植被恢复对退化红壤表层土壤颗粒中有机碳和Pb、Cd分布的影响

采用原状土壤水稳性团聚体分离方法提取不同粒径的土壤颗粒,测定其有机碳及重金属元素Pb、Cd的含量,研究了退化红壤在植被恢复下表层(0～10cm和10～20cm)土壤颗粒中有机碳与重金属分布及其关系.这些土壤颗粒中有机碳和重金属元素Pb、Cd的含量范围分别介于7.5～15g/kg,11～20mg/kg和20～70μg/kg,且粒组间有显著差异.尽管所测组分的含量以＜0.002mm粒组中最高,但2～0.25mm的粒组占其总量的50%左右,其次约20%存在于0.25～0.02mm粒组中.以土壤粒组中分量而言,有机碳和所测的重金属元素间有密切的依存关系.与荒地相比,植被恢复措施降低了各土层2～0.25mm粒组中Pb的含量和分量,但提高了0～10cm土层Cd的含量和分量.在所研究的几种处理中,玉米-包菜处理显著地促进了有机碳和重金属在各颗粒粒组中的均衡分布.因此,退化红壤植被恢复措施改变了上壤颗粒中有机碳和重金属的分布,因而可能影响着土壤环境中有机碳和重金属的形态及其活性.对于这些措施下土壤环境中有机碳和重金属的生物有效性机制尚需进一步研究.     

植被恢复对退化红壤表层土壤颗粒中有机碳和Pd、Cd分布的影响

采用原状土壤水稳性团聚体分离方法提取不同粒径的土壤颗粒,测定其有机碳及重金属元素Pb、Cd的含量,研究了退化红壤在植被恢复下表层（0-10cm和10－20cm)土壤颗粒中有机碳与重金属分而及其关系。这些土壤颗粒中有机碳和重金属元素Pb、Cd的含量范围分别于7.5-15g/kg,11-20mg/kg和20-70μg/kg,,且粒组间有显著差异。尽管所测组分的含量以＜0.002mm粒事最高,但2－0.25mm的粒组占其总量的50％左右,其次约20％存在于0.25-0.02mm粒组中,以土壤粒组中分量而言,有机碳和所测的重金属元素间有密切的依存关系。与荒地相比,植被恢复措施降低了各土层2－0.25mm粒组中Pb的含量和分量,但提高了0－10cm土层Cd的含量和分量。在所研究的几种处理中,玉米－包菜处理显著地促进了有机碳和重金属在各颗粒粒组中的均衡分布。因此,退化红壤植被恢复改变了土壤颗粒中有机碳和重金属的分布,因而可能影响着土壤环境中有机碳和重金属的形态及其活性。对于这些措施下土壤环境中有机碳和重金属的生物有效性机制尚需进一步研究。     

名山河流域水稻土组分对微团聚体吸附-解吸锌的影响

通过模拟-培养试验和选择溶解法,研究了四川省名山河流域水稻土各土壤组分对原土和不同粒径微团聚体吸附解吸Zn2+能力的影响.结果表明:原土和不同粒径微团聚体对Zn2+的吸附与有机质、游离氧化铁、无定形氧化铁、阳离子交换量(CEC)含量极显著相关,原土去除各土壤组分前后对Zn2+的吸附均用Freundlich方程拟合最佳,对Zn2+的吸附能力大小顺序为:小于0.002mm0.25～2mm原土0.002～0.053mm0.053～0.25mm.与未去除土壤组分相比,去除土壤组分的原土和微团聚体对Zn2+的吸附量均有一定程度的减小,吸附量的减小以0.002mm粒径最高,0.25～0.053mm粒径最低,原土介于各微团聚体中间.去除有机质后,0.002mm、0.053～0.25mm和原土吸附Zn2+的减少量依次为39.56%±1.97%、26.68%±4.21%和36.39%±2.31%;去除游离氧化铁后,吸附Zn2+的减少量依次为30.41%±1.91%、20.14%±3.33%和28.73%±1.22%;去除无定形氧化铁后,吸附Zn2+的减少量依次为22.12%±1.27%、12.43%±2.11%和20.15%±2.62%.吸附减少量大小顺序为:去除有机质去除游离氧化铁去除无定形氧化铁,不同处理间差异极显著.去除各土壤组分后,原土和各粒径微团聚体对Zn2+的非专性吸附量显著上升,增加了Zn2+在土壤中的流动性;而专性吸附量降低,降低了原土和各粒径微团聚体对Zn2+的缓冲能力和固持能力.     

