区域性土壤流失预测方程的初步研究

应用我国南方花岗岩侵蚀红壤区的径流小区观测资料,采用数值分析方法推导出适合花岗岩侵蚀红壤区,计算各次降雨吋土壤流失量和年土壤流失量方程:A₁=4·y_s·K·LS;并利用野外调查量测资料,推导出适合长江三峡低中山区的土壤流失方程:A₂=(152.5D-1016)·R·LS·C^-2.3利用上述方程可以预测特定区域的土壤流失量。     

土壤对磷的吸持特性及其与土壤供磷指标之间的关系

本试验测定了浙江省几种代表性土壤对磷的等温吸持特性。实测值与Frundlich、Langmuir、两项式Langmuir和Temkin方程都很符合,相关系数变化范围在0.919-0.999之间,都达到极显著水平。其中以简单Langmuir等温式与本实验资料最为吻合。从Langmuir方程得到的土壤吸持特性值(k×q_m)被认为与土壤供磷特性有关。几种供试样品的(k×q_m)值是:针铁矿21100>黄筋泥4218>黄筋泥田991>青紫泥798>粉泥田660>高岭石485>老黄筋泥田423>泥质田298。根据土壤吸持特性值以田菁进行盆栽试验来估算作物磷肥需要量,结果表明,供磷强度0.3ppm P基本能满足田菁早期生长的需要。为使不同土壤达到相同的供磷强度,(k×q_m)值大的土壤要求更高的有效磷值。供试土壤的几种磷素指标:E值、Bray1-P值和(NaOH-Na₂C₂O₄)法值对(k×q_m)值的变化比较敏感,而EDTA-P和Olsen-P指标对(k×q_m)值的变化较为迟钝。     

采石废弃地弃渣与农田土混合土壤粒径特征及水文效应

探究弃渣与农田土不同混合比例下重构土体粒径特征和水文效应的差异,对于提高采石废弃地重构土体的结构稳定、水资源高效利用以及资源利用化具有重要意义。以采石场弃渣和农田土为重构基质,以0∶10(C₁),3∶7(C₂),5∶5(C₃),7∶3(C₄),10∶0(C₅)体积比例混合,采用野外土柱模拟方法,探究不同配比下土壤粒径特征和水文效应的差异。结果表明:(1)不同配比下弃渣含量越高,砂粒比重越大、黏粒和粉粒比重越小,砂粒比重最大为61.50%,分散度、偏度、峰态等群体特征参数变化分别为降低、升高、升高,不均匀系数显著降低,曲率系数在1~3波动,分形维数呈不显著降低趋势,土体结构朝不稳定方向变化。(2)混合土壤弃渣含量增大会引起容重变大、毛管孔隙和总孔隙数量减少、非毛管孔隙数量增加等土壤孔隙方面以及田间持水、毛管持水、饱和持水三者下降等土壤持水性能方面的变化,同时,初始入渗、稳定入渗、平均入渗等速率变化以及累计入渗量基本呈增加趋势,稳渗用时呈波动式变化。不同配比下土壤入渗模型拟合R²≥0.856,RRMSE≤0.153,整体上模型拟合效果较好,灰色关联分析结果表明,C₅入渗性能最好。(3)弃渣∶农田土以3∶7体积比例混合后的土壤在粒径结构和水文效应2个方面评价结果中表现最佳。[JP]     

