四苯硼钠溶液中含钾矿物非交换态钾的释放特性研究

含钾矿物的全钾含量、非交换态钾总量以及非交换态钾的释放速率因矿物种类而异,且3种参数之间没有必然的相关性。供试5种含钾矿物非交换态钾总量由高到低的顺序是:金云母 5.19% 黑云母3.08% 蛭石2.01% 白云母1.18% 钾长石0.24%,占各矿物全钾的比例分别为:58.4% 、99.7% 、62.5% 、14.2% 和4.98% ,平均达48%。选择较弱提取力的四苯硼钠溶液进行非交换态钾的释放特性研究,5种矿物非交换态钾3d释放累积量顺序为:黑云母 蛭石 金云母 白云母 钾长石;非交换态钾平均释放速率也表现为同样的顺序。上述5种矿物在弱提取力的四苯硼钠溶液中释放3 d,非交换态钾的平均释放速率分别为5.99、2.34、0.52、0.22和0.17 mg/(kgmin),差异明显。如何根据非交换态钾的释放量和释放速率来综合评价矿物钾的生物有效性是未来研究中需要明确的问题。     

不同提取方法土壤非交换性钾释放动力学及其速率的研究

采用Ca2+饱和土壤的 0.50molL-1硝酸、0.0 1molL-1草酸和氢质阳离子交换树脂恒温连续提取法 ,利用Elovich和二级动力学模型 ,结合生物吸钾试验 ,研究探讨了描述土壤非交换性钾释放及其速率较为理想的连续提取法及其动力学模型。研究结果表明 ,氢质树脂提取法的Elovich模型描述非交换性钾释放及其速率的效果较为理想 ,拟合方程的相关系数达极显著水平(r =0.982～ 0.996 ) ;不同时间非交换性钾累积释放量的计算值与实测值的标准差最小 (S =1.335～2.480 ) ;通过速率方程计算的不同时间非交换性钾释放速率与黑麦草吸收的非交换性钾数量的相关性也最为密切 (r =0.944～ 0.963) ,故氢质阳离子交换树脂连续提取法结合Elovich模型是描述土壤非交换性钾释放及其速率较为理想的组合方法。以伊利石为主的 2、3和 8号土壤非交换性钾释放速率明显高于其它以高岭石或蒙脱石为主的供试土壤     

北方主要土壤对当季作物的供钾能力

本文研究了我国北方农区主要土壤对当季作物的供钾能力.结果表明,供试土壤对当季作物的供钾能力的总趋势是,取自西北的土壤较高,而取自华北和东北的土壤较低.土壤速效钾可利用部分的大小及其最低值出现的时间可以较好地反映土壤对当季作物的供钾状况.供试土壤对当季作物的供钾能力是速效钾和非交换性钾共同作用的结果.     

菜园土壤有效钾提取方法比较研究——以重庆地区为例

研究菜园土壤有效钾的测定方法,为蔬菜合理施用钾肥提供理论依据。以36个莴笋钾肥田间试验的产量及吸钾量为参比标准,采用7种方法 (醋酸铵法、ASI法、Mehlich3法、冷硝酸法、四苯硼钠法1、四苯硼钠法2和沸硝酸法)测定土壤有效钾含量。结果表明,土壤有效钾含量以沸硝酸法四苯硼钠法2四苯硼钠法1冷硝酸法Mehlich3法醋酸铵法ASI法。7种测定方法测得的土壤有效钾含量间呈不同程度正相关,均具有评价土壤钾素有效性的潜力。四苯硼钠法1和四苯硼钠法2测得的土壤有效钾含量与无肥区占施钾区莴笋相对产量(RY_(CK))、缺钾区占施钾区莴笋相对产量(RY_(NP))、无肥区占施钾区莴笋相对吸钾量(RUK_(CK))的相关性均达显著水平,即其测得的土壤钾素的生物有效性均较好。综合而言,在所试验土壤地区,四苯硼钠法1和四苯硼钠法2均是评价菜园土壤当季钾素有效性的较好方法,其中以四苯硼钠法1更好。     