真菌和细菌生物量在土壤团聚体中的分布和耕作响应

首次报道亚热带紫色水稻土中土壤真菌和细菌生物量在不同粒径水稳性团聚体中的分布及耕作的影响.实验样品采自16 年的国家紫色土长期定位试验站的垄作免耕(Combining Ridge and No-tillage, NT)、冬水稻田(Flooded Paddy Field, FPF)和常规平作(Conventional Tillage, CT)土壤.表层土样(0～20cm)通过湿筛法分别得到>4.76 mm、2.0～4.76 mm、1.0～2.0 mm、0.25～1.0 mm、0.053～0.25 mm、<0.053mm粒径的土壤团聚体.采用麦角固醇和胞壁酸标记法测定各级团聚体中真菌和细菌的生物量.结果显示在垄作免耕、冬水稻田、常规平作土样中,真菌生物量与细菌生物量在<0.053 mm的粘粒中含量最低;在0.053～0.25 mm的土壤微团聚体中最高;在大于0.25 mm的大团聚体中真菌和细菌生物量随粒径的增大而增多,但细菌和真菌生物量在不同耕作方式的土样中的变化模式有一定的差异.3种耕作方式相比较,垄作免耕的土壤真菌和细菌的生物量在3种耕作方式中最高,冬水稻田次之,常规平作最低.真菌生物量与细菌生物量的比率分布模式在不同耕作方式的土样中差异较大,垄作免耕的真菌生物量与细菌生物量的比率在3种耕作方式中最高,冬水稻田次之,常规平作最低,但除了在0.25～1.0 mm、2.0～4.76 mm的团聚体之间有明显差异外(P＜0.05),其余粒径之间均无明显差异(P＞0.05).这表明土壤真菌生物量和细菌生物量在亚热带紫色水稻土水稳定性团聚体中的分布模式与团聚体的粒径和耕作方式有关,3种耕作方式中垄作免耕对真菌和细菌生物量分布的响应最为明显.     

宁南山区植被恢复对土壤团聚体养分特征及微生物特性的影响

测定了宁夏黄土丘陵区植被恢复近30年的天然草地和农地不同粒径团聚体的土壤养分含量、微生物生物量、呼吸特性和生态化学计量比等指标,探索黄土丘陵区植被恢复对不同粒径土壤团聚体的养分特性和微生物学性质的影响.结果表明: 微团聚体(粒径<0.25 mm)质量百分比、各粒径土壤团聚体养分(有机碳、全氮、速效钾)含量、C/N均表现为天然草地大于农地,其中1～2 mm粒径团聚体有机碳、全氮含量在天然草地和农地中均最高,C/N也较高,说明植被恢复能有效促进土壤团粒的形成,适宜养分积累和有机碳的汇集,且在1～2 mm粒径团聚体上表现最为突出;天然草地各粒径土壤团聚体微生物生物量(碳、氮)、基础呼吸强度均高于农地,而呼吸熵低于农地,可见植被恢复措施可有效提高各粒径土壤微生物生物量与活性,并使土壤生境趋于稳定;但由于养分特性的差异,不同粒径团聚体微生物特性对植被修复的响应存在差异,其中天然草地土壤1～2 mm粒径团聚体微生物生物量碳,<0.25、0.25～1、1～2 mm粒径团聚体微生物生物量氮,以及1～2、>5 mm粒径团聚体基础呼吸强度显著高于其他粒径,即上述粒径团聚体的微生物生物量和微生物活性在植被恢复过程中逐渐被改善.表明宁南山区植被恢复有效改善了土壤团聚体的肥力状况与结构特征,且1～2 mm粒径团聚体的改良效果最为突出.     