磁化水处理对镉胁迫下欧美杨幼苗光合及生长特性的影响

为探讨磁化水灌溉处理在促进植物生长、提高植株重金属耐受性方面的作用机制,本研究采用随机区组试验设计,研究了镉胁迫（0 μmol·L^-1、50 μmol·L^-1、100 μmol·L^-1）下磁化水灌溉处理对1 a生欧美杨''I-107''光合特性、叶绿素荧光动力学参数及生长特性的影响。结果表明：1）镉胁迫会显著降低植株高生长和根茎叶干物质量;低浓度（50 μmol·L^-1）镉处理促进根系直径及体积增大（P<0.05）,高浓度（100 μmol·L^-1）则会抑制根系各形态参数;镉胁迫下欧美杨叶绿素b和类胡萝卜素含量分别降低12.50%、43.24%和19.27%、46.37%（P<0.05）,净光合速率（P_n）、蒸腾速率（T_r）、胞间二氧化碳（C_i）分别降低13.68%和33.68%、8.07%和27.81%、5.00%和14.99%（P<0.05）,同时,PSⅡ潜在活性（F_v/F_m）、最大光化学速率（F_v/F_o）、光合性能指数（PIabs）和量子产额（φ_Eo）均有不同程度降低。2）磁化水灌溉提高镉胁迫植株高生长及根茎叶干物质量,增加植株根系长度及表面积;同时,叶绿素a、叶绿素b和类胡萝卜素含量在0 μmol·L^-1和100 μmol·L^-1镉胁迫下分别提高16.99%、40.20%,8.67%、39.10%和17.32%、50.52%（P<0.05）;G_s、C_i及WUE显著升高,T_r则降低24.20%、23.33%、12.06%（P<0.05）;另外,F_v/F_m、F_v/F_o、PIabs显著升高（P<0.05）。综上所述,磁化水灌溉处理有助于提高镉胁迫下欧美杨幼苗光合色素含量,维持光合机构功能,增强光合碳同化速率,减轻镉胁迫对植株生长发育的抑制。     

生物质炭对土壤N2O消耗的影响及其微生物影响机理

生物质炭在温室气体减排方面具有很大的发展前景,它不仅能实现固碳,对于在大气中停留时间长且增温潜势大的N₂O也能发挥积极作用。本研究采用室内厌氧培养试验,按照生物质炭与土壤质量比（0、1%和5%）加入一定量生物质炭,土壤重量含水率控制在20%。利用Robotized Incubation平台实时检测N₂O和N₂浓度变化,通过测定土壤中反硝化功能基因丰度（nirK、nirS、nosZ）分析生物质炭对N₂O消耗的影响及其微生物方面的影响机理。结果表明：经过20 h厌氧培养后,0生物质炭处理的反硝化功能基因丰度（基因拷贝数·g^-1）分别为6.80×10⁷（nirK）、5.59×10⁸（nirS）和1.22×10⁸（nosZ）。与0生物质炭处理相比,1%生物质炭处理的nirS基因丰度由最初的2.65×10⁸基因拷贝数·g^-1升至7.43×10⁸基因拷贝数·g^-1,nosZ基因丰度则提高了一个数量级,由4.82×10⁷基因拷贝数·g^-1升至1.50×10⁸基因拷贝数·g^-1,然而nirK基因丰度并无明显变化;5%生物质炭处理的反硝化功能基因丰度并未发生显著变化。试验结束时,添加生物质炭处理的N₂/（N₂O+N₂）比值也明显高于0生物质炭处理。相关性分析结果表明,nirS基因丰度和nosZ基因丰度均与N₂O浓度在0.01水平上显著相关。试验末期nirS基因丰度和nosZ基因丰度均随着N₂O浓度的降低而升高。因此在本试验中,添加1%生物质炭可显著提高nirS和nosZ基因型反硝化细菌的丰度,增大N₂/（N₂O+N₂）比值,促进N₂O彻底还原成N₂。生物质炭对于N₂O主要影响机理是增大了可以还原氧化亚氮的细菌活性,促进完全反硝化。     

