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1.
综合论述了国内外风化成土速率计算模型的研究方法及其成果。质量平衡法主要通过比较土层与成土母质之间元素组成的差异来计算风化速率,其关键是准确测定两者中元素的组成;Barth模型法主要是在小流域范围内通过化学侵蚀过程对沉积物的形成或母岩成土速率进行估算,但在估算时需结合土壤形成的各种条件和自然环境特征、生产力水平,需进行较多的校正;PROFILE模型通过矿物与土壤溶液之间风化和释放盐基阳离子的速率测定风化速率,是目前计算土壤风化成土速率公认的方法;Sr同位素比值法的关键因素是Sr同位素在地壳风化系统,如植被、土壤交换场、河流水、大气沉降和矿物风化中的分配模式和标样的选择,在土壤数据和其它数据的获取方面存在较大困难,仅用于典型土壤的研究。  相似文献   

2.
模拟酸雨淋溶下强风化土壤矿物风化计量关系研究   总被引:5,自引:2,他引:3       下载免费PDF全文
矿物风化计量关系对于定量土壤酸化速率至关重要。我国亚热带地区矿物风化强烈,土壤的酸敏感性高。为获取强风化土壤在矿物风化过程中元素释放特征及其化学计量关系,选取花岗岩发育的富铁土,先用EDTA-乙酸铵溶液洗脱土壤胶体上吸附的盐基离子,然后采用改进的Batch法,将洗脱盐基土壤与未洗脱盐基土壤同时进行模拟酸雨淋溶。结果表明:(1)洗脱盐基土壤与未洗脱盐基土壤的盐基离子(K~+、Na~+、Ca~(2+)和Mg~(2+))释放情况存在显著差异,洗脱盐基后土壤在淋溶中释放的盐基来源为矿物风化,释放缓慢而平稳;(2)未洗脱盐基土壤在淋溶初期,盐基的释放量较大,随着淋溶的进行,释放量迅速下降,淋溶后期的释放速率与洗脱盐基土壤接近,这说明未洗脱盐基土壤在淋溶初期释放的盐基主要来源于阳离子交换过程,后期则主要来源于风化过程;(3)洗脱盐基土壤和未洗脱盐基土壤经酸雨淋溶释放的各盐基化学计量关系(K~+∶Na~+∶Ca~(2+)∶Mg~(2+))以及盐基离子与硅的化学计量关系(BC∶Si)差异较大,由于未洗脱盐基土壤受到阳离子交换的影响,因此只有洗脱盐基土壤的矿物风化计量关系可以作为定量估算土壤酸化速率的依据。  相似文献   

3.
植物根系强化黄土土层化学风化速率的作用   总被引:4,自引:0,他引:4  
黄土的风化主要为植物群落根系的物理作用及其所引起的生物化学作用。利用原状土柱淋滤实验装置及大型挖掘剖面壁法,在陕北黄土丘陵沟壑区进行野外实验研究,定量分析了林、草和农地土壤化学风化的剖面特征及动力学过程。研究结果表明,黄土土层的化学风化具有明显的垂直剖面分异特征,即风化速率随土层深度增加而递减。土壤化学风化的动力学过程可划分为急剧减小和稳定状态两个阶段。不同植被类型土壤风化速率及主导风化矿物组合类型的剖面差异主要受制于直径≤1mm的须根在剖面中的缠绕分布特征。植物根系对土壤风化作用的强化效应为油松林群落>白草群落;油松林群落和白草群落根系显著提高矿物风化速率的稳定土层深度范围分别为0~45cm和0~30cm,有效根密度分别在17根/100cm2和60根/100cm2以上。  相似文献   

4.
土壤中低分子量有机酸在物质循环中的作用   总被引:28,自引:1,他引:27  
本文为近三十年来有关土壤低分子量有机酸研究的扼要回顾。主要综述了森林和农业土壤中低分子量有机酸的组成特点、数量、来源及影响因素;侧重阐述了其在土壤矿物风化与形成、养分活化与迁移、土壤酸化与铝毒、以及与重金属相互作用等一系列物理和化学的影响机制;并提出了进一步研究需关注的问题。  相似文献   

