大田条件下水稻败育与铜缺乏的关系

The effect of liming 4 soils developed from Quaternary red clay and red sandstone on the cadmium forms and its toxicity were investigated.Liming the acid red soils could greatly reduce Cd toxicity to plants because the soluble Cd and organic Cd in the soils decreased significantly while Cd bound to minerals/oxides and residual Cd increased markedly with increasing lime rates(pH).     

石灰处理对红壤中镉形态及其毒性的影响

The effect of liming 4 red soils developed from Quaternary red clay and red sandstone on the cadmium forms and its toxicity were investigated. Liming the acid red soils could greatly reduce Cd toxicity to plants because the soluble Cd and organic Cd in the soils decreased significantly while Cd bound to minerals/oxides and residual Cd increased markedly with increasing lime rates (pH).     

基于小白菜Cd吸收推算土壤Cd安全阈值

Cadmium(Cd), a common toxic heavy metal in soil, has relatively high bioavailability, which seriously threatens agricultural products. In this study, 8 different soils with contrasting soil properties were collected from different regions in China to investigate the Cd transfer coefficient from soil to Chinese cabbage(Brassica chinensis L.) and the threshold levels of Cd in soils for production of Chinese cabbage according to the food safety standard for Cd. Exogenous Cd(0–4 mg kg~(-1)) was added to the soils and equilibrated for 2 weeks before Chinese cabbage was grown under greenhouse conditions. The influence of soil properties on the relationship between soil and cabbage Cd concentrations was investigated. The results showed that Cd concentration in the edible part of Chinese cabbage increased linearly with soil Cd concentration in 5 soils, but showed a curvilinear pattern with a plateau at the highest dose of exogenous Cd in the other 3 soils. The Cd transfer coefficient from soil to plant varied significantly among the different soils and decreased with increasing soil p H from 4.7 to 7.5. However, further increase in soil pH to 8.0 resulted in a significant decrease in the Cd transfer coefficient. According to the measured Cd transfer coefficient and by reference to the National Food Safety Standards of China, the safety threshold of Cd concentration in soil was predicted to be between 0.12 and 1.7 mg kg~(-1) for the tested soils. The predicted threshold values were higher than the current soil quality standard for Cd in 5 soils, but lower than the standard in the other 3 soils. Regression analysis showed a significant positive relationship between the predicted soil Cd safety threshold value and soil p H in combination with soil organic matter or clay content.     

七种钾释放动力学方程的比较和动力学参数的应用

Batch equilibrium experiments were conducted to investigate cadmium （Cd） sorption by two permanent-charge soils, a yellow-cinnamon soil and a yellow-brown soil, and two variable-charge soils, a red soil and a latosol, with addition of selected organic acids （acetate, tartrate, and citrate）. Results showed that with an increase in acetate concentrations from 0 to 3.0 mmol L^-1, Cd sorption percentage by the yellow-cinnamon soil, the yellow-brown soil, and the latosol decreased. The sorption percentage of Cd by the yellow-clnnamon soil and generally the yellow-brown soil （permanent-charge soils） decreased with an increase in tartrate concentration, but increased at low tartrate concentrations for the red soil and the latosol. Curves of percentage of Cd sorption for citrate were similar to those for tartrate. For the variable-charge soils with tartrate and citrate, there were obvious peaks in Cd sorption percentage. These peaks, where organic acids had maximum influence, changed with soil type, and were at a higher organic acid concentration for the variable-charge soils than for the permanent charge soils. Addition of cadmium after tartrate adsorption resulted in higher sorption increase for the varlable-charge soils than permanent-charge soils. When tartrate and Cd solution were added together, sorption of Cd decreased with tartrate concentration for the yellow-brown soil, but increased at low tartrate concentrations and then decreased with tartrate concentration for the red soil and the latosol.     

