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1.
不同改良剂对酸性土壤的修复效应 总被引：3，自引：1，他引：2
为明确不同改良剂对酸性植烟土壤的修复效应,采用盆栽试验,分析了施用丰收延酸性土壤改良剂、金叶酸性土壤改良剂及石灰后土壤pH、水解性酸、潜性酸及土壤交换性能的动态变化。结果表明:施用改良剂可提高土壤pH 3.01%~24.11%,降低土壤水解性酸16.08%~50.46%、交换性Al 3+51.80%~64.27%、交换性H+含量84.12%~93.56%,提高土壤交换性盐基总量45.18%~46.16%、阳离子交换量0.33%~20.10%、盐基饱和度21.35%~49.78%。施用土壤改良剂后,土壤pH先升高后下降,至移栽60天后趋于稳定;土壤水解性酸在烤烟移栽后30~90天差异较小,至移栽后120天略有增加。施用石灰的土壤交换性氢、交换性铝一直下降,但施用丰收延、金叶酸性土壤改良剂的土壤交换性铝下降至烟苗移栽后120天略有增加,土壤交换性氢上升至烟苗移栽后120天大幅度下降。施用土壤改良剂后,土壤交换性盐基总量、阳离子交换量、盐基饱和度一直提高,但变化幅度较小。不同土壤改良剂的材料来源及组成成分不同,其对酸性土壤的恢复效果也不同,以施用石灰的效果最好。 相似文献
2.
模拟酸雨对果园土壤主要形态酸变化的影响研究 总被引：1，自引：0，他引：1
采用室内淋溶的方法研究了模拟酸雨对果园土壤pH（H2O）、pH（KCl）、交换性酸（EA）、交换性铝（EAl）、可滴定酸度（BNC）等各形态酸的变化影响,并依据淋溶前后各形态酸的含量评价了土壤酸度的变化。试验结果表明：以土壤pH（H2O）值作为供试土壤酸化指标,pH≤4．5的模拟酸雨淋溶促进了土壤酸化,而pH≥5．5的酸雨淋溶缓冲了土壤的酸化;以土壤pH（KCl）值、交换性酸（EA）、交换性铝（EAl）或可滴定酸度（BNC）作为土壤酸化的指标,pH2．5的酸雨淋溶促进了土壤酸化,而pH≥3．5的淋溶处理缓冲了土壤的酸化,土壤酸度减弱。 相似文献
3.
工业副产品对红壤酸度改良的研究 总被引：17，自引：5，他引：12
选择4种工业副产品(粉煤灰、碱渣、赤泥和磷石青),通过室内培养实验研究了它们对酸性红壤的改良效果.结果表明碱渣和赤泥能降低土壤溶液中的毒性形态的Al、可溶性Al以及交换性Al,增加土壤pH、交换性盐基和ECEC,可成为石灰的替代品作为酸性土壤的改良剂,且长期施用不会像石灰那样加剧土壤Mg、K的缺乏.粉煤灰的改良效果不太理想,而磷石青虽然能增加土壤交换性盐基和ECEC,降低土壤的交换性Al,但增加土壤溶液中的毒性形态的Al和可溶性Al,因此不利于表层土壤酸化的改良.加入质子消耗量与土壤交换性酸量等当量的碱渣和赤泥时,红壤pH升高到5.81～6.26,土壤Al的饱和度降低到15%以下,即可消除Al的毒害.根据碱渣和赤泥的质子消耗容量和红壤的交换性酸量来确定改良剂的施入量是估算改良剂用量的可行方法. 相似文献
4.