土壤重金属污染生态过程、效应及修复

本文探讨了重金属在土壤中的行为特性及其生态化学过程作用的特点,不同的重金属元素在土壤胶体颗粒表面的吸附特性及不同元素间的交互作用类型有所不同,自然对重金属迁移积累的影响有所不同。土壤重金属污染影响了种子萌发、幼苗生长、作物产量及体内重金属含量,探讨了污染土壤的酶学评价方法。阐述了重金属污染土壤生物修复的特点,展望了重金属污染生态过程研究的未来发展趋势。     

喀斯特峰丛洼地原生林土壤团聚体有机碳的剖面分布

以喀斯特峰丛洼地的伊桐、侧柏和菜豆树3个原生林植物群落为对象,分析了土壤团聚体的组成、有机碳及其剖面分布.结果表明:3个植物群落的土壤分布均以＞2 mm大粒径团聚体为主,约占土壤团聚体总量的76％.土壤总有机碳含量介于12.73 ～ 68.66 g·kg-1之间,群落类型显著影响土壤有机碳含量及其分布.＜1 mm小粒径团聚体中的有机碳含量比＞2 mm团聚体稍高,但大部分土壤有机碳储存在大粒径团聚体中,＞2 mm团聚体对土壤有机碳的贡献率约70％.2 ～5和5～8 mm团聚体含量与土壤有机碳含量呈显著正相关.提高土壤中2～8 mm团聚体的含量能有效增强喀斯特地区土壤固碳能力.伊桐群落2～8 mm土壤团聚体的含量及其全土有机碳含量分别达46％和37.62 g· kg-1,伊桐更适合作为喀斯特地区生态恢复树种.     

红壤坡面土壤团聚体特性与侵蚀泥沙的相关性

借助室内人工模拟降雨试验为研究手段,以强降雨过程中红壤丘陵区坡菜地侵蚀泥沙颗粒组成及土壤团聚体稳定性变化特征与规律为研究目的,分别在不同坡长(2,3,4m)、不同植被覆盖度(0,30%,60%,90%)条件下进行了有效模拟降雨试验共计12场次,每场次降雨试验的产流历时设计为30min,固定雨强为2.0mm/min。试验结果表明:1)侵蚀泥沙中颗粒粒径以2μm粘粒和2—20μm细粉粒为主。在原土中,粘粒(0—2μm)和细粉粒(2—20μm)含量之和占总量的43.92%,在泥沙中粘粒和细粉粒之和占总量的约57.08%,均出现不同程度的增加;2)在不同处理中,坡面土壤1mm干筛法团聚体含量明显大于湿筛团聚体(1mm)的含量,可认为水稳性团聚体的含量更能作为衡量土壤结构的稳定性的指标。0.25mm团聚体分散度(PAD0.25)和2mm团聚体分散度(PAD_2)含量均出现增大,而0.25mm水稳性团聚体含量(WAS_(0.25))减少,植被覆盖度对土壤团聚体稳定性影响明显强于坡长;3)WAS_(0.25)含量是影响侵蚀泥沙的颗粒粒径分布的主要因素,随着坡面土壤中WAS_(0.25)的增加,侵蚀泥沙的平均重量直径逐渐降低。同时,泥沙颗粒平均直径与土壤团聚体平均重量直径(MWD_(团聚体))含量呈极显著负相关,可知坡面大团聚体越稳定,坡面土壤的粗化过程越不易形成。     

长期施肥对水稻土有机碳分布及化学结合形态的影响

采用湖南省4个23年连续施肥的稻田长期定位试验,研究了施肥对湖南省水稻土有机碳分布及化学键合形态的影响。试验设不施肥(CK)、化肥(NPK)、中量有机肥(MOM)和高量有机肥(HOM)4个处理。结果表明:在所有施肥处理中,水稳性团聚体均以0.25～1mm和2～5mm粒径含量最高,分别达全土总量的18%～43%和13%～48%。中、高量有机肥处理显著增加了>1mm大团聚体含量以及有机碳在大团聚体中的分配,其中0.25～1mm和1～2mm粒径团聚体中有机碳含量均略高于其余粒径组。与不施肥比较,钙结合态有机碳(Ca-SOC)占总有机碳的比例在2%～4%左右且随有机肥施用呈下降趋势,而铁铝结合态有机碳Fe(Al)-SOC占总有机碳的18%～33%呈上升趋势。有机肥施用条件下,有机碳在大团聚体中的分布的增加、Fe(Al)-SOC的提升以及Ca-SOC的降低意味着土壤有机碳物理和化学保护作用的增强,有利于稻田土壤有机碳的积累,是有机肥施用条件下保持稻田土壤较高固碳速率的重要原因。     