通过施用碱性矿渣和作物残茬生物炭以促进酸性老成土中盐基饱并降低土壤酸度

This investigation was conducted by using alkaline slag and crop straw biochars to reduce acidity of an acidic Ultisol through incubation and pot experiments with lime as a comparison. The soil was amended with different liming materials： lime（1 g kg^-1）,alkaline slag（2 and 4 g kg^-1）, peanut straw biochar（10 and 20 g kg^-1）, canola straw biochar（10 and 20 g kg^-1） and combinations of alkaline slag（2 g kg^-1） and biochars（10 g kg^-1） in the incubation study. A pot experiment was also conducted to observe the soybean growth responses to the above treatments. The results showed that all the liming materials increased soil p H and decreased soil exchangeable acidity. The higher the rates of alkaline slag, biochars, and alkaline slag combined with biochars, the greater the increase in soil p H and the reduction in soil exchangeable acidity. All the amendments increased the levels of one or more soil exchangeable base cations. The lime treatment increased soil exchangeable Ca^2＋, the alkaline slag treatment increased exchangeable Ca^2＋ and Mg^2＋ levels, and the biochars and combined applications of alkaline slag with biochars increased soil exchangeable Ca^2＋, Mg^2＋ and K^＋ and soil available P. The amendments enhanced the uptake of one or more nutrients of N, P, K, Ca and Mg by soybean in the pot experiment. Of the different amendments, the combined application of alkaline slag with crop straw biochars was the best choice for increasing base saturation and reducing soil acidity of the acidic Ultisol. The combined application of alkaline slag with biochars led to the greatest reduction in soil acidity, increased soil Ca, Mg, K and P levels, and enhanced the uptake of Ca, Mg, K and P by soybean plants.     

有机物料对淹水土壤中施入的镉形态的影响

The effect of three organic materials(rice straw,Chinese milk vetch and pig manure)on the fractionation of cadmium added into two soils(a red soil and a fluvo-aquic soil) was studied using submerged incubation experiment.The organic materials increased soil soild organic carbon(SOC),pH value,the concentration of active Si in all the treatments and active Fe and Mn in some treatments.Accumulated SOC caused directly the increase of Cd bound to solid organic matter and consequently the decrease of exchangeable Cd.Higher active Si and pH,as well as lower Eh,were also responsible for the reduction of exchangeable Cd.Cd bound to mn oxide was positively correlated with pH values and rose significantly after one-month incubation,but decreased after three-month incubation.Cd bound to amporphous Fe oxide increased with the incubation time,but was not affected significantly by adding organic materials.     

接种菌根真菌影响青菜中铅镉的累积和迁移

Heavy metal(HM) contamination in soils is an environmental issue worldwide that threatens the quality and safety of crops and human health. A greenhouse experiment was carried out to investigate the growth, mycorrhizal colonization, and Pb and Cd accumulation of pakchoi(Brassica chinensis L. cv. Suzhou) in response to inoculation with three arbuscular mycorrhizal(AM) fungi(AMF), Funneliformis mosseae, Glomus versiforme, and Rhizophagus intraradices, aimed at exploring how AMF inoculation affected safe crop production by altering plant-soil interaction. The symbiotic relationship was well established between pakchoi and three AMF inocula even under Pb or Cd stress, where the colonization rates in the roots ranged from 24.5% to 38.5%. Compared with the non-inoculated plants, the shoot biomass of the inoculated plants increased by 8.7%–22.1% and 9.2%–24.3% in Pb and Cd addition treatments, respectively. Both glomalin-related soil protein(GRSP) and polyphosphate concentrations reduced as Pb or Cd concentration increased. Arbuscular mycorrhizal fungi inoculation significantly enhanced total absorbed Pb and Cd(except for a few samples) and increased the distribution ratio(root/shoot) in pakchoi at each Pb or Cd addition level. However, the three inocula significantly decreased Pb concentration in pakchoi shoots by 20.6%–67.5% in Pb addition treatments, and significantly reduced Cd concentration in the shoots of pakchoi in the Cd addition treatments(14.3%–54.1%), compared to the non-inoculated plants.Concentrations of Pb and Cd in the shoots of inoculated pakchois were all below the allowable limits of Chinese Food Safety Standard.The translocation factor of Pb or Cd increased significantly with increasing Pb or Cd addition levels, while there was no significant difference among the three AMF inocula at each metal addition level. Meanwhile, compared with the non-inoculated plants, AMF inocula significantly increased soil p H, electrical conductivity, and Pb or Cd concentrations in soil organic matter in the soils at the highest Pb or Cd dose after harvest of pakchoi, whereas the proportion of bioavailable Pb or Cd fraction declined in the AMF inoculated soil. Our study provided the first evidence that AM fungi colonized the roots of pakchoi and indicated the potential application of AMF in the safe production of vegetables in Pb or Cd contaminated soils.     