九龙坡花椒种植区地形、土壤肥力与花椒产量的关系

为了解九龙坡花椒种植区土壤养分状况及该区地形因子、土壤肥力因子与花椒产量的关系,为科学合理制定花椒高效施肥措施提供理论依据,本研究采用田间调查研究和室内分析的方法,研究了九龙坡花椒种植区低、中、高产区的海拔、坡度及土壤pH、有机质、大量微量元素含量和交换性能的变化特征,及其与花椒产量的关系。研究结果表明：九龙坡花椒普遍种植于200~500 m海拔范围,高产区集中在300 m左右的海拔;从低产区到高产区坡度略有增加,但未达显著水平。土壤均属酸性土,pH<6.5。土壤肥力总体属高水平范围,但各养分因子差异很大,其中土壤阳离子交换量（CEC）、有效磷、有效钙、有效镁、有效铁、有效锰、有效铜、有效锌含量丰富,分别为27.2 cmol（+）·kg^-1、35.2 mg·kg^-1、3 289.8 mg·kg^-1、271.8 mg·kg^-1、48.6 mg·kg^-1、62.1 mg·kg^-1、1.5 mg·kg^-1、4.5 mg·kg^-1;有机质、碱解氮、速效钾、交换性酸属适中水平,分别为19.1 mg·kg^-1、114.9 mg·kg^-1、107.0 mg·kg^-1、8.1 cmol（+）·kg^-1;水溶性硼缺乏,为0.28 mg·kg^-1。相关分析表明花椒产量与有效钙、CEC、pH、有效锰、水溶性硼呈显著正相关;通径分析结果表明有效钙、CEC、交换性酸、有效铜、有效铁、有效锌是影响花椒产量的主要因子,逐步回归分析构建了有效钙（X₆）与花椒产量（Y）的最优回归线性方程：Y=11.693+0.003X₆。综上所述,九龙坡花椒种植区土壤养分失衡较为严重,施肥应注重养分的平衡,增施有机肥,改善土壤理化性状,治理土壤酸化。     

粗颗粒土壤坡面侵蚀泥沙颗粒特征

为揭示粗颗粒土壤坡面侵蚀机理,采用湖北通城县、江西赣县、福建长汀县、广东五华县4个样地的4种粗颗粒土壤（分别定义为TCA、GXA、CTA、WHA）进行室内模拟降雨试验,研究粗颗粒土壤坡面侵蚀过程及侵蚀泥沙颗粒组成的变化规律。结果表明：（1）4种土壤的地表径流随着降雨时间的增长呈现出先增加后递减并趋于稳定的规律;（2）4种土壤的侵蚀特征存在差异,土壤侵蚀速率表现为WHA>TCA>GXA>CTA;（3）4种土壤的侵蚀泥沙中颗粒分布百分比大小均为砂粒>黏粒>粉粒>砾石。不同土壤侵蚀泥沙富集率表现出明显差异;（4）水流功率与土壤侵蚀速率的相关性显著,用幂函数可以准确描述其关系。在表达式中引入土壤黏粒含量、砾石含量后模型更加可靠（D_r=0.001ω^1.163C_l^-4.069,R²=0.82;D_r=0.003ω^1.149G_r^-1.934,R²=0.84）,提高了模型预测土壤侵蚀速率的精度,在实际应用中具有更广的适应范围与现实价值。     

细菌在土壤上吸附的研究——以一株假单胞菌(Pseudomonas Sp·)为例

本文以7种土壤作为吸附剂,用从土壤中分离并被32P放射性标记的纯假单胞菌(Psevdomonas sp·)作为吸附质,研究细菌在土壤上的等温吸附。在所选择的实验条件下(pH=7温度为30℃),发现细菌体在土壤上的吸附属于线性等温吸附:Ns=K_BN_W,并且还发现吸附常数K_B的大小与土壤中有机质含量呈正相关(r=0.992)。     