不同林型树倒林隙内微立地类型的土壤微团聚体组成及其分形特征

采用野外调查和室内分析相结合的方法,分析小兴安岭地区阔叶红松林和云冷杉红松林两种林型下树倒林隙内丘坑微立地类型(丘顶和坑底)土壤微团聚体组成及其分形特征。结果表明: 两种林型的土壤微团聚体0.25～2 mm和0.05～0.25 mm粒级含量较高,分别为25.7%～50.7%和27.0%～42.8%,<0.002 mm粒级含量最小,为4.4%～8.9%。在两种林型的树倒林隙内,坑底和丘顶的土壤容重较大,且丘顶土壤养分含量均高于坑底。阔叶红松林树倒林隙内丘顶和坑底的土壤养分含量均高于云冷杉红松林。<0.002 mm土壤微团聚体与土壤物理和化学性质均无相关性,0.25～2 mm和0.002～0.02 mm土壤微团聚体分别与土壤非毛管孔隙度、总孔隙度、通气度、有机质、全磷、全氮和有机碳之间呈极显著正相关和极显著负相关。整体来看,阔叶红松林的土壤分形维数(D)和土壤特征微团聚体组成比例(PCM)大于云冷杉红松林。两种林型下,丘顶和坑底的土壤特征微团聚体粒级比值(RMD)均增高。土壤D和PCM与各土壤理化性质均无显著相关性,土壤RMD与土壤毛管孔隙度、总孔隙度、土壤容重和通气度呈显著负相关。丘顶和坑底微立地的形成会导致土壤较大粒级微团聚体减少,土壤微团聚体稳定性降低,土壤D和PCM增加,RMD显著增加;土壤RMD可作为定量化描述不同林型下丘坑微立地内土壤理化性质的指标。     

长期重金属胁迫对农田土壤微生物生物量、活性和种群的影响

调查了沈阳张士灌区长期污水灌溉造成的原位农田土壤重金属污染状况,从土壤微生物生物量、微生物活性和微生物种群数量的角度评价了长期重金属污染对农田土壤生态系统的影响.结果表明,张士灌区土壤存在严重的Cd污染,土壤Cd含量达1.75～3.89 mg·kg ^-1,部分区域还伴有Cu、Zn复合污染.在目前污染程度下,土壤微生物生物量碳(C_mic)、微生物商(qM)、土壤脱氢酶活性以及自生固氮菌数量随土壤重金属含量增加呈下降趋势,代谢商(qCO₂)随土壤重金属含量增加显著升高,而底物诱导呼吸强度(SIR)、纤维素酶活性以及细菌、放线菌和真菌数量无明显变化.相关性分析表明,土壤Cd含量变化是影响微生物参数变化的主要因素,在微生物参数中微生物商和代谢商对重金属污染最敏感.     

Phyto-availability and speciation change of heavy metals in soils amended with lignin as micro-fertilizer

Lignin is a primary byproduct from the black liquor treatment in paper making industries, its application as micro-fertilizer in agricultural land might provide a promising alternative to sewage discharge. However, application of such a micro-fertilizer might affect the soil properties and result in soil pollution. In this study, the effects of lignin application on phytoavailability and speciation change of heavy metals in soils were investigated. Greenhouse experiments showed that lignin application improved the growth of winter wheat (Triticum aestivum L.) in all three soils investigated. The increase of the biomass for wheat shoot was 59.7%, 39.8% and 12.3% for Beijing soil, Jiangxi soil and Dongbei soil, respectively. In contrast, lignin amendment decreased the concentrations of heavy metals in wheat shoots from 2.2% to 61.0%. Sequential extraction procedure of a three-step BCR was used to investigate the fraction distribution. The extractable fractions were specified as fraction B1: water soluble, exchangeable and carbonate bound or weakly specifically adsorbed; B2: Fe-Mn oxide bound; B3: organic matter and sulfide bound. The results showed that lignin application led to the redistribution of heavy metals in each fraction. Generally, heavy metals decreased in B1 and B2 fractions and increased in B3 fraction. Upon the results short-term application of lignin in agricultural land not only improves the growth of wheat but also reduces the phyto-abailability of heavy metal in wheat.     