Growth,Cadmium and Zinc Accumulation of Ornamental Sunflower(Helianthus annuus L.)in Contaminated Soil with Different Amendments

Use of ornamental plants for phytoremediation of metal-contaminated soil is a new option. A pot experiment was carried out to assess the effect of application of amendments, i.e., swine manure, salicylic acid (SA) and potassium chloride (KCl), on the growth, uptake and translocation of cadmium (Cd) and zinc (Zn) of ornamental sunflower (Helianthus annuus L.) grown on a contaminated soil. The three amendments increased sunflower height, flower diameter, and biomass. Manure significantly decreased Cd and Zn concentrations in sunflower, and thus decreased the bioaccumulation coeffcient (BCF) of Cd and Zn. However, using of KCl markedly increased Cd concentrations in sunflower and the BCF of Cd. Additionally, both swine manure and KCl application increased Cd and Zn translocation from root to aboveground part. Swine manure and salicylic acid reduced the Cd/Zn ratios in flower of sunflower, while KCl significantly increased the Cd/Zn ratios. Correlation analysis demonstrated that the Cd/Zn ratio in the root of sunflower was affected by K/Na ratio in root and soil available potassium (K) concentration. Ornamental sunflower could be grown as an alternative plant in the Cd- and Zn-contaminated soil with KCl application to get the balance between environmental and economic interests.     

水稻突变体对镉的吸收及其亚细胞分布和化学形态特点

Wild-type （Zhonghua 11） and mutant rice （Oryza sativa L.） plants were used to investigate the effect of cadmium （Cd） application on biomass production, to characterize the influx of Cd from roots to shoots, and to determine the form, content, and subcellular distribution of Cd in the roots, leaf sheaths, and leaves of the rice plants. Seedlings were cultivated in a nutrient solution and were treated with 0.5 mmol L^-1 of Cd^2＋ for 14 d. The sensitivity of rice plants to Cd toxicity was tested by studying the changes in biomass production and by observing the onset of toxicity symptoms in the plants. Both the wild-type and mutant rice plants developed symptoms of Cd stress. In addition, Cd application significantly （P ≤ 0.01） decreased dry matter production of roots, leaf sheaths, and leaves of both types, especially the mutant. The Cd content in roots of the mutant was significantly （P ≤0.05） higher than that of the wild-type rice. However, there was no significant difference in the Cd content of roots, leaf sheaths, and leaves between the wild-type and mutant rice. Most of the Cd was bound to the cell wall of the roots, leaf sheaths, and leaves, and the mutant had greater Cd content in cell organelles than the wild type. The uneven subcellular distribution could be responsible for the Cd sensitivity of the mutant rice. Furthermore, different chemical forms of Cd were found to occur in the roots, leaf sheaths, and leaves of both types of rice plants. Ethanol-, water-, and NaCl-extractable Cd had greater toxicity than the other forms of Cd and induced stunted growth and chlorosis in the plants. The high Cd content of the toxic forms of Cd in the cell organelles could seriously damage the cells and the metabolic processes in mutant rice plants.     