5.
为探明生物结皮发育对风沙土盐基离子释放和矿物风化的影响,以进一步明确生物结皮的风化成土作用。以典型风沙土上发育的生物结皮为对象,通过模拟淋溶试验比较不同类型生物结皮(藻结皮、藻—藓混生结皮和藓结皮)覆盖土壤的盐基离子释放规律,探究盐基离子释放量随淋溶液pH的变化趋势,以及量化生物结皮覆盖土壤的矿物风化速率。结果表明:矿物风化反应阶段不同种类盐基离子的淋出量均较为平缓,生物结皮覆盖土壤的各盐基离子总淋出量表现为Ca2+>K+>Mg2+>Na+,其中藻结皮覆盖土壤的盐基离子总淋出量最高,比无结皮、混生结皮和藓结皮分别增加了112.0%,31.2%,27.1%。淋溶液pH显著影响盐基离子的淋溶释放,且其作用程度因离子种类和结皮类型而异。生物结皮覆盖提升了土壤的易风化矿物含量、风化程度和速率,藻结皮、混生结皮和藓结皮覆盖土壤的风化速率相比无结皮分别提升了61.2%,27.1%,152.6%,并且风化速率随淋溶液pH降低而提升。综上,生物结皮能显著促进风沙土矿物风化,其对风沙土改良和修复具有积极意义。  相似文献   

6.
庄翔宇  杨金玲  张甘霖  王艳玲 《土壤》2016,48(2):374-380
矿物风化过程中盐基离子释放遵从一定的化学计量关系,这种化学计量关系一般只能通过模拟实验来获取。本研究采用pH 7.0的EDTA-乙酸铵溶液将土壤中的交换性盐基离子完全洗脱出来,然后用Batch方法模拟不同pH溶液淋溶洗脱盐基和未洗脱盐基土壤,旨在消除土壤中交换性盐基离子的影响后更为准确地判断土壤矿物风化的盐基离子释放特征。结果表明:未洗脱盐基土壤的淋出液pH由3.73±0.14逐渐上升到4.23±0.06,主要原因是淋溶液中有高浓度的NH_4~+;洗脱盐基土壤矿物风化后淋出液pH从7.39±0.02逐渐下降到5.39±0.17,主要是由于土壤中可风化矿物减少。土壤交换性盐基离子会改变盐基离子释放特征、释放总量:未洗脱盐基土壤经酸雨淋溶后,各盐基离子释放均呈现急速下降后逐渐平缓的趋势,洗脱盐基土壤矿物风化后,K~+及盐基离子释放总量呈波动上升趋势,且盐基离子释放总量比未洗脱盐基土壤低。土壤交换性盐基离子的存在还会改变淋出液中的盐基离子化学计量关系:未洗脱盐基土壤的K~+︰Ca~(2+)︰Mg~(2+)︰Na+化学计量关系为11︰13︰4︰1(当量比),而洗脱盐基土壤为7︰2︰2︰1。K~+是盐基离子中风化释放量最多的,大部分K~+来自于土壤中云母的风化。因此,只有利用洗脱盐基土壤的盐基离子释放量才能准确计算矿物风化速率并获得准确的化学计量关系。土壤矿物风化作用随着淋溶液酸度增大而增强,但模拟一年降雨量的情况下,p H 3.5、4.5和5.5三种不同p H溶液对矿物风化后盐基离子的释放在实验期间没有显著性影响,较长时间后的差异性有待观察。本研究表明,可以通过预洗脱盐基土壤然后模拟酸雨淋溶的方法,观察矿物风化特征,特别是盐基离子释放的化学计量特征。  相似文献   

