analyses. The results showed that the growth and development of rice plants were strongly influenced by the double-element combined pollution. There was an average decrease in the height of rice plants of 4.0–5.0 cm, and grain yield was decreased by 20.0–30.0%, compared with the control. The uptake of Cd by rice plants was promoted due to the interactions between Cd and the other heavy metals added to the soil. The Cd concentration in roots, stems/leaves and seeds increased 31.6–47.7, 16.7–61.5 and 19.6–78.6%, respectively. Due to interactions, uptake of Pb, Cu and Zn by roots and stems/leaves was inhibited, accumulation of Pb, Cu and Zn in seeds was increased, uptake of As by roots was promoted and uptake of As by stems/leaves was inhibited. In particular, the upward transporting ability of the heavy metals absorbed by rice plants was significantly increased.     

碳酸钙对水稻吸收重金属(Pb、Cd、Zn)和As的影响

选用重金属(Pb、Cd、Zn)和As复合污染土壤进行水稻盆栽试验,结果表明,碳酸钙的添加显著提高了土壤pH值,显著降低了土壤中交换态Pb、Cd、Zn和As的含量,与对照相比,交换态Pb、Cd、Zn和As含量分别最多降低了98.35%,93.72%,98.52%和69.48%。碳酸钙对水稻根、稻谷干重和总生物量没有显著影响,添加量过高时显著降低了水稻分蘖数和茎叶干重,说明过量施用碳酸钙对水稻生长会产生负面作用。因为碳酸钙的添加,水稻植株各部位重金属Zn含量显著降低,糙米中Zn含量最多减少了34.95%;根、谷壳中Pb、Cd含量显著降低,但糙米中含量却未显著降低;水稻各部位As含量均没有显著降低。参照《食品中污染物限量》(GB2762—2012),试验糙米中Pb、Cd、无机As含量均未达到限量标准。显然,碳酸钙的添加降低了Pb、Cd、Zn的生物有效性(水稻根系对Pb、Cd、Zn的吸收累积减少),但并未有效地抑制Pb、Cd向糙米转运;碳酸钙显著降低了土壤的交换态As含量,但并未使土壤中As的生物有效性明显降低(水稻植株各部位的As含量并未显著减少)。     

Mechanisms Controlling Arsenic Uptake in Rice Grown in Mining Impacted Regions in South China

Foods produced on soils impacted by Pb-Zn mining activities are a potential health risk due to plant uptake of the arsenic (As) associated with such mining. A field survey was undertaken in two Pb-Zn mining-impacted paddy fields in Guangdong Province, China to assess As accumulation and translocation, as well as other factors influencing As in twelve commonly grown rice cultivars. The results showed that grain As concentrations in all the surveyed rice failed national food standards, irrespective of As speciation. Among the 12 rice cultivars, “SY-89” and “DY-162” had the least As in rice grain. No significant difference for As concentration in grain was observed between the rice grown in the two areas that differed significantly for soil As levels, suggesting that the amount of As contamination in the soil is not necessarily the overriding factor controlling the As content in the rice grain. The iron and manganese plaque on the root surface curtailed As accumulation in rice roots. Based on our results, the accumulation of As within rice plants was strongly associated with such soil properties such as silicon, phosphorus, organic matter, pH, and clay content. Understanding the factors and mechanisms controlling As uptake is important to develop mitigation measures that can reduce the amount of As accumulated in rice grains produced on contaminated soils.