堆肥缓解土壤镉的植物毒性: 对白菜生长的影响

The growth performance of pakchoi (Brassica chinensis L.) in relation to soil cadmium (Cd) fractionations was investigated to evaluate the remediating effect of poultry manure compost on Cd-contaminated soil. A yellow-brown soil (Alfisol) treated with various levels of Cd (0–50 mg Cd kg-1 soil) was amended with increasing amounts of compost from 0 to 120 g kg-1 . Compost application transformed 47.8%–69.8% of soluble/exchangeable Cd to the organic-bound fraction, and consequently decreased Cd uptake of pakchoi by 56.2%–62.5% as compared with unamended soil. Alleviation of Cd bioavailability by compost was attributed primarily to the increase of soil pH and complexation of Cd by organic matter including dissolved organic matter. In general, the improvement of pakchoi performance was more pronounced in higher Cd-contaminated soil. Addition of large amount of compost also favored the anti-oxidative capability of pakchoi against Cd toxicity. This low cost remediation method seems to be very effective in the restoration of Cd-contaminated soils.     

CaCO_3对Cd和几种营养元素在红壤-黄豆系统中的调控作用

利用盆栽试验,通过研究CaCO3施用对Cd在红壤-黄豆系统中的迁移与分配和对几种营养元素在土壤以及黄豆叶片中含量变化的影响,探讨了CaCO3对Cd和几种营养元素在红壤-黄豆系统中的调控作用。结果表明,CaCO3施用能提高土壤pH值和交换态Ca含量,显著降低土壤交换态Cd含量,有效抑制黄豆植株对Cd的吸收和转运,从而达到修复土壤Cd污染的目的。同时,随着CaCO3施用量的增加,土壤交换态K,Mg,Zn,Mn等营养元素含量下降,黄豆叶片中这些元素含量也同时降低。CaCO3施用虽然能够降低土壤Cd的活性,有效抑制土壤Cd向植物地上部分迁移,显著降低黄豆各器官的Cd含量,但是黄豆叶片中营养元素含量下降的现象应该引起人们的注意。     

施用有机物料对土壤镉形态的影响

采用室内培养试验,研究作物新鲜秸秆和腐熟猪粪对模拟镉（Cd）污染的土壤中Cd形态转化的动态影响。结果表明,各处理土壤交换态Cd含量随培养时间均逐渐降低。碳酸盐结合态和铁锰氧化物结合态Cd含量先增加后降低, 而有机质结合态和残渣态Cd含量则逐渐增加。添加秸秆可增加土壤交换态Cd含量,但随时间延长,增幅逐渐降低, 猪粪则可降低土壤交换态Cd含量。添加有机物后土壤交换态Cd含量的变化主要是由有机质结合态或残渣态Cd含量的变化而引起。秸秆和猪粪对土壤Cd形态的转化与土壤胡敏酸（HA）和富里酸（FA）的变化有关。秸秆对能活化土壤Cd的FA增加幅度大于对能钝化土壤Cd的HA增加幅度,降低HA/FA比,但降幅随时间逐渐减少; 猪粪在整个培养阶段对HA增加幅度均大于FA的增加幅度,增加HA/FA比。秸秆和猪粪均可降低潮土pH而提高红壤pH,但只有猪粪可通过提高红壤pH降低Cd向交换态转化。添加秸秆和猪粪后,Cd由低活性态向交换态转化与HA/FA呈显著负相关。     