长期施用猪粪对红壤酸度的改良效应 总被引：10，自引：1，他引：9
土壤酸化严重限制了我国南方红壤区土壤的农业利用。本研究应用江西鹰潭红壤生态实验站长期猪粪养分淋失试验,分析了不同施肥处理（对照处理：N 0 kg/hm2;低量有机肥：N 150 kg/hm2;高量有机肥：N 600 kg/hm2;高量有机肥+石灰处理：有机肥N 600 kg/hm2 ＋石灰3 000 kg/(hm2·3a)）长期施用对红壤酸度的改良效应。研究结果表明,9年高量有机肥施用中土壤pH值平均每年上升0.085个单位,而低量有机肥施用对土壤pH没有显著影响。有机肥长期施用增加了土壤盐基离子浓度,其中Ca、Mg增加幅度较大,使得长期施肥后土壤盐基以Ca为主,其次是Mg,而K、Na比例较低。长期有机肥施用有效降低了红壤旱地表层土壤交换性酸含量,尤其是对交换性铝含量的降低程度较大,且随施肥量的增加而增大,在施肥4年后可基本消除铝毒。高量施肥基础上的石灰添加进一步提高了土壤pH值,加快了土壤酸度改良。红壤旱地猪粪施用显著提高了玉米产量,达到酸度改良效果的最低猪粪用量为Ca 162 kg/hm2。在施肥初期添加一次石灰,将土壤pH值迅速提高,然后通过有机肥对pH的稳定作用保持和逐步提高土壤pH,可在最短时间、用最少投入消除土壤酸害。 相似文献
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为比较碱渣、牡蛎粉和石灰对酸性烟田的改良效果及其对烤烟生长影响，本研究通过田间试验探究了三种改良剂对酸性烟田土壤酸度、烤烟产量与品质及经济效益影响。结果表明，三种改良剂施用均有效提高土壤pH，降低交换性酸和可溶性铝（Al）的含量，提升土壤交换性盐基阳离子含量。碱渣对土壤酸度的改良效果最佳，可使土壤pH提高0.38个单位，交换性酸和可溶性Al含量降低90.9%和39.8%。同时，碱渣处理中土壤交换性Ca2+和Mg2+含量分别增加了72.8%和91.9%。随着土壤性质的改善，三种改良剂均促进了烤烟的生长，提升了烟叶产量与内在品质。三种改良剂使烟叶产量增加6.0%~9.5%，上等烟比例提高4.0%~16.9%，产值增加11.7%~19.5%，净增收益增加4593.00~9270.30元/hm2，其中碱渣的增产增收幅度最大。此外，改良剂的施用优化了烤烟化学成分组成，其中牡蛎粉处理烟叶的品质最佳。总体看，利用碱渣改良酸性烟田具有广泛的应用前景，但在实际应用中，需注意控制碱渣Na和Cl元素含量。 相似文献
6.
改良剂对反酸田土壤性质与水稻产量的影响 总被引：11，自引：0，他引：11
采用盆栽试验研究了不同改良剂在反酸田土壤上的应用效果。结果表明,土壤pH在3.47~4.90范围内,pH与交换性H+和交换性Al3+呈极显著线性负相关关系,而与土壤有效铁和有效硫含量呈显著正相关。不同改良处理在提高作物产量和改良土壤性质方面较对照处理与NPK处理效果明显,且钙镁磷肥、自研改良剂、石灰及碱渣等无机改良剂改良效果显著高于添加腐植酸、精制有机肥、碱性有机肥处理。其改良效果主要体现在提高土壤pH,显著降低土壤交换性H+和交换性Al3+含量,明显增加土壤有效钙和有效镁的含量,改善根系生长环境,增加水稻地上部养分吸收和水稻籽粒产量。综上,初步认为酸害(包括活性酸和潜在酸)是反酸田土壤最主要的限制因子,钙镁磷肥、自研改良剂和石灰等偏碱性且富含有效钙或磷的无机矿物质是农业生产中改良反酸田的适宜改良剂。 相似文献
7.