Phyto-availability and speciation change of heavy metals in soils amended with lignin as micro-fertilizer

Lignin is a primary byproduct from the black liquor treatment in paper making industries, its application as micro-fertilizer in agricultural land might provide a promising alternative to sewage discharge. However, application of such a micro-fertilizer might affect the soil properties and result in soil pollution. In this study, the effects of lignin application on phyto-availability and speciation change of heavy metals in soils were investigated. Greenhouse experiments showed that lignin application improved the growth of winter wheat (Triticum aestivum L.) in all three soils investigated. The increase of the biomass for wheat shoot was 59.7%, 39.8% and 12.3% for Beijing soil, Jiangxi soil and Dongbei soil, respectively. In contrast, lignin amendment decreased the concentrations of heavy metals in wheat shoots from 2.2% to 61.0%. Sequential extraction procedure of a three-step BCR was used to investigate the fraction distribution. The extractable fractions were specified as fraction B1: water soluble,     

重金属污染对土壤有机质积累的影响

采用田间采样分析与室内培养试验相结合的方法,研究了不同重金属污染土壤中有机质积累的差异及重金属污染强度对土壤有机质矿化动态变化的影响.结果表明：污染土壤中重金属的大量积累可减弱有机物质的矿化速率,增加土壤有机质的积累.土壤中颗粒态有机质及其占总有机碳的比例随重金属积累的增加而增加;而微生物生物量碳占总碳的比例却随土壤重金属污染水平的提高而下降.污染土壤中颗粒态有机质对重金属有显著的富集,这可能是影响土壤有机物质进一步矿化的原因之一.重金属污染可改变土壤有机质的矿化速率,影响土壤有机质的积累与分配.     

Distribution of extractable heavy metals in different soil fractions

Abstract

Due to the difficulties of precisely characterizing environmentally contaminated soil, the effects of heavy metals on plants are studied using uncontaminated soil spiked with known quantities of heavy metals. One problem in using spiked soils is how accurately the distribution of metals mimics stabilized natural soils. We studied the distribution of cadmium, chromium, copper, lead, nickel, and zinc in soil fractions after application in soluble form. The soil samples included a control (an uncontaminated Typic Argiudoll) and two samples spiked with either a moderate or high heavy metal concentration). After application of the salts the soils were subjected to wet/dry cycles over the course of three months. The soils were fractionated using a sequential chemical extraction procedure employing: (1) CaCl₂,(2) NaOH, (3) Na₂EDTA and (4) HNO₃, HCl, and HF. Soil physical separation was carried out by ultrasonic dispersion. The heavy metal levels were determined using ICP-AES. Each heavy metal displayed a unique behavior when added to soil in the form of soluble salts. Cadmium and zinc remained in the soluble fraction, indicating that no equilibrium was attained, while nickel primarily appeared in the insoluble fraction. Chromium, copper and lead were distributed among various soil chemical fractions. The highest levels of all metals appeared in the clay fraction except lead which was mainly present in the silt fraction.     

Assessment of Metal Availability in Soils from a Pb-Zn Mine Site of South-Central Spain

Heavy metal pollution of the soils around an abandoned Pb-Zn mine site located in the Alcudia Valley (South Central Spain) have been characterized by analysis of extractable and total metal concentrations in 60 samples of arable, pasture, and mine lands. The samples showed a broad range of size-particle distribution, cation exchange capacity, and pH values as well as high levels of total metal concentrations (up to 98510 mg kg^?1 of Pb, up to 20912 mg kg^?1 of Zn, and up to 61 mg kg^?1 of Cd). In order to assess the potential availability of metals the metal partitioning in two different soil size fractions (<2 mm and <63 μm) was determined using EDTA and CaCl₂ as sequestering reagents. The average contents of Pb, Zn, and Cd in the <63 μm particle size fraction for both extractions were higher than those of the <2 mm fraction due to the high metal adsorption capacity of the fine soil particles. Concentrations of heavy metals extracted by CaCl₂ were up to three orders of magnitude lower than those extracted by EDTA, because CaCl₂ only extracts the easily mobile fraction. Metal concentrations extracted by both procedures in the two granulometric fractions increased with total metal concentrations, thus increasing the potential environmental risk associated to heavy metal pollution.     