Cd胁迫对5种植物体内Cd积累及根际土壤特性的影响

以大豆、棉花、曼陀罗、蓖麻和玉米为供试材料,采用土柱栽培试验,探讨Cd胁迫后,5种植物根系活力与各器官间cd含量的差异,以及5种植物根际土壤酶活性与根际土壤营养含量对Cd胁迫的反应.结果表明:(1)5种受污染的植物体Cd富集量超出对照不受污染的植物体达3～7倍之多,但都未达富集临界值100 mg/kg.(2)不同植物不同器官Cd运转积累部位不同,以根冠比衡量,蓖麻、玉米、棉花R/S大于1,称作根优势植物;大豆、曼陀罗R/S小于1,称作冠优势植物;棉花R/S近于1,称作冠根均衡植物.5种植物吸收富集最强的前3位植物(大豆、玉米、棉花)都是人工驯化的栽培植物,其吸肥能力强于野生植物的,这种吸肥能力与吸Cd能力是否呈正相关关系,吸肥能力的差异是否可以作为污染土壤利用改良的依据值得进一步研究.(3)大豆、曼陀罗茎秆中Cd含量均较根、叶、籽实中的高,考虑到大豆是粮食作物,同时其根部Cd含量仅次子茎的,而曼陀罗作为一种杂草,其地上部Cd转移系数大于1.0,因此,比较供试5种植物,应优先选择曼陀罗用于Cd污染区域的土壤净化.(4)Cd胁迫(5 mg/kg)提高了5种植物根系还原TTC强度,抑制了大豆和蓖麻根际土壤多种酶活性,而促进了曼陀罗和玉米根际土壤多种酶活性以及棉花根际土壤脲酶、蔗糖酶和碱性磷酸酶活性;比较5种酶活性,碱性磷酸酶活性对Cd反应较不敏感,脲酶和蔗糖酶活性对Cd反应较敏感,多酚氧化酶和过氩化氯酶活性对CA的敏感程度因不同植物而异.结果还表明Cd胁迫不同程度地提高了供试5种植物根际土壤营养含量.(5)研究为有效开展Cd污染土壤的植物修复资源提供理论依据.     

海泡石对典型水稻土镉吸附能力的影响

通过吸附解吸实验研究了添加海泡石后典型水稻土对Cd的吸附解吸特性及其对吸附溶液pH值变化的响应。结果表明,Freundlich方程可以较好地拟合红黄泥、黄泥田和红沙泥3种典型水稻土对Cd的等温吸附过程（R2〉0.962）。在溶液初始Cd浓度相同的情况下,添加海泡石可使3种水稻土对Cd的吸附量增加20%以上,增强土壤对Cd的吸附强度,有效降低吸附Cd的解吸率,其效果随海泡石添加量的增大而增强。3种水稻土吸附Cd的解吸率均高于70%,而且都随吸附量的增加而上升。溶液的pH值是影响土壤吸附Cd的一个重要因素,在低pH值的条件下（pH〈4）,随着溶液pH值的降低,土壤对Cd的吸附量迅速降低,当溶液pH值高于5时,pH值的变化对吸附量的影响较小。在溶液初始pH值2-8范围内,添加海泡石均能有效提高3种水稻土对Cd的吸附能力。     

添加有机酸对土壤镉形态转化及苋菜镉积累的影响

植物根系分泌的低分子量有机酸能够与土壤中的镉形成镉–有机酸复合体,从而影响根际镉的移动性。本文通过添加有机酸对土壤镉形态转化的研究,阐明有机酸与镉生物积累的关系。采用盆栽试验及土壤培养等方法,研究了添加苹果酸、柠檬酸对赤红壤和黄棕壤中镉的形态转化以及超积累型苋菜天星米镉生物积累的影响。结果表明,与Cd 25 mg/kg处理比较,Cd 25 mg/kg＋苹果酸、Cd 25mg/kg＋柠檬酸处理对苋菜生物量未产生影响,但显著增加苋菜根系及地上部镉含量;添加苹果酸、柠檬酸处理显著降低土壤专性吸附态Cd含量,却显著增加了交换态Cd、碳酸盐结合态Cd和有机结合态Cd含量。说明添加苹果酸、柠檬酸还能够通过影响土壤镉形态转化而促进苋菜对镉的积累。     