不同水分供应对甘薯叶片光合与荧光特性的影响及其光响应模型比较

水分供应对甘薯生长发育、产量形成具有重要影响。为探讨不同水分处理对甘薯光合与荧光特性的影响,本研究以鲜食型甘薯‘烟薯25号’为试验材料,研究不同水分处理下甘薯叶片的光合-光响应过程及其荧光特性,并利用不同模型对光响应过程进行拟合。研究结果表明：干旱和淹水处理显著降低了甘薯叶片净光合速率（P_n）、气孔导度（G_s）和蒸腾速率（T_r）;当PAR≤1 000 μmol·m^-2·s^-1时,干旱及淹水处理P_n的降低主要受气孔限制,当PAR>1 000 μmol·m^-2·s^-1时,P_n的降低主要受非气孔限制。荧光参数表明,干旱及淹水处理下甘薯叶片光系统Ⅱ（PSⅡ）对光的捕获及吸收能力下降,热耗散增加。光响应模型以直角双曲线修正模型拟合精度最高,且能拟合出饱和光强,适用于不同的土壤水分环境。模型拟合参数显示,所有处理甘薯叶片初始量子效率（α）为0.039~0.055,位于0~0.125的理论范围值内,干旱、淹水处理下甘薯叶片表现出显著的光饱和、光抑制现象,光能利用减弱,且淹水处理的光利用能力小于干旱处理。综合分析认为,直角双曲线修正模型是甘薯不同水分条件下光响应变化最佳模型。干旱及淹水处理均会对甘薯光系统造成损伤,使甘薯光合能力下降,淹水比干旱更易于降低甘薯叶片对光的利用能力,高光强会加重甘薯水分的胁迫程度。     

淮北主要土壤持水性能及其与颗粒组成的关系

本文研究了淮北主要耕作土壤的持水曲线、颗粒组成和微团聚体组成等物理性质,发现经验方程θ=AS^-B在中、低吸力段对土壤持水曲线有良好的模拟性,F检验都达到0.001的显著性水平。由此推导出比水容量为:C_θ=-(dθ/ds)=ABS^-(B+1),用解析法计算出各吸力值下不同土壤的比水容量,并认为AB值可作为土壤持水性能好坏的评价指标。同时尝试了以对数S型曲线的I型:P=1/a₂+b₂c^-lgD拟合土壤的颗粒大小分配曲线,以Ⅱ型:N(μ,σ)=a₂+b₂ lgD拟合微团聚体分布曲线,得到了较好的结果。并分析了土壤水分性质与其它物理性质的关系,以及这三个拟合方程中各参数的意义与相互关系,说明该区域土壤持水性能与颗粒组成、微团聚体有密切相关。     

Desorption behaviour of lead in two calcareous soils as affected by Pb level without and with compost supply

A laboratory study was performed to investigate the influence of soil texture (sandy loam vs. clay loam), Pb supply (as Pb(NO₃)₂ without or with compost) and Pb levels on the extraction of available Pb by diethylene triamine pentaacetic acid (DTPA) and its desorption patterns at ten shaking periods. The soils were polluted with five Pb levels without or with compost and incubated for 1 month. Kinetic models commonly used to study the release of the nutrients were used in this study. Results showed that Power function model described the pattern of Pb desorption better than other models. The amount of extracted Pb increased as the Pb levels increased and was found to be higher in sandy loam soil treated with Pb without compost than that of clay loam soil treated with Pb with compost. The a value (Pb desorption constant) was the highest in sandy loam soil amended with Pb without compost. The lowest value of a, however, was observed in clay loam soil amended with Pb with compost. The ab coefficient (initial desorption rate of Pb) was higher in sandy loam than clay loam soil, demonstrating higher initial release rates of Pb in the coarser-textured soil. Addition of Pb without compost resulted in a higher increase in ab value in comparison with Pb with compost, in both the soils.     

Comparison of Four Equations to Describe the Kinetics of Lead Desorption from Soils

The rate of Pb desorption was investigated from clay (Silty clay, Torrifluvent), CaCO₃-rich (Sandy clay, Calciorthid), and sandy (Sandy loam, Quartzipsamment) soils at two different temperatures. Lead has not been released from CaCO₃-rich soils which suggests irreversible Pb sorption by the soil. The desorption was quite hysteretic from sand and clay soils. The total amount of Pb released from the clay soil exceeded that released from the sandy soil. The lower Pb desorption associated with the sandy soil is probably due to its higher calcium carbonate content relative to the clay soil. The kinetics of Pb desorption were evaluated using the Elovich, modified Freundlich, parabolic diffusion, and first order equations. The first order and parabolic diffusion equations adequately described the kinetics of Pb desorption from clay and sandy soils under isothermal conditions. The choice of first order and parabolic equations among others investigated was based on the goodness of fit and the more scientific theoretical assumptions of the equations. The apparent Pb diffusion rate coefficient (D_d) and desorption rate coefficient (k_d) values from the clay and sandy soils increased with increasing temperature.     