不同提取方法测定的土壤钾的有效性比较研究

以122个油菜钾肥田间试验的籽粒产量和植株吸钾量为标准,分别采用1 mol L-1中性醋酸铵、1 mol L-1沸硝酸和0.2 mol L-1四苯硼钠3种浸提剂测定试验基础土壤的钾素含量,并按浸提剂种类和速效钾、缓效钾将其分类,通过相关性分析探索土壤有效钾的准确测定方法,并建立与之对应的土壤钾素丰缺指标。研究结果表明,不同方法的提取能力有所不同,沸硝酸钾含量四苯硼钠钾含量醋酸铵钾含量。用醋酸铵法和四苯硼钠法测得的土壤钾素的生物有效性均较好,其中又以四苯硼钠法更好。长江流域冬油菜区醋酸铵法浸提的土壤钾素"低"、"中"、"高"和"极高"指标分别为45 mg kg-1、45~115 mg kg-1、115~190mg kg-1和190 mg kg-1;四苯硼钠法浸提的土壤钾素"低"、"中"、"高"和"极高"指标分别为125 mg kg-1、125~415 mg kg-1、415~755 mg kg-1和755 mg kg-1。综合结果表明四苯硼钠法和醋酸铵法测得的土壤钾素含量与油菜相对产量和相对吸钾量间呈极显著相关关系。据此建立的土壤钾素丰缺指标可以用来指导长江流域油菜的测土配方施肥,另外此区域应该重视并合理的施用钾肥。     

土壤—作物系统钾素动力学模型及其参数研究

基于生态学的Lotka Volterra模型 ,在土壤—作物系统中提出一个新的土壤钾素动力学方程。盆栽试验表明 ,该模型能很好地拟合花生一个生长周期内土壤缓效钾和速效钾的动态变化。吸钾量实测结果表明 ,花生不同生育期吸钾量符合Logistic模型。结合上述 2个模型 ,分别求出矿物钾最大释放速率常数Kmm、缓效钾最大释放速率常数Krm和速效钾最大供钾速率常数Kam。相关分析表明 ,Kam与花生当季吸钾量、生物学产量和荚果产量以及Krm与花生当季吸钾量有显著水平以上的对数正相关。Krm和Kam可作为评价土壤当季供钾能力的速率指标。     

土壤矿物钾的释放及其在植物营养中的意义

本文对土壤钾的形态、矿物钾释放的影响因素及钾的固定、土壤含钾矿物与土壤供钾能力间关系、矿物钾的植物有效性进行了综述 ,表明土壤钾素从有效性的角度进行划分时 ,不能仅把速效性钾和1mol/L热硝酸提取的缓效性钾列为作物吸钾的主要来源 ,而忽视矿物钾的作用 .     

施肥方式对砂姜黑土钾素利用及盈亏的影响

以砂姜黑土长期施肥试验为平台,研究砂姜黑土冬小麦—夏大豆轮作系统下作物钾素吸收量、钾素回收率、土壤钾素盈亏量和速效钾含量的演变特征,探明土壤速效钾与外源钾投入、土壤累积钾盈亏的响应关系,分析不施肥(CK)、常规化肥(CF)、化肥+麦秆(SCF)、化肥+猪粪(PCF)、化肥+牛粪(CCF)等施肥方式对土壤钾素利用及盈亏的影响,以期探寻砂姜黑土地区高产高效的施钾方式。结果表明:29 a作物钾素平均回收率在55.1%~66.1%,高低顺序为CCFPCFSCFCF。土壤累积钾盈亏与土壤速效钾增量呈显著线性关系(p0.05),土壤中钾素每盈余100 kg hm-2,CF、SCF、PCF和CCF处理土壤速效钾含量分别增加1.4、1.8、2.3和15.8 mg kg-1;土壤钾素投入量与速效钾含量呈显著线性关系(p0.05),CF处理每投入钾100 kg hm-2,土壤速效钾含量增加0.4 mg kg-1,而SCF、PCF和CCF处理每投入钾100 kg hm-2,土壤速效钾含量分别增加0.5、0.6和4.3 mg kg-1,这说明适当增施有机肥可提升土壤钾素的供应能力。综上所述,投入有机物料是影响土壤钾素利用的重要调控措施,长期增施有机肥可提高作物钾素回收率以及土壤中盈余的钾素向速效钾的转化能力,本试验条件下以增施牛粪效果最好,猪粪和秸秆次之。因此,砂姜黑土小麦—大豆轮作系统下秸秆养畜过腹还田是实现作物高产高效的一种推荐施钾方式。     