7.
以水为浸提溶液,研究了不同温度、pH和盐离子浓度条件对4种复合改性矿物包膜尿素养分释放的影响。结果表明,温度对复合改性矿物包膜尿素的养分释放速率有显著的影响,在15,25,35℃条件下,随着温度升高,水中养分溶出率均显著加快;盐浓度也是影响养分释放的重要因素,在5%,10%,20%尿素、氯化钾溶液中,随着尿素、氯化钾浓度的增大,复合改性矿物包膜养分释放速率明显降低;pH对复合改性矿物包膜尿素的养分释放的影响因包膜材料不同有所差异。  相似文献   

8.
植物根系分泌物与根际营养关系评述   总被引:47,自引:0,他引:47  
根系分泌物(root exudates,RE)主要有粘胶、外酶、有机酸、糖、酚及各种氨基酸。不同营养基因型的植物,RE级分明显不同,存在养分和环境胁迫时,植物通过增加粘胶、酶及某些有机酸的分泌量以适应变化的环境。RE也是植物改善根际营养环境的重要手段。RE可改善土壤物理结构,促进矿物风化、提高土壤CEC,影响土壤pH、土壤矿物表面吸附性能及土壤生物学性质。RE还存化根际土壤养分,促进植物对养分吸收  相似文献   

9.
岩石风化和土壤形成是地球表层物质循环的重要环节,了解岩石风化和土壤形成速率对土壤资源可持续利用和流域管理具有重要意义.本研究以位于我国亚热带的皖南花岗岩地区森林流域为例,通过野外监测其主要矿质元素输入输出量,应用流域中元素地球化学质量平衡原理,估算岩石风化和土壤形成速率.研究结果表明,在目前的降雨和酸沉降条件下,我国亚热带森林流域中,花岗岩的平均风化速率为0.696 t hm-2 a-1,土壤平均形成速率为0.598 t hm-2 a-1,所以需要经过2万年以上才能形成1 m厚的土壤.研究发现,大量输入土壤系统的H+由于被土壤风化和阳离子交换所消耗,径流水不至酸化,但是从长远来看,这会带来土壤的酸化.研究还表明根据当前的土壤形成速率,土壤允许流失量标准需要重新制定.  相似文献   

10.
[目的] 研究川中丘陵区桤木、柏木树种对紫色土风化与养分特征的影响,为该区水土流失防治与农业生产提供科学依据。[方法] 选择川中丘陵区万安小流域为研究区,以桤木、柏木为研究对象,运用野外调查、剖面挖掘采样等方法,研究桤木、柏木对紫色土剖面风化与养分的影响。[结果] ①桤木、柏木下土壤剖面分形维数分别为2.07和2.13,较对照分别提高了6.47%和9.03%,其中柏木对物理风化的提升幅度高于桤木。②桤木、柏木、对照剖面的化学风化程度差异并不显著,桤木、柏木生长对土壤剖面化学风化的影响较小。③桤木、柏木下土壤剖面综合肥力指数较之对照分别提高了14.08%和11.27%,其中桤木的提升效果优于柏木,其对有机质、全N、碱解N、速效K的提升尤为显著。④桤木、柏木根系分布密度与剖面分形维数、综合肥力指数均呈现较强的正相关关系(p<0.05),但与化学风化指数的相关关系并不显著(p>0.05)。[结论] 桤木、柏木在提升川中丘陵区紫色土物理风化速率与养分特征方面均发挥了积极的作用。  相似文献   

11.
Critical loads of acidity for mineral soils can be set according to the capacity of the underlying bedrock to replenish the base cations leached by acid deposition. Unfortunately, this relatively simple approach cannot be applied to peat, one of the most widely occurring soil types in the wetter, western areas of Europe. These organic soils depend on atmospheric deposition for their supply of base cations rather than mineral weathering. We aim to develop a critical load methodology for ombrotrophic peat, using a combination of field observations and laboratory experiments. Simulated rain has been applied to intact cores of peat to determine the key chemical processes governing the response of these soils to both increases and decreases in acid deposition. It is evident that peat does not behave as a simple ion exchanger; the complex reactions of decomposition, sulphate reduction, nitrate uptake and organic acid production also control the response to acid inputs. This paper looks at some of the results from these experiments and considers the implications for setting critical loads.  相似文献   

