异丙隆在土壤中的淋溶迁移及其影响因素研究

采用室内土壤淋洗柱法,以黄褐土、砂姜黑土和水稻土为供试土壤,研究了异丙隆在土壤中的淋溶迁移行为,探讨了淋溶水量、淋溶水pH值、施药量和添加外源木炭等因素对异丙隆在土壤中淋溶迁移的影响。结果表明,不同土壤中异丙隆淋出率为黄褐土〉砂姜黑土〉水稻土;淋溶水量与异丙隆的淋出率呈正相关,且对淋溶后异丙隆在土层中的分布有明显影响;用不同pH值的淋溶水时,异丙隆的淋出率为pH5〉pH9〉pH7;施加不同药量时,异丙隆的淋出率为10mg〉5mg〉20mg;异丙隆的淋出率随外源木炭添加量的增大而减小,而异丙隆在土壤柱中的滞留量则随着木炭添加量增大而增大,提示添加外源木炭可明显减少异丙隆在土壤中的淋出率,降低异丙隆在土壤中的淋溶深度。     

Effect of liming and added phosphate on charge characteristics of acid soils

The effects of liming-induced pH changes on surface charge were studied with four acid Fijian soils. All the soils possessed both positive and negative charge. Much of this charge was pH-dependent, but some negative charge was present at pH values as low as 4.0 and small quantities of positive charge were detected at pH values as high as 8.2. Adsorption of phosphate (P) reduced positive charge at low pH and increased negative charge at high pH. The net amount of surface charge per unit of P adsorbed varied with pH and appeared to depend on the mineralogy of the soil.     

Modern and paleolimnological evidence for accelerated leaching and metal accumulation in soils in New England,caused by atmospheric deposition

Empirical field evidence for changing chemical processes in soils caused by atmospheric deposition of pollutants consists of: (1) Long-term water quality data including total dissolved solids, concentrations of specific metals (e.g. Ca), and conductivity; (2) Cation exchange capacity and base saturation values for soils located on precipitation pH gradients; (3) Lysimeter studies; and (4) Chemical analysis of organic soils on precipitation pH and metal gradients. For well-drained organic soils, as precipitation pH decreases, metals are differentially leached at an accelerated rate (Mn>Ca>Mg≥Zn>Cd and Na>Al). Experimental field and laboratory lysimeter studies on soil columns yield similar results, with increases in leaching rates for soil solutions with pH=3 up to 100 × values for soil solutions with pH=5. Nearly 100% of the Pb from precipitation is accumulating in the organic soil layer or sediments. Zn is accumulating in soils and sediments where the pH's of precipitation, soil solutions, and surface waters are generally above 5 to 5.5. At lower pH values Zn and other chemically similar elements are desorbed/leached (net) at an accelerated rate. Chemical analyses of dated sediment cores from high and low altitude lakes, with drainage basins relatively undisturbed for the last 200+ yr, reveal that increased deposition of metals on a regional scale started in the northeastern United States as early as 1880, consistent with increased fossil fuel consumption. This suggests acidified precipitation as early as 1880. Cores from historically acidified lakes (pH<≈5.3 to 5.5) indicate that, as acidification of surface waters occurs (caused by acidic deposition), concentrations of Zn, Mn, and Ca decrease in the sediment. Apparently the metals are leached from the detritus prior to sedimentation. This conclusion results from data from experimental acidification of sediment cores and the general observation that precipitation pH is generally ≥0.5 pH units lower than lake water pH. Accelerated leaching of soil in New England dates to earlier than 1900.     

砂质土壤磷素的组成特点与释放规律研究

砂质土壤磷素主要以可提取态形式积累,有很高的释放潜力。该类土壤磷素的释放受土壤pH、土水作用时间和土壤溶液化学组成等的影响。土壤酸化、土壤溶液中Na+浓度的提高及土壤与水的作用时间增加可促进土壤磷素的释放。用淋洗方法和平衡提取等2种方法对土壤磷素的释放评价表明,淋洗方法测得的P量较小,可代表土壤短期内P释放强度;而平衡提取法提取的P数量较大,可代表土壤P长期释放的容量。     

Origin of the effect of ph on the saturated hydraulic conductivity of non‐sodic soils

Abstract

The effect of pH on the saturated hydraulic conductivity (K) of repacked columns of two non‐sodic soils (Healaugh and Fagaga soils) was examined. The K value was greater for the Fagaga soil than for the Healaugh soil which is attributed to the difference in the amount of free iron oxides between the soils. The K values reached a maximum when the pH was close to the point of zero net charge (PZNC) (3.7 and 4.8 for the Healaugh and the Fagaga soil, respectively) and decreased on either side of these pH values. The effect of pH on K was related to its effect on surface charge. As the pH of variable‐charge soils approaches the PZNC, the net surface charge decreases resulting in flocculation and maintenance of a high K. Conversely, as the pH deviates from the PZNC, the net surface charge increases, resulting in dispersion and a decrease in K. There was a negative relationship between the amount of dispersed clay and the K values, suggesting that clay dispersion and the resulting clogging of pores decreases K in these soils.     