石灰和绿肥对不同种植制度植烟酸性土壤改良效果 总被引：3，自引：1，他引：2
为寻求酸性植烟土壤可持续改良方法,采用大田试验研究了石灰、石灰+绿肥在烤烟连作、烤烟与玉米轮作方式上对酸性植烟土壤物理特性、主要养分和酸度特征指标的影响,并分析了土壤pH与土壤理化指标的相关性。结果表明:在烤烟连作方式下,施用石灰并结合种植绿肥还田改良酸性土壤比单施石灰效果好,能使土壤容重、水解性酸、交换性酸、交换性氢和交换性铝分别降低11.97%,25.00%,18.46%,21.74%和16.67%,土壤孔隙度、有机质、碱解氮、有效磷、速效钾含量、pH、阳离子交换量、盐基饱和度和土壤缓冲容量分别提高42.26%,57.02%,11.86%,16.39%,50.65%,5.97%,8.05%,13.17%和81.90%。施用石灰并结合种植绿肥对烤烟与玉米轮作方式的酸性土壤修复效果较烤烟连作更好,土壤容重、水解性酸、交换性酸、交换性氢和交换性铝可分别降低4.00%,20.51%,27.92%,10.00%和37.14%,土壤孔隙度、有机质、碱解氮、有效磷、速效钾含量、pH、阳离子交换量、盐基饱和度和土壤缓冲容量可分别提高9.17%,13.97%,7.22%,12.06%,5.08%,5.15%,35.27%,15.44%和28.05%。石灰+绿肥协同改良酸性土壤的效果比单施石灰好,烤烟与玉米轮作较烤烟连作更有利于酸化土壤的修复。研究结果为采用石灰和种植绿肥还田改良酸性土壤提供了理论依据和实践指导。 相似文献
8.
酸沉降与我国南方森林土壤的酸化 总被引：4，自引：0，他引：4
通过模拟酸沉降土壤连续浸泡试验，研究了我国南方5种森林土壤的酸化过程，并讨论了影响土壤酸化的几个因素。结果表明，土壤对酸沉降H^ 的中和能力，对酸沉降阴离子（SO4^2-和NO3^-）的吸附，土壤阳离子（Ca^2 ,Mg^2 )等盐基离子以及Al^3 )的风化，土壤pH和BS的变化，都在土壤酸化过程中有着重要作用。同时，酸沉降的酸度（pH值）是决定土壤酸化的主要因素，而酸沉降中高含量的盐基离子可能缓解土壤的酸化过程。结合土壤本身物理化学基本特性可以得知，福建土壤对酸沉降引起的酸化最为敏感；江西、湖南土壤次之；重庆土壤的酸化敏感性较弱；而贵州土壤对酸沉降不太敏感。 相似文献
9.
浙江中部红壤施用石灰对土壤交换性钙、镁及土壤酸度的影响 总被引：42，自引：0，他引：42
为了确定红壤施用石灰后钙、镁移动和土壤酸化速率,监测了耕层（10～20ｃｍ）和底土（20～60ｃｍ）的ｐＨ和交换性Ca2+、Mg2+、Al2+的长期变化。结果表明,耕层交换性Ca2+在施用石灰后的一年半时间达到最高值,此后随着时间的推移而急剧减少;而底土的交换性Ca2+随石灰用量的增加和施用石灰后时间的推移而增加。镁在土壤剖面中的移动比钙快;施用石灰后耕层和底土酸度的降低与交换性Ca2+的增加基本同步。在本试验条件下,不论施用石灰与否都存在着复酸化过程,但施用石灰后复酸化作用更强。 相似文献
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11.
通过培养实验,比较研究了茶树老叶和刺槐叶对2种酸化茶园土壤的改良效果。结果表明,在酸性茶园土壤中分别加入5、10和20g·kg^-1。茶树老叶和剌槐叶培养35d后,相对于对照,土壤pH值有不同程度的提高,土壤交换性酸减小,土壤交换性钙和镁等交换性盐基离子数量有所提高,土壤毒性铝离子的数量减少。2种树叶对土壤酸度的改良效果随其加入量的增加而增加,刺槐叶的改良效果好于茶树老叶,2种树叶对红壤的改良效果优于其对黄棕壤的改良效果。植物物料所含的灰化碱及豆科植物所含大量有机氮的矿化是导致土壤酸度下降的主要原因。 相似文献
12.