12.
Critical loads of acid deposition are exceeded in parts of the Southern Uplands of Scotland where base saturation in the topmost mineral horizons in many soils developed on greywackes and shales is <10%. Long-term weathering rates calculated by the elemental depletion method from nine soil profiles across a 200 km transect indicate losses of base cations in the range 4–31 meq m?2a?1. In every profile the most depleted base cation is Mg which is directly related to the weathering of chlorite which is often present at the 20–40% level in basal horizons but is often completely weathered out in E horizons. The second most depleted base cation is usually K, and this is clearly related to the weathering of mica to a vermiculitic mineral which, in the clay fractions, contains polymeric hydroxyaluminium in the interlamellar space if the soil pH is >4.3. The base cation least depleted is Ca and this is in sharp contrast to current weathering rates calculated from input-output budgets where Ca is the main base cation being exported. This discrepancy may be due to a contribution to the output from easily soluble Ca-bearing minerals (e.g. calcite) in narrow veins and fractures in the bedrock.  相似文献   

13.
The proton budgets of deciduous and coniferous forest ecosystems on volcanogenous regosols in Hokkaido, northern Japan, were studied by measuring the biogeochemical fluxes (atmospheric deposition, canopy leaching, vegetation uptake and leaching from soil) at each site during a three year period. The proton budgets were developed for individual compartments of the ecosystem: vegetation canopy, organic and mineral soil layers. At both sites, atmospheric S deposition was the dominant proton source in the vegetation canopy. In organic horizons, dissociation of weak acids (bicarbonate and/or organic acids) and vegetation uptake of base cations were the dominant proton sources, and the net mineralization of base cations was the dominant proton sink. Atmospheric acid deposition was almost neutralized in the forest canopy and organic horizon. At both sites, weathering and/or ion exchange of base cations and protonation of weak acids (mainly bicarbonate) were the dominant proton sinks in the mineral soil. In both organic and mineral soil, internal proton sources (mainly vegetation uptake of base cations and dissociation of weak acids) exceeded external proton sources, indicating that acid deposition was not the main driving force of soil acidification in the studied forest ecosystems.  相似文献   

14.
In addition to strong natural stresses forest ecosystems in the Kola Subarctic, Russia, receive high loads of sulphur and heavy metals from the nickel smelter. To estimate soil response to acid deposition we compared the soil field data along a pollution gradient and simulated time effects. Multivariate technique was applied to investigate spatial distribution of soil field data. Time response of soils to acid deposition was evaluated with the SMART model. According to field observations there is no evidence for strong soil acidification effects close to the smelter. Concentrations of exchangeable Ca and base saturation increase, while acidity decrease in lower soil mineral horizons towards the pollution source. However, some features seem to reflect the early stages of the started acidification. Most soil profiles have low pH values. Despite increasing of exchangeable Ca and Mg towards the smelter in lower mineral horizons due to geological inheritance, they do not reveal the same trends in the upper ones. Concentration of exchangeable K in organic horizons decreases towards the smelter, thus confirming the starting acidification. As result, exchangeable base cations are depleted in the considerable part of shallow soil profiles. According to model simulation the present acid load does not effect considerably on forest soils in background areas, however, dramatic shift in soil chemistry near the smelter is expected within several decades. Due to low pool of exchangeable base cations and low weathering rate continued acid deposition can lead to increased soil acidification and nutrient imbalance.  相似文献   

15.
In spruce and beech stands, mineral budgets for a rotation period were calculated from measured element fluxes. The release of base cations by mineral weathering was calculated with the steady state soil chemistry model PROFILE. The calcium release rate by weathering of the mineral fine earth was extremely low. For the period of one rotation, mineral weathering cannot provide enough Ca to compensate timber harvesting and leaching. Forest sustainability depends strongly on the amounts of Ca gained from deposition and lost by biomass removal. Magnesium was supplied by atmospheric deposition and mineral weathering. Calculated weathering rates were close to present soil losses. However, as the model assumes that all dissolution reactions are congruent, the computed release rate of Mg from illite might be too high. Main inputs of K to the soil solutions were primarily attributed to canopy leaching and litterfall in upper horizons and to mineral weathering in deeper horizons. The cation budget of the beech stand was much more equilibrated than that of the spruce stand. Given possible changes in silviculture and deposition chemistry, the sustainability of the present stands is rather improbable with respect to their mineral supply.  相似文献   