Effect of flow rate on the adsorption and desorption of glyphosate,simazine and atrazine in columns of sandy soils

Adsorption and desorption of the herbicides glyphosate [N-phosphonomethyl-aminoaceticacid], simazine [6-chloro-N,N′-diethyl-1,3,5-triazine-2,4-diamine] and atrazine [6-chloro-N²-ethyl-N⁴-isopropyl-1,3,5-triazine-2,4-diamine] were studied in four sandy soils from Western Australia. Distribution coefficients (K_ds) were calculated from breakthrough curves (BTCs) resulting from leaching step changes in concentrations through small saturated columns of soil at flow rates ranging from 0.3 to 30 m day^–1. A comparison was made with K_ds obtained after batch equilibrating solutions of the herbicides with the same soils. The K_ds of herbicides in soils decreased with increasing flow rate and most strongly for glyphosate in soils rich in clay content. Resulting increases in mobility of about 40–50% were estimated for simazine and atrazine and > 50% for glyphosate at flow rates of 3 m day^–1. Adsorption and desorption rates were estimated by fitting numerically simulated BTCs to experimental BTCs. Best fits were obtained with a time-dependent Freundlich adsorption equation. The resulting coefficient for time dependency in the equation suggests that the rates of adsorption and desorption are controlled mainly by diffusion in an adsorbing layer on or in soil particles.     

Adsorption and Desorption of Arsenate in Different Soils and Gold Mining Substrates of Minas Gerais State,Brazil

Background  Arsenic (As) availability in natural environment is related to the element’s adsorption and desorption processes in soils. Total As is better related to available As in temperate soils than in tropical soils. In tropical soils, total As is not very significant in terms of availability, therefore justifying the necessity for studies into As dynamics. Knowledge of As dynamics in soil as well as development of new analytical methodologies involving tropical soils are insufficient and necessary for future mitigation projects. Objective  The objectives of this study were: (1) To adjust methodologies which may assist in understanding arsenate dynamics in tropical soils and substrates; (2) To evaluate the adsorption and desorption of arsenate in soils and substrate samples, and to find a minimum value of arsenate available in soil which is lethal to sorghum plants. Material and Methods  Samples of three soils from Minas Gerais State (YL, RYL, and CS) and two sulfide substrates of gold mining (B1 and B2) were used in the assays. All the material was physically and chemically characterized. Remaining As (As-rem) and remaining P (P-rem) of each material, along with MAC_P and MAC_As (using the Langmuir isotherms), were obtained. After agitation to obtain MAC_P and MAC_As, arsenate was extracted by anionic resin and Mehlich-III to evaluate arsenate desorption of the material retained on the filter paper. Subsequently, arsenate desorption curves for the different materials were obtained, and arsenate availability was determined through a bioassay with sorghum plants. Samples of soils and substrate B1 were incubated with six levels of As doses. Plants were grown under greenhouse conditions for 30 days. The plants were then harvested, dried and weighed. Available As in the soils and substrate was determined by Mehlich-III. Results and Discussions  As-rem level decreased from YL (sandy) to RYL (clayey) soil samples, which always showed lower values than P-rem. Among the soils and substrates evaluated, RYL showed the highest MAC_As and MAC_P, followed by CS, YL and Bl. The results were in accordance with the values observed for As-rem and P-rem and confirm the idea that the ability of the assayed materials to remove As from the soil/substrate solution is higher than the ability to remove P. On the other hand, the binding energy (a) between soil/substrate and As is weaker than the binding energy of P. Given the fact that the studied soils present a real ability to remove As from the solution, only a small part of As would be unavailable considering MAC_As as a reference. As-Mehlich-III values were higher than As-resin for substrate Bl. Mehlich-III seemed to be more appropriate to extract labile forms of arsenate in substrate B1 as well as in the soils. Available As by Mehlich-III (26.9 mg/dm³) was considered a reference of As LCL to sorghum plants. CC50 was sensitive to the buffering capacity of each soil, showing values varying from 1.34 mg/dm³ As (clay soil with lower As-rem) to 12.31 mg/dm³ As (sandy soil with higher As-rem). Conclusions  The adaptation of the As-rem and MAC_As methodologies was satisfactory and of great value in the study of adsorption, desorption and As availability for soils and mining substrate. Mehlich-III was also satisfactory to estimate available As and was sensitive to soil buffering capacity. Nevertheless, resin can also be used as an alternative. MAC_As varied among soils and was higher than MAC_p. However, As showed higher lability than P. Using Mehlich-III, we determined the value corresponding to CC50 that showed a good reference of toxicity to available As. Outlook  The environmental implications of the As behavior are quite serious. Beside the fact that arsenate is removed very fast from the soil solution, an anthropogenic input of the element, being part of the soil quantity factor, may remain in a reversible form for a long time. As may therefore return to the soil solution and becomes available to plants, animals and the entire environment. Considering that CC50 is the maximum contents of available As the environment can tolerate to allow some vegetal biomass production, the maximum capacity of As immobilization in each soil is reduced when compared to the soils’ MAC_As values. Therefore, the maximum and safe values of reference to be used in the evaluation of incidental discharge of the element in soils must be reduced.     