下辽河平原潮棕壤不同粒级碳和氮分布研究

采用具有不同开垦年限的0～20和20～40 cm耕层土壤,对其不同粒级的有机碳和全N分布进行了研究.结果表明,在0～20和20～40 cm耕层,＜0.002 mm粒级的有机碳含量最高,＜0.02 mm粒级含量次之,＜0.2 mm粒级含量最少.土壤全N的粒级分布规律与有机碳基本相同.在同一粒级中,有机碳和全N的各粒级分布与开垦年限没有明显的相关性.各粒级的有机碳与全N相关性极显著,在＜0.2 mm粒级的相关系数为0.74,在＜0.02 mm和＜0.002 mm分别达到了0.94和0.91.     

福建省耕地土壤重金属含量和可浸提性研究

测定了福建省6市、县耕地土壤中的Cu、Zn、Cd、Ni、Pb、Hg、As等7种重金属元素的全量和可浸提态含量,并对测定结果进行了数理统计。结果表明,福建省耕地土壤存在着不同程度的重金属污染,但依元素不同而不同,重金属可浸提态含量占全量的10.0?52.2 Cu、Zn、Cd、Pb、Ni的可浸提态含量与全量之间的相关达极显著水平,Zn、Cd、Pb、As等4元素含量之间存在着显著正相关,而Ni则只与Zn元素有极显著正相关,Cu和Hg与其它重金属元素的相关则均不显著。     

Effects of biochar amendments on speciation and bioavailability of heavy metals in coal-mine-contaminated soil

An incubation experiment was executed on applying biochar as a soil remediation amendment to discuss an effect of the various addition rates on the speciation and bioavailability of heavy metals in mining-contaminated soil. The result showed that the content of Cd in soil was 9.51 times higher than the Huainan soil background values. The contents of Cu, Zn and As were 2.97, 1.60 and 1.42 times the background values, respectively, and the total contents of all heavy metals were higher than the standard values of soil environment quality GB15618-1995 set by the China Ministry of Environmental Protection. Speciation analysis indicated that Cu and Cd were mainly associated with the reducible fraction, while Zn and As were dominated by the residual fraction. After biochar was added to contaminated soil, the residual fractions of heavy metals increased, while the acid-soluble fractions reduced. According to the results of CaCl₂ extraction experiment, CaCl₂-extractable concentrations of Cu, Zn, As, and Cd were observed with a biochar dosage rate of 10%, which were 57.26%, 51.37%, 6.94% and 42.04% lower than those of control soil samples, respectively, but there were no obvious changes of CaCl₂-extractable As.     

芦竹对不同重金属耐性的研究

研究芦竹(Arundo donax)在不同重金属污染湿地中的耐毒性能,测定了不同生长时段芦竹的生物性状和叶绿素含量,以及土壤中重金属含量的变化.结果表明,芦竹分别在浓度为100 mg·kg^-1左右的CuCu²⁺、Pb²⁺、Cd²⁺、Zn²⁺、Ni²⁺、Hg²⁺和50 mg·kg^-1以下的Cr⁶⁺污染环境中能正常成活,在40 d的生长期内,植物体内叶绿素有不同程度降低,下降比率在20%～56%,植物出现叶片软化,叶尖枯黄等症状,但植株仍呈现增长趋势.与对照植物相比较,在重金属胁迫下,植株细长,茎、叶呈黄绿色,除Cr⁶⁺、Hg²⁺外,植物高度基本不受重金属胁迫的影响.芦竹在高浓度(100mg·kg^-1)Cr⁶⁺污染环境中耐性较弱,表现出生长缓慢,部分地下茎腐烂,叶片短时间内出现枯萎等症状.结果还表明,土壤中重金属浓度随植物生长期增长而降低,除被植物吸收,植物挥发外,还存在着重金属向根际圈环境迁移的趋势,根周边湿土中重金属含量,明显高于试验缸外围湿土中重金属含量.可以认为,芦竹具有生物量大,根系发达,适应性强等特点,对修复湿地重金属污染蕴藏着巨大潜力,研究芦竹在植物修复技术中的应用,具有一定的现实意义.