Sorption and mobility of 14C-labeled imazaquin and metolachlor in four soils as influenced by soil properties

Aqueous batch-type sorption-desorption studies and soil column leaching studies were conducted to determine the influence of soil properties, soil and suspension pH, and ionic concentration on the retention, release, and mobility of [14C]imazaquin in Cape Fear sandy clay loam, Norfolk loamy sand, Rion sandy loam, and Webster clay loam. Sorption of [14C]metolachlor was also included as a reference standard. L-type sorption isotherms, which were well described by the Freundlich equation, were observed for both compounds on all soils. Metolachlor was sorbed to soils in amounts 2-8 times that of imazaquin, and retention of both herbicides was related to soil organic matter (OM) and humic matter (HM) contents and to herbicide concentration. Metolachlor retention was also related to soil clay content. Imazaquin sorption to one soil (Cape Fear) increased as concentration increased and as suspension pH decreased, with maximum sorption occurring in the vicinity of pK(a1) = (1.8). At pH levels below pK(a1) imazaquin sorption decreased as hydronium ions (H3O+) increased and competed for sites. NaCl was more effective than water in desorption of imazaquin at pH levels near the pK(a1). Mechanisms of bonding are postulated and discussed. The mobility of imazaquin through soil columns was in the order Rion > or = Norfolk > Cape Fear > or = Webster, whereas for metolachlor it was Rion > or = Norfolk > Webster > or = Cape Fear. Imazaquin was from 2 to 10 times as mobile as metolachlor.     

离子强度和pH对可变电荷土壤与铜离子相互作用的影响

研究了离子强度和pH对可变电荷土壤表面电荷与铜离子吸附的影响。作为对照 ,也研究了它们对恒电荷土壤黄棕壤的有关性质的影响。结果表明 ,随pH升高 ,土壤的表面负电荷增加 ,正电荷减少。对于可变电荷土壤 ,可出现电荷零点 (pH0 )。随pH升高 ,土壤对Cu2 的吸附量增大。随着离子强度增大 ,恒电荷土壤对Cu2 的吸附百分率明显降低 ,可变电荷土壤对Cu2 离子的吸附百分率也降低 ,但降低的幅度比恒电荷土壤者小得多。土壤中氧化铁的含量越高 ,降低的幅度越小。对于含 2 1 %左右游离氧化铁的铁质砖红壤 ,即使支持电解质NaNO3的浓度高达 1molL- 1,对Cu2 的吸附仍然几乎没有影响。从离子强度和pH与土壤表面电荷和铜离子吸附的关系 ,可以推测在土壤对铜离子的吸附中 ,既存在电性吸附 ,又存在专性吸附。在可变电荷土壤对铜离子的吸附中 ,专性吸附较为重要     

Surface chemical properties and pedogenesis of tropical soils derived from basalts with different ages in Hainan,China

Limited information is available on the changes of surface chemical properties of tropical soils with time during the pedogenesis. Soil samples of three profiles derived from basalts of 10, 1330 and 2290 kilo annum (ka) in age were collected from adjacent locations in a tropical region of Hainan Province, China. The changes in soil surface chemical properties and the mineralogy of the soil clay fraction with time were investigated using ion adsorption, micro-electrophoresis, and X-ray diffraction analysis. The content of 2:1-type clay minerals decreased, while those of kaolinite and gibbsite increased with increasing basalt age and degree of soil development. The content of pedogenic free iron (Fe) oxides and the ratio of free Fe oxides/total Fe oxides increased with soil development stage, while soil poorly crystalline Fe and aluminum (Al) oxides had an opposite trend. The positive surface charge of the soils increased with increasing basalt age and degree of soil development; this was consistent with the change in their contents of free Fe/Al oxides. However, the value of negative surface charge had an opposite behavior. The soil derived from 10-ka-basalt had much more negative charge than soils derived from 1330- and 2290-ka-basalt. Soil net surface charge and zeta potential of the soil clay-fraction decreased with the increase in basalt age. Both net charge–pH curves and zeta potential–pH curves shifted to positive values with increased basalt age and degree of soil development. Increasing age also elevated the point of zero net charge of the soil and the isoelectric point of soil colloids.     

Ionic-strength and pH effects on the sorption of cadmium and the surface charge of soils