Adsorption and desorption of sulphate in some soils of the West Indies

Adsorption of sulphate was studied on eight West Indian soils. Adsorption was dependent on concentration for all the soils studied. At low concentrations of dissolved sulphate, the amount adsorbed was in accordance with the Langmuir equation. At higher concentrations this relationship broke down and it is postulated that this is due to differing adsorption sites.In desorption studies, the amount of sulphate released decreased with each successive extraction. Only 32.7% and 76.4% of the initially adsorbed sulphate was recovered in four KH₂PO₄ extractions from Montserrat clay and Montreal sandy loam, respectively. This is ascribed to the different properties of the two soils.Sulphate adsorption was related to the percentage of NaOH-extractable aluminium in the soil.     

Zeolite Effects on Immobile Water Content and Mass Exchange Coefficient at Different Soil Textures

The concern for groundwater pollution by agrichemicals through solute movement within the soil is widespread. Zeolite is a type of soil amendment that is utilized to improve physical properties of soil and ameliorate polluted soil. The high negative charge of the zeolite and its open space structure allows adsorption and access of heavy metals and other cations and anions. The objectives of this research were (i) to determine the effects of different application rates of zeolite (0, 2, 4, and 8 g kg^?1) on the immobile water content and mass exchange coefficient in a loam soil and then (ii) to determine the effects of optimum application rate of zeolite on the immobile water content and mass exchange coefficient of sandy loam and clay loam soils in saturated conditions by a mobile and immobile (MIM) model. In a disturbed soil column, a method was proposed for determination of MIM model parameters, that is, immobile water content (θ_im), mass exchange coefficient (α), and hydrodynamic dispersion coefficient (D_h). Breakthrough curves were obtained for different soil textures with different zeolite applications in three replicates, by miscible displacement of chloride (Cl^?1) in disturbed soil column. Cl^?1 breakthrough curves were evaluated in terms of the MIM model. The results showed that the pore water velocity calculated based on the total soil volumetric water content (θ_im+ θ_m) and real pore water velocity calculated based on the mobile water content (θ_m) increased in the loam soil with an increase in zeolite application rate, so that, between these different rates of zeolite application, the maximum value of pore water velocity and real pore water velocity occurred at zeolite application rates of 8.6 and 11.5 g kg^?1, which are indicated as the optimum application rates. However, the comparison between different soils showed that the zeolite application rate of 8 g kg^?1 could increase pore water velocity of sandy loam and loam soils by 31% more than that of clay loam soil. The immobile water content and mass exchange coefficient of loam soil were correlated with the zeolite application rate and reduced with an increase in the rate of applied zeolite. In a comparison between different soils at zeolite application rate of 8 g kg^?1, the immobile water contents of the zeolite-treated soil decreased by 57%, 60%, and 39% on sandy loam, loam, and clay loam soils, respectively, compared with the untreated soil. Furthermore, zeolite application could reduce mass exchange coefficient by 9%, 43%, and 21% on sandy loam, loam, and clay loam soils, respectively. A positive linear relationship was found between θ_im and α. Zeolite application increased real pore water velocity of sandy loam soil by 39% and 46% compared with loam and clay loam soils, respectively. In other studies there was a decrease in ammonium and nitrate leaching due to the zeolite application, and therefore, an increase in real pore water velocity due to zeolite application in sandy loam soil, as compared with the loam and clay loam soils, may not show more rapid movement of solute and agrichemicals to the groundwater.     