不同氮形态对镉胁迫下小白菜生长及镉含量的影响

【目的】研究施用速效氮肥（全铵、全硝、硝铵复合和尿素）对镉（Cd）污染土壤小白菜生长和Cd含量的影响,为合理选择氮肥,缓解Cd对植物生长的胁迫并减少Cd在作物体内的积累提供依据。【方法】以小白菜为试材,采用菜园土进行了盆栽试验。以CdCl2溶液模拟土壤Cd胁迫,设土壤Cd含量0、1、3和5 mg/kg 4个水平,每个胁迫水平分别供应小白菜铵态氮、硝态氮、硝铵（1:1）和尿素4种氮形态,总氮添加量均为N 400 mg/kg土。收获后分析各处理间小白菜的生长、光合、氧化胁迫及Cd含量的差异。【结果】 1）与无Cd对照相比,Cd 1 mg/kg处理水平下,全铵、全硝、硝铵和尿素处理的小白菜可食部分鲜重分别下降了31%、16%、21%和26%;Cd 3 mg/kg处理水平下分别下降了58%、28%、35%和39%;Cd 5 mg/kg处理水平下分别下降了83%、38%、52%和69%。全硝和硝铵处理间小白菜Cd耐受系数（TICd）差异不显著,但均高于全铵和尿素处理。2）与无Cd对照相比,Cd 1 mg/kg处理下,全铵、全硝、硝铵和尿素处理小白菜叶片的光合速率分别下降了14%、10%、12%和13%;Cd 3 mg/kg处理分别下降了33%、22%、25%和40%;Cd 5 mg/kg处理分别下降了53%、42%、41%和56%。与无Cd对照相比,1 mg/kg Cd浓度时全铵、全硝、硝铵和尿素处理小白菜叶片的丙二醛含量分别增加了11%、4%、9%和11%;超氧自由基产生速率分别增加了5%、1%、2%和4%,综合比较,以全硝处理下小白菜受Cd的光合抑制及氧化胁迫相对最小。3）3个Cd处理水平,均以施用全铵和尿素处理的小白菜体内Cd含量最高,硝铵处理次之,全硝处理最低。【结论】在供试菜园土上,小白菜施用铵态氮和尿素易引起Cd在小白菜体内的积累。施用硝态氮可缓解Cd诱导的光合抑制和氧化胁迫,减轻Cd对小白菜的生长胁迫,降低作物体内Cd的含量。     

钙质钝化材料对四川盆地6种主要旱作土壤Cd的钝化效应

为针对性、定量化地利用钝化处理实现不同类型Cd污染土壤的安全利用,以四川盆地6种主要旱作土壤为研究对象,采用室内培养试验和土培试验探讨了6个剂量水平下,钙质钝化材料对土壤pH、CEC、有效Cd含量、Cd形态、小白菜生物量和Cd含量的影响。结果表明:(1)钙质钝化材料可提升6种土壤的pH和CEC,土壤CEC随用量的增加而持续增加,而土壤pH在提升至微碱性水平后,不再随用量的增加而增加;(2)6种土壤有效Cd含量随钝化材料用量的增加先显著降低,后趋于平稳,用量＞2.5%后均无显著变化。该添加量下,有效Cd含量降幅为典型黄壤(63.32%)＞酸性紫色土(46.65%)＞漂洗黄壤(38.51%)＞中性紫色土(34.97%)＞石灰性紫色土(18.03%)＞灰潮土(16.60%);土壤中可交换态Cd主要向碳酸盐结合态、铁锰氧化物结合态和残渣态形态转化;(3)除石灰性紫色土外,钙质钝化材料可显著提升其余5种污染土壤中小白菜的生物量并显著降低其可食部位Cd含量。用量为2.5%时,典型黄壤、漂洗黄壤和酸性紫色土中小白菜Cd含量降幅高达84.28%,79.90%,69.87%,显著优于中性紫色土、灰潮土和石灰性紫色土(5%用量时降幅仅为40.27%,31.13%,17.98%)。该研究揭示钙质钝化材料对6种Cd污染旱作土壤的剂量-效应差异,并在典型黄壤、漂洗黄壤和酸性紫色土中钝化效率较优,为不同土壤条件下钙质钝化材料的合理使用提供科学依据。     