小麦-玉米轮作周期内土壤钾素与作物吸收钾动态变化研究

通过田间定位试验,研究了不同施肥条件下作物吸收与土壤速效钾动态的关系。研究结果表明:作物对土壤钾素的吸收量随施钾量的增加而增加,土壤速效钾在小麦-玉米轮作周期内呈现出"M"型动态变化。土壤速效钾的这种动态变化是作物吸收、施肥、气候等多种因素共同作用的结果。施用钾肥可以提高轮作周期内的土壤供钾能力,减轻土壤钾素消耗。     

解钾细菌C6X对不同富钾矿物含量土壤钾素迁移的影响

为了改善黄土高原地区煤炭开采引起土壤质量急剧退化的现状,该文以玉米为供试植物,通过日光温室短期盆栽的方式,系统研究解钾细菌C6X和玉米生长对土壤钾素迁移的影响.结果表明:1)玉米生长条件下,解钾细菌在富钾矿物质量分数45％上层土壤(0～20 cm)中对速效钾增量的促进作用最佳.2)解钾细菌和玉米生长协同提高上层土壤钾素固定能力,缓效钾增量在土壤富钾矿物质量分数68％为最大值.3)解钾细菌和玉米生长协同促进土壤钾素上移能力,在富钾矿物质量分数45％水平,土壤上移速效钾呈最大值;同时,解钾细菌促进土壤上移速效钾和玉米钾素积累量二者趋于线性稳定,利于土壤钾肥长期管理.因此,解钾细菌和玉米生长协同促进土壤钾素的释放和固定,并促进土壤钾素上移.     

土壤非交换态钾与结构态钾能够区分吗？

Nonexchangeable K (NEK) is the major portion of the reserve of available K in soil and a primary factor in determining soil K fertility. The questions of how much NEK is in soils and how to quantify total NEK in soils are so far still unclear due to the complicated effects of various minerals on K fixation. In this study, the NEK in 9 soils was extracted with sodium tetraphenylboron (NaBPh₄) for various time periods longer than 1 d. The results showed that the NEK extracted by NaBPh₄ gradually increased with time, but showed no more increase after the duration of extraction exceeded 10--20 d. As the temperature increased from 25 to 45 ^oC, the duration to obtain the maximum extraction of NEK was reduced from 20 to 10 d, and the maximum values of NEK released at both temperatures was almost the same for each soil. The maximum NEK (MNEK) of the 9 soils extracted by NaBPh4 varied from 3 074 to 10 081 mg kg^-1, accounting for 21%--56% of the total soil K. There was no significant correlation between MNEK released by NaBPh₄ and other forms of K, such as NH₄OAc-extracted K, HNO₃-extracted K and total K in soils, which indicates that NEK is a special form of K that has no inevitable relationship to the other forms of K in soils. The MNEK extraction by NaBPh₄ in this study indicated that the total NEK in the soils could be differentiated from soil structural K and quantified with the modified NaBPh₄ method. The high MNEK in soils made NEK much more important in the role of the plant-available K pool. How to fractionate NEK into different fractions and establish the methods to quantify each NEK fraction according to their bioavailability is of great importance for future research.     