Sahin Hatice Dieffenbach Antje Kaupenjohann Martin Peiffer Stefan 《Water, air, and soil pollution》1998,102(1-2):117-138
Investigations on soil and freshwater acidification are usually focused on well-aerated systems. This study deals with the role of reductive processes for the neutralization of acid soil solution within helocrene springs. Two toposequences consisting each of three profiles (forest soil, margin of fen, fen) were established to study the chemistry of the solid phase (soil pH, CEC, pedogenic Fe- and Al-oxides) and the soil solution in two small spring catchments on three dates during 1991 and 1992. Despite high acid inputs and acidified forest soils the pH of the spring outflow is near neutral, and the soil solid phases of the spring fens are not acidified. The results support the following hypothesis: Aluminum with its corresponding anion sulfate is leached with the soil solution into the water-saturated fens. Dissimilatory iron and sulfate reduction take place within the fen and generate alkalinity. Reduced iron either reacts with sulfide to form pyrite or migrates within the fen profile and precipitates in the uppermost, oxic horizons, consuming part of the generated alkalinity. Due to the higher pH values in the fens the incoming aluminum precipitates releasing acidity. The alkalinity generated exceeds the amount of acidity released by oxidation and precipitation of iron and the precipitation of aluminum. A balance of alkalinity consuming and alkalinity generating processes based on solid phases showed that iron and sulfate reduction can account for at least 67% of the neutralization of acidity entering the fen of one of the catchments. Due to shorter water retention times and higher discharge these processes are of minor importance in the other catchment. 相似文献
13.
工业副产品改良土壤酸度和铝毒的潜力 总被引：12，自引：0，他引：12
It is imperative to choose some low cost, available and effective ameliorants to correct soil acidity in southern China for sustainable agriculture. The present investigation dealt with the possible role of industrial byproducts, i. e., coal fly ash (CFA), alkaline slag (AS), red mud (RM) and phosphogypsum (PG) in correcting acidity and aluminum (Al) toxicity of soils under tea plantation using an indoor incubation experiment. Results indicated that CFA, AS and RM increased soil pH, while PG decreased the pHs of an Ultisol and an Alfisol. The increment of soil pH followed the order of RM > AS > CFA. All the industrial byproducts invariably decreased exchangeable Al and hence increased exchangeable Ca, Mg, K and Na and effective cation exchange capacity. RM, AS and lime decreased total soluble Al, exchangeable Al and organically bound Al. Formation and retention of hydroxyl-Al polymers were the principal mechanism through which Al phytotoxicity was alleviated by application of these amendments. In addition, the heavy metal contents in the four industrial byproducts constituted a limited environmental hazard in a short time at the rates normally used in agriculture. Therefore, the short-term use of the byproducts, especially AS and RM, as amendments for soil acidity and Al toxicity in acid soils may be a potential alternative to the traditional use of mined gypsum and lime. 相似文献
14.
Soil acidification and the importance of liming agricultural soils with particular reference to the United Kingdom 
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下载免费PDF全文 K. W. T. Goulding 《Soil Use and Management》2016,32(3):390-399
Soil acidification is caused by a number of factors including acidic precipitation and the deposition from the atmosphere of acidifying gases or particles, such as sulphur dioxide, ammonia and nitric acid. The most important causes of soil acidification on agricultural land, however, are the application of ammonium‐based fertilizers and urea, elemental S fertilizer and the growth of legumes. Acidification causes the loss of base cations, an increase in aluminium saturation and a decline in crop yields; severe acidification can cause nonreversible clay mineral dissolution and a reduction in cation exchange capacity, accompanied by structural deterioration. Soil acidity is ameliorated by applying lime or other acid‐neutralizing materials. ‘Liming’ also reduces N2O emissions, but this is more than offset by CO2 emissions from the lime as it neutralizes acidity. Because crop plants vary in their tolerance to acidity and plant nutrients have different optimal pH ranges, target soil pH values in the UK are set at 6.5 (5.8 in peaty soils) for cropped land and 6.0 (5.3 in peaty soils) for grassland. Agricultural lime products can be sold as ‘EC Fertiliser Liming Materials’ but, although vital for soil quality and agricultural production, liming tends to be strongly influenced by the economics of farming. Consequently, much less lime is being applied in the UK than required, and many arable and grassland soils are below optimum pH. 相似文献