生物炭对红壤和褐土中镉形态的影响

【目的】重金属对环境危害的大小主要取决于其形态分布,尤其是生物有效态镉 (Cd) 的含量和存在比例。添加生物炭可以降低Cd超标土壤中生物有效态Cd的含量,本文研究了施用生物炭后红壤和褐土中Cd形态的变化及其与生物炭施用量的关系,以加深对生物炭修复Cd污染土壤机理的认识。【方法】选择红壤 (pH 5.21) 和褐土 (pH 7.75) 两类土壤进行了室内培养试验。将两个过2 mm筛的自然风干土壤各40 kg,分别装于20 L塑料盒中,加Cd(NO₃)₂溶液使土壤外源Cd含量达到5 mg/kg,保持70%田间最大持水量,于25℃条件下平衡两周;之后,在每1000 g土内,分别添加生物炭0、5、10、20 g,均匀混合后,室温培养50 d;在培养1、4、7、14、21、35、49 d时分别取样,测定土壤pH和有机碳含量,利用Tessier分级法测定土壤Cd形态。【结果】红壤pH随生物炭施用量的增加显著升高,培养14天后,生物炭施加量为2%时,土壤由酸性变为弱碱性,生物炭对褐土pH的提高作用不显著。红壤和褐土有机碳含量均随生物炭施用量的增加而升高。培养49天后,红壤可交换态Cd含量的降幅较大,降幅为0.31～0.82 mg/kg,且处理2%的可交换态Cd含量最低,为1.24 mg/kg,生物炭施用量2%的红壤碳酸盐结合态Cd含量最高,为1.06 mg/kg,施用生物炭的红壤碳酸盐结合态Cd和Fe、Mn氧化物结合态Cd所占比例增加了3.14%～14.21%、8.20%～23.96%,施用生物炭的褐土碳酸盐结合态Cd和Fe、Mn氧化物结合态Cd升高了0.94%～2.61%、0.80%～7.90%。褐土的土壤有机碳含量和生物炭施用量与土壤可交换态Cd呈极显著负相关关系,与土壤碳酸盐结合态Cd,土壤Fe、Mn氧化物结合态Cd和土壤有机结合态Cd呈极显著正相关关系;红壤pH、有机碳含量和生物炭施用量均与土壤可交换态Cd呈极显著负相关关系,与土壤其他四种形态Cd呈极显著正相关关系。但在红壤中土壤有机碳和生物炭施用量与各形态Cd的相关系数均大于在褐土中的相关系数。【结论】综合分析两种类型土壤中Cd形态的变化,发现生物炭对红壤的修复效果优于对褐土的修复效果,因此生物炭可以作为Cd污染的酸性土壤的一种修复改良材料。     

石灰与生物炭配施对不同浓度镉污染土壤修复

通过室内培养试验,研究生物炭与石灰不同用量配施对镉污染土壤pH和镉赋存形态的影响。结果表明,生物炭与石灰配施能够明显提高污染土壤pH,且随着施入量的增加pH提升效果显著。随着石灰和生物炭配施用量的增加,土壤交换态镉降低比例逐渐增大。培养60天后,镉污染浓度为5mg/kg的土壤交换态镉含量同对照处理相比依次减少36.80%,49.12%和57.38%;而土壤镉污染浓度为20mg/kg的土壤交换态镉含量较对照相比分别降低29.27%,31.68%和39.03%。2个浓度中土壤碳酸盐结合态镉、铁锰氧化物结合态镉和有机结合态镉均有所增加,残渣态镉虽有所增加,但在不同浓度之间存在差异。总体来看,本试验用量条件下,石灰和生物炭配施对污染浓度为5mg/kg的土壤镉钝化效果优于污染浓度为20mg/kg的土壤。