Fixation of radiocaesium traces in a weathering sequence mica → vermiculite → hydroxy interlayered vermiculite

Radiocaesium fixation in soils is reported to occur on frayed edge sites of micaceous minerals. The weathering of mica in acid soils may therefore influence the Cs⁺ fixation process and thereby the mobility of the radiopollutant. We produced a laboratory weathering model biotite → trioctahedral vermiculite → oxidized vermiculite → hydroxy interlayered vermiculite (HIV) and quantified the Cs⁺ fixation of each mineral both in a fixed K⁺–Ca²⁺ background and in acid conditions. The transformation process was achieved through K depletion by Na-tetraphenylboron, oxidation with Br₂ and Al-intercalation using NaOH and AlCl₃. In a constant K⁺–Ca²⁺ background, vermiculite fixed 92–95% of the initial ¹³⁷Cs⁺ contamination while biotite and HIV fixed only 18–33%. In acid conditions, the interlayer occupancy by either potassium (biotite) or hydroxy-Al groups (HIV) strongly limited Cs⁺ fixation to 1–4% of the initial ¹³⁷Cs⁺ contamination. Cs⁺ fixation occurred on vermiculitic sites associated with micaceous wedge zones. Though both oxidized and trioctahedral vermiculites fixed similar Cs⁺ amounts in a constant K⁺–Ca²⁺ background (92–95%), the oxidized vermiculite retained much more radiocaesium in acid conditions (78–84% against 54–59%), because of its dioctahedral character.     

Effects of organic matter and calcium on soil structural stability

The cationic bridging effect of the calcium ion (Ca²⁺) and the flocculating ability of clay and organic matter are crucial in the formation and stability of soil aggregates. They are therefore likely to influence the soil's saturated hydraulic conductivity ( K _s). We tested the individual effects of these factors on aggregate stability and related hydraulic properties, and studied the influence of clay mineralogy also. Samples from the surface (0–10 cm) of three contrasting soils in Trinidad were used. The soils were treated with three levels of Ca²⁺ and three levels of organic matter in a 3 × 3 × 3 factorial design and incubated for 14 days. Both aggregate stability and saturated hydraulic conductivity were influenced by all factor combinations. Interactions between soil type and Ca²⁺ revealed the importance of polyvalent cations in aggregate stability of soils with low activity minerals. The influence of organic matter varied with quantity; the more there was, the more stable the soil became, particularly in the soil containing little clay. Clay dispersion and slaking of expanding minerals occurred even with large additions of Ca²⁺ and organic matter, emphasizing the overall influence of mineralogy in determining the response of soils to stability treatments.     

The nature and kinetics of organic matter release from soil by salt solutions

Laboratory experiments in soil columns were performed to study the influence of dissolved salts on the amount and composition of organic matter (OM) released from soil. Samples of two surface soils from former wastewater infiltration sites were leached with solutions containing dissolved salts (NaH₂PO₄, NaNO₃, CaCl₂) and by deionized water. The NaH₂PO₄ solution induced strongest release with 0.6% of soil organic carbon (C_org) with 700 ml for 100 g of soil, while CaCl₂ released the least, summing to 0.1–0.2% of C_org. The OM released was characterized by UV absorbance (aromaticity), ultrafiltration (molecular size distribution) and solid-phase extraction (polarity). The results suggest that CaCl₂ preferentially released readily soluble OM. For the other solutions we assume solubilization by enhanced electrostatic repulsion (water), sodium exchange (NaNO₃), and sodium exchange and calcium decomplexation and displacement of sorbed organic anions (NaH₂PO₄) to be the major mechanisms of release. In all experiments a phase of spontaneous desorption was observed, followed by a phase of steady-state desorption. Activation energies for steady-state release were estimated from kinetic investigations and suggest that the release is controlled by diffusion towards the phase boundary. These investigations emphasize the influence of dissolved salts on the nature and quantity of organic matter released from soil. The method presented seems able to characterize soil organic matter with respect to its availability and its mode of association with the soil matrix.     