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用自行设计的动力学装置,研究了酸性条件下Cu在可变电荷土壤表面的反应动力学吸附特征。结果表明,在酸性条件下,Cu吸附过程分为快反应和慢反应。从一级动力学方程拟合的参数可知,3种土壤的最大吸附量依次为砖红壤〉赤红壤〉红壤,Cu最大吸附量随酸度增加显著下降;用Elovich方程和抛物线扩散方程常数b值,解释离子的表观扩散速率,3种土壤的b值依次为砖红壤〉赤红壤〉红壤,且随酸度的增大而降低。从相关系数的比较看,Elovich方程在描述Cu的吸附数据比一级动力学方程和抛物线扩散方程要差。在Cu吸附过程中,pH为5．5和4．3时,红壤和赤红壤流出液中有质子释放,质子的释放可能涉及铜离子的水解;而砖红壤在pH为5．5有质子的释放,pH4-3时有质子的消耗。当原液pH为3.3和3．8时,都存在质子的消耗。3种土壤H＋的消耗过程有较大的区别,砖红壤上快速消耗H＋鱼-远远大于红壤和赤红壤。反应初期,H＋质子的消耗是快速反应,主要包括土壤交换阳离子的缓冲作用、土壤表面的质子化及硫酸根专性吸附释放的羟基中和H＋质子;而以后的反应中,H＋质子对矿物的溶解是一缓慢过程。 相似文献
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采用模拟方法对Cr^3＋的土壤脲酶效应进行了研究,结果表明,土壤pH对Cr^3＋的生态毒性有重要影响;酸性土壤脲酶受到显著抑制,活性及动力学特征参数与Cr^3＋浓度间达显著或极显著负相关,而且模型U=β0（/β1×C＋1）揭示其间机理为完全抑制,动力学则进一步细化为非竞争性抑制;获得土壤轻微和中度污染时的生态剂量ED10和ED50分别为50.59和865.7 mg.kg^-1;酸性土壤中脲酶活性、Vmax、k可作为土壤Cr^3＋污染的监测指标之一,而碱性土壤则反应不敏感,其随铬浓度增加,脲酶活性及动力学参数呈先增加后降低的规律性变化,总体变幅较小;两类土壤的差别可能主要是由于土壤环境引起了不同价态铬转变的缘故。 相似文献
17.
长白山地区不同植被下土壤酸度状况 总被引：3，自引：0，他引：3
The acidity regimes of representative soils on the north slope of the Changbai Mountains were examined through determinations of pH and pCa of the soil paste as well as in-situ determinations,For soils under broad-leaf forest or broad-leaf-Korean pine forest,the pH decreased from the litte to lower layers gradually until it did not change or decreased further slightly .For soils under coniferous of Erans birch forest,ther was a minimum in pH at a depth of 3-6 cm where the content of humus was high,The pCa increased gradually from the soil surface downward to a constant value.The lime potential(pH-0.5pCa) showed a similar trend as the pH in its distribution.For a given soil,the measured pH value of the thick paste,ranging from 4.5 to 5.5,was lower by about 0.5 units than the value determined by the conventional method with a water to soil ratio of 5:1 ,The pH determined in situ was even lower.It was found that there was a firly close relationship between soil acidity and the type of vegetation.The pH showed a trend of decreasing from soils under broda-leaf forest through broad-leaf-conifer mixed rorest and coniferos forest to Ermans birch forest,and the pCa showed an opposite trend in variation. 相似文献
18.
《Communications in Soil Science and Plant Analysis》2012,43(8):699-715
Abstract A buffer is generally a mixture of a weak acid and a salt of the same weak acid. Hence it can neutralize both acids and bases, and thus resists marked changes in pH of a system. Yet systematic change in pH of a buffer caused by addition of an acidic substance can be used to indicate the total acidity represented by the change in buffer pH. Since acid soil is itself a buffer, when it is added to a buffer mixture for the purpose of measuring its acidity or lime requirement (LR), the resulting double‐buffer suspension (soil‐buffer) is a relatively complex system. Much of the complication in interpreting the changes in buffer pH brought about by mixing soil and buffer stems from the facts: i) that much of the acidity is pH‐dependent, and ii) that quick‐test methodology involves reaction of only a fraction of the total soil acidity with the buffer. Marked change in relative amounts of H ions dissociating from the soil‐SMP‐buffer system at soil‐buffer pH 6.9 and above accounts for relatively wide variations between buffer‐indicated and CaCO3 incubation‐measured LR of low LR soils. Similarly, decreased reactivity of H+ in high organic matter soils and increased reactivity of H in acid‐leached soils cause errors in buffer‐indicated LR. Awareness of these principles helps avoid pitfalls of existing buffer methods, and has led to incorporation of the double‐buffer feature for improving the SMP method. 相似文献