土壤质地对柱花草生长发育、生物量及土壤肥力变化的影响

采用大田试验的方法,在云南省元谋县小雷宰流域内壤土、砂壤土和重壤土3种质地土壤上,以热研5号柱花草为材料,研究土壤质地对柱花草生长发育、生物量及土壤有机质、有机碳、全氮和全磷的影响。试验结果表明:3种土壤质地上种植柱花草,柱花草地上部和地下部生长量和生物量表现幼苗期增加缓慢,而分枝期后增加快的趋势。壤土耕性好,兼有砂土和重壤土的优点,有利柱花草地上部分的生长发育,柱花草地上部生长量、生物量及改善土壤肥力方面显著高于重壤土。砂壤土有利于柱花草根系向深层土壤生长,柱花草地下部生长量、生物量及根瘤显著高于种植在重壤土。在3种土壤质地种植柱花草后,土壤有机质、有机碳、全氮和全磷均有上升趋势。综合而言,通气性和保肥保水能力居中的壤土更适合柱花草的生长发育及干物质的积累。     

Adsorption and desorption of dimepiperate by soils

The adsorption and desorption of dimepiperate, S-(,-dimethylbenzyl)-1-piperidinecarbothioate, on three soils of various physical and chemical properties was studied. Adsorption isotherms conformed to Freundlich equation. The k _f values increased with increasing organic carbon content of the soils. To confirm the effect of organic matter, the adsorption of the herbicide was studied after removal of organic matter by peroxidation. This soil treatment caused a sequential loss of adsorptive capacity. Desorption isotherms also conformed to Freundlich equation, but K _des values were higher than those for adsorption and increased with increase in concentration of initially adsorbed dimepiperate. Hysteresis was indicated by the decrease in slope of desorption compared to adsorption isotherms. Hysteresis decreased with increasing methanol content in the extracting solution. The factors involved are discussed.     

Short‐Term Effect of Lime,Phosphorus, and Iron Amendments on Water‐Extractable Lead and Arsenic in Orchard Soils

Abstract

Lead arsenate was extensively used to control insects in apple and plum orchards in the 1900s. Continuous use of lead arsenate resulted in elevated soil levels of lead (Pb) and arsenic (As). There are concerns that As and Pb will become solubilized upon a change in land use. In situ chemical stabilization practices, such as the use of phosphate‐phosphorus (P), have been investigated as a possible method for reducing the solubility, mobility, and potential toxicity of Pb and As in these soils. The objective of this study was to determine the effectiveness of calcium carbonate (lime), P, and iron (Fe) amendments in reducing the solubility of As and Pb in lead‐arsenate‐treated soils over time. Under controlled conditions, two orchard soils, Thurmont loam (Hapludults) and Burch loam (Haploxerolls), were amended with reagent‐grade calcium carbonate (CaCO₃), iron hydroxide [Fe(OH)₃], and potassium phosphate (KH₂PO₄) and incubated for 16 weeks at 26°C. The experimental results suggested that the inorganic P increased competitive sorption between H₂PO₄ ^? and dihydrogen arsenate (H₂AsO₄ ^?), resulting in greater desorption of As in both Thurmont and Burch soils. Therefore, addition of lime, potassium phosphate, and Fe to lead‐arsenate‐contaminated soils could increase the risk of loss of soluble As and Pb from surface soil and potentially increase these metal species in runoff and movement to groundwater.