1-Aminocyclopropane-1-carboxylate-dependent biosynthesis of ethylene in soils of different texture

1-Aminocyclopropane-1-carboxylic acid (ACC) is an established intermediate in methionine-derived ethylene (C₂H₄) biosynthesis in plants. This study reports concentration-dependent ACC-derived C₂H₄ biosynthesis in two differently textured soils (silt clay loam and fine loam). The gas chromatographic analysis showed that addition of up to 10 mmol l⁻¹ ACC significantly stimulated C₂H₄ biosynthesis in both soils while no C₂H₄ was detected in sterilized soils amended with a sterilized ACC solution. Kinetic analysis revealed that the ethylene-forming enzyme (EFE)-mediated reaction was more linear in the silt clay loam (R²=0.992) than in the fine loam soil (R²=0.668) when reaction velocity (V) was plotted against substrate concentration [S] that ranged from 2.5 to 10 mmol l⁻¹. Within this range of [S], a first-order reaction was observed. Amendment of soils either with glucose (C source) or NH₄NO₃ (N source) strongly inhibited ACC-dependent C₂H₄ production. Maximum C₂H₄ production in both soils was recorded at a substrate concentration of 10 mmol l⁻¹ when reaction mixture was maintained at a pH of 7.0 and incubated for a period of 120 h at 35 °C while shaking. Among the nine trace elements tested, seven showed a positive effect on ACC-dependent biosynthesis of C₂H₄ in both soils, while Fe(III) and Ag(I) inhibited the biotransformation of ACC into C₂H₄. However, three of the five tested electron complexes, added at 1.0 mmol l⁻¹, had inhibitory effects on ACC-derived C₂H₄ biosynthesis while mannitol and hydroquinone stimulated C₂H₄ production in both soils. The addition of antibiotics (1.0 mmol l⁻¹) to ACC-amended soils significantly reduced C₂H₄ production in both soils. Overall, C₂H₄ production from ACC was greater in the silt clay loam soil than in the fine loam soil. Knowledge of the factors affecting C₂H₄ biosynthesis in soil could be of great significance since even very low concentrations (ppb) of C₂H₄ in the root environment are known to affect plant growth dramatically.     

Release of potassium from some benchmark soils of India

Release of potassium from 15 surface samples of benchmark Alluvial, Red and Black soils of India to 0.01 M solutions of BaCl₂, CaCl₂, NH₄Cl and NaCl was studied in soils either untreated or pretreated with 5 × 10⁻³ M KCl. In the untreated soils, the efficacy of the extractants declined in the sequence: BaCl₂ > NH₄Cl > CaCl₂ > NaCl. Cumulative K-release was greatest from Black soils, followed by Red and Alluvial soils. From soils pretreated with 5 * 10⁻³ M KCl, more K was released than retained, and more 'native' K was released than that from untreated soils. Increase in the release of 'native' K decreased in the sequence: Red > Alluvial > Black soils. The amounts of surface and internal K, desorption rate constants and parabolic diffusion constants were calculated from K release to the various electrolytes.     

Correlations between extractable Na, K, Mg, Ca, P & N from fresh and dried samples of two Aquults

Significant increases in extractable ions resulted from air-drying and grinding samples of two infertile Aquults. Effects of the sample preparation differed markedly between ions and between the two soils. Regression equations were calculated to predict extractable ions in dried, ground samples from extractable ions in fresh, unground samples and the relationships were compared between the two soil series. Regressions were significantly different between soils for extractable PO³₄, Mg⁺⁺, and K⁺, but not for Ca⁺⁺ and Na⁺. Extractable NH ⁺₄ and NO-₃ in fresh, unground samples were not correlated with those in air-dry, ground samples of either soil. Differences in response to preparation between soil types appeared to be related to the oxidative status of these soils in the field, wherein constituents of more poorly-drained soils may be less stable to the oxidizing conditions of air-drying and grinding. Such complexities suggest that effects of sample preparation should be considered when interpreting soil nutrient data for studies of forest nutrient cycling and forest soil fertility.     