16.
贡嘎山海螺沟冰川退缩区土壤序列矿物组成变化   总被引:2,自引:1,他引:1  
阐明土壤中矿物随时间变化的机制是理解矿物风化和土壤发育的基础。利用X射线衍射法对贡嘎山海螺沟冰川退缩区土壤矿物组成随成土作用时间变化进行了定量分析。结果表明,冰川退缩区成土母质的矿物组成同质性较高,以硅酸盐矿物为主(约90%),包括:斜长石(28.5%)、石英(24.5%)、黑云母、钾长石、普通辉石、角闪石、绿泥石、蛭石;并有少量碳酸盐矿物,如方解石(8%)、白云石(2.3%);以及磷酸盐矿物磷灰石(2.1%)。退缩区土壤的矿物组成总体呈新发育土壤特征,随着成土年龄的增加,方解石逐渐被风化成为草酸钙石,角闪石、黑云母、磷灰石和绿泥石含量逐渐降低,长英质矿物的相对含量有所增加。成土作用中矿物组成的变化受植被原生演替和土壤p H的影响,快速发育的植被导致土壤p H迅速降低,风化程度增强。  相似文献   

17.
The majority of Scottish upland soils are particularly sensitive to acid deposition because of their low weathering rates. The compositions of the exchangeable base cations of such soils in the United Kingdom are dominated by sea salt inputs rather than by mineral weathering inputs of base cations. Catchments with low mineral weathering rates are also those particularly susceptible to freshwater acidification. Therefore, catchments exhibiting a high sea salt effect should also exhibit the most acid waters under base flow and storm flow conditions. A field evaluation study based on 61 catchments in NE Scotland has shown that this is indeed the case. River water pH under both base flow and high flow conditions is correlated stronhly with the relative contribution of Na+ to the sum of Ca2+, Mg2+ and Na+. From these results, an attempt is being made to produce a quantitative signature of weathering for the soils within the catchment upstream of the sampling point. Representative soil samples from the LFH, AE, B and C horizons and on 4 different parent materials have been obtained from the surrounding catchments to validate the above results for associated soil solutions. Sampling took place on upland moorland podzols under Calluna vulgaris. Tension lysimeters were used to sample the soil solutions so that their chemistry could be compared with that of the relevant river water.  相似文献   

18.
Soil response to acid and sulphur inputs is influenced largely by the soil's physico‐chemical properties. We studied the effects of such depositions in two types of Andosols exposed to volcanogenic emission (Masaya, Nicaragua), namely Eutric Andosols rich in allophanic constituents, and Vitric Andosols rich in volcanic glass. Small mineral reserves and large contents of secondary short‐range ordered minerals indicate a more advanced weathering of the Eutric than the Vitric Andosols. Strong correlations between soil specific surface and oxalate‐extractable Al, Si and Fe contents highlight the predominant contribution of short‐range ordered minerals to surface area. Both types of Andosols showed a decrease in pH upon acid input. Sulphur deposition increased the soil's S content to 5470 mg S kg?1. However, the acid neutralizing capacity of the soil solid phase (ANCs) was not significantly affected by the acid and S inputs. Non‐exchangeable (mineral reserve) and exchangeable cations and total contents of sulphur and phosphorus dictate most of the ANCs variation. In the Vitric Andosols, mineral reserves contributed up to 97% to these four additive pools, whereas the exchangeable cations accounted for 1–4%. In the Eutric Andosols, the contribution of mineral reserves was less (71–92%), but the exchangeable cation content was greater (1–20%), whereas the contribution of sulphur and phosphorus was significant at 1–15% and 2–7%, respectively. The main process involved in H+ consumption is mineral weathering in Vitric Andosols and ion exchange in Eutric Andosols.  相似文献   

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