用稀悬液Wien效应测量法来研究重金属离子与水稻土的相互作用

Interactions of three heavy metal ions, Cu²⁺, Cd²⁺, and Pb²⁺, and, for comparison, Na⁺ with electrodialytic clay fractions (less than 2 μm in diameter) of four paddy soils as well as a yellow-brown soil as a control soil were evaluated based on measurements of the Wien effect in dilute suspensions with a clay concentration of 10 g kg^?1 in four nitrate solutions of 2 × 10^?4/z mol L^?1, where z is the cation valence, and a nitric acid solution of 3 × 10^?5 mol L^?1. Field strengths ranging from 15 to 230 kV cm^?1 were applied for measuring the electrical conductivities (ECs) of the suspensions. The mean free binding energies between the various cations and all of the soils determined from exchange equilibrium increased in the order: Na⁺ < Cd²⁺ < Cu²⁺ < Pb²⁺. In general, the ECs of the suspensions in the sodium nitrate solution were smaller than those of the suspensions in the heavy metal solutions because of the lower electrophoretic mobility of sodium compared to the divalent cations. In terms of relative electrical conductivity-field strength relationships, relative electrical conductivity (REC) of suspensions containing various cations at field strengths larger than about 50 kV cm^?1 were in the descending order: Na⁺ > Cu²⁺ > Cd²⁺ > Pb²⁺ for all tested soils. A characteristic parameter of the REC-field strength curves, ΔREC₂₀₀, REC at a field strength of 200 kV cm^?1 minus that at the local minimum of the concave segment of the REC-field strength curves, characterized the strength of adsorption of the cations stripped off by the applied strong electrical field, and for all soils the values of ΔREC₂₀₀ were generally in the order: Na⁺ < Cu²⁺ ≤ Cd²⁺ ≤ Pb²⁺.     

Acid rain, cation dissolution, and sulphate retention in three tropical soils

Surface and subsurface samples of three tropical soils were examined with respect to their interaction with dilute solutions of sulphuric acid of pH 3. In calcareous clayey samples with a large cation exchange capacity the H⁺ was replaced by an equivalent concentration of metal cations which remained in solution along with SO^2-₄ as counterion. In a coarse-textured neutral soil with small cation exchange capacity, there was less chemical interaction and a major proportion of the H₂SO₄ remained unchanged in the equilibrium solution. Another soil exhibited considerable ability to remove SO^2-₄ from solution and, therefore, the total ionic concentration was greatly reduced. Other samples showed behaviour which was intermediate to these three types.
The ability to adsorb SO^2-₄ is one of the most important factors which determines the nature of the interaction of soil with dilute sulphuric acid. This ability was shown to be affected by the content of hydrous sesquioxides and organic matter in these soils.     

The reactions of cadmium with calcium carbonate surfaces

The reaction of cadmium with calcite was studied with 10⁻⁶–10⁻²M Cd²⁺ using 4g CaCO₃ and 50 ml solution. The calcite-water suspension was equilibrated for 2 d before adding Cd(NO₃)₂. The CaCO₃ surface has a high affinity for Cd and at < 1 μmol g⁻¹ a linear adsorption isotherm (C-type) describes the reaction, whereas precipitation of CdCO₃ on calcite predominates at higher Cd additions. In the latter case pH decreased and solutions were undersaturated with respect to CaCO₃ indicating that CdCO₃ prevented the CaCO₃ surface from reacting with the acidity generated from CdCO₃ precipitation. The data for low Cd additions suggests that an ideal surface solid solution is formed between CdCO₃ and CaCO₃ and the Thorstenson and Plummer equation expressing the pIAP values of surface solid solutions is valid. Equilibrium was attained for low Cd additions in several minutes, whereas precipitation was a slow process; at the changeover point distinction between the two processes is difficult. The reacting surface area calculated from the maximum adsorption of Cd is 0.5-1.0 times that measured by the BET method.
The Cd-reacting surface areas of four natural calcareous minerals were much less than those found by the BET method which includes the surfaces of other minerals present. The Thorstenson and Plummer equation may be a useful way to relate solution composition and carbonate-adsorbed Cd in contaminated soils.