Two Oxisols (Mena and Malanda), a Xeralf and a Xerert from Australia and an Andept (Patua) and a Fragiaqualf (Tokomaru) from New Zealand were used to examine the effect of pH and ionic strength on the surface charge of soil and sorption of cadmium. Adsorption of Cd was measured using water, 0.01 mol dmp^?3 Ca(NO₃)₂, and various concentrations of NaNO₃ (0.01–1.5 mol dm^?3) as background solutions at a range of pH values (3–8). In all soils, the net surface charge decreased with an increase in pH. The pH at which the net surface charge was zero (point of net zero charge, PZC) differed between the soils. The PZC was higher for soils dominated by variable-charge components (Oxisols and Andept) than soils dominated by permanent charge (Xeralf, Xerert and Fragiaqualf). For all soils, the adsorption of Cd increased with an increase in pH and most of the variation in adsorption with pH was explained by the variation in negative surface charge. The effect of ionic strength on Cd adsorption varied between the soils and with the pH. In Oxisols, which are dominated by variable-charge components, there was a characteristic pH below which increasing ionic strength of NaNO₃ increased Cd adsorption and above which the reverse occurred. In all the soils in the normal pH range (i.e. pH>PZC), the adsorption of Cd always decreased with an increase in ionic strength irrespective of pH. If increasing ionic strength decreases cation adsorption, then the potential in the plane of adsorption is negative. Also, if increasing ionic strength increases adsorption below the PZC, then the potential in the plane of adsorption must be positive. These observations suggest that, depending upon the pH and PZC, Cd is adsorbed when potential in the plane of adsorption is either positive or negative providing evidence for both specific and non-specific adsorption of Cd. Adsorption of Cd was approximately doubled when Na rather than Ca was used as the index cation.     

长期施肥对砂姜黑土可溶性碳淋溶的影响

研究施肥对砂姜黑土可溶性碳淋溶的影响,对有机肥的可持续利用有重要意义。该研究依托33 a的长期试验,分析常规施肥（MF）、化肥+低量小麦秸秆（MFL）、化肥+高量小麦秸秆（MFH）、化肥+猪粪（MFP）和化肥+牛粪（MFC）等施肥方式对土壤剖面（0～60 cm）理化性质、微生物性状、可溶性有机碳（Dissolved Organic Carbon,DOC）和可溶性无机碳（Dissolved Inorganic Carbon,DIC）含量与分布的影响,探寻可持续的有机肥利用方式。结果表明,长期增施有机肥后0～60 cm剖面各土层有机碳、微生物量碳、氮均有不同程度提升,而对土壤全氮、容重和pH值的影响主要发生在0～20 cm表层。与MF处理相比,增施有机肥后0～20和>20～40 cm土层DOC含量均有显著（P <0.05）提高,而对>40～60 cm土层无显著影响。相对而言,0～60 cm各土层DIC的含量均有显著提升。长期增施有机肥后0～60 cm各土层DOC的UV280吸收值和芳香性指数分别较MF处理均有显著提高,其中以MFC处理最为显著,0～20、>20～40和>40～60 cm土层DOC的芳香性指数分别提高71.2%、153.3%和38.1%,这说明长期增施有机肥后土壤剖面DOC结构发生明显改变,芳香化合物含量提高,化合物结构变得更加复杂。逐步线性回归模型表明,土壤剖面DOC和DIC分布主要受pH值和微生物量碳的共同影响,且pH值的影响强度大于微生物量碳,而土壤剖面DOC化学结构受微生物量碳的影响。总体而言,外源有机物料投入的类型和数量是影响土壤剖面可溶性碳分布的重要措施,长期增施农家肥的碳淋失风险高于秸秆还田。     

Phosphate fertilizers influence leaching of lead and arsenic in a soil contaminated with lead arsenate

Use of high rates of monoammonium phosphate (MAP) or monocalcium phosphate (MCP) fertilizers has the potential to alter Pb and As mobility in soils contaminated with lead arsenate pesticide residues. A laboratory column experiment was conducted to determine the effects of P amendment source (MAP, MCP), P rate (0, 0.31, 0.62 g column^–1), and amount of leaching (1, 2 pore volume displacements, PVD) on Pb, As, P, pH, and salinity distribution within and leaching from a Burch loam soil containing 1800 mg Pb kg^–1 and 400 mg As kg^–1 Addition of either MAP or MCP significantly increased the amount of As leached from the soil. The P amendments reduced the amount of Pb in the first PVD but enhanced Pb in the second PVD so that the cumulative amount of Pb leached was independent of treatment. Phosphorus source, P rate, and quantity of leaching water influenced the total amount of leachate As, and soil and leachate P, pH, and salinity. Use of phosphate fertilizers on lead arsenate-contaminated soils may temporarily enhance potential for As phytoavailability or As contamination of groundwater.Dept. of Agronomy and Soils Paper No. 9001-11. Project No. 0747, College of Agric. and Home Economics Res. Ctr., Washington State Univ., Pullman, WA 99164.     

模拟酸雨对太湖地区水稻土铜吸附—解吸的影响

以太湖地区三种典型的水稻土（黄泥土、白土、乌泥土）为例，利用模拟-培养试验，着重研究模拟酸雨对土壤的铜吸附解吸能力的影响，研究结果表明：与未淋溶土壤相比，经模拟酸雨淋溶的三种土壤对铜的吸附量有所增加，随着淋溶液pH的降低，增幅减小：易解吸态铜的解吸量则随淋溶液pH的降低而增大，模拟酸雨降低了土壤对重金融污染的缓冲能力；虽然黄泥土、乌泥土对铜的吸附量远大于白土，但模拟酸雨对乌泥土的吸附-解吸能力的影响速度也大于白土。     

Effect of liming and phosphate additions on sulphate leaching in soils

The effect of lime (CaCO₃) and phosphate additions on surface charge characteristics and their effect on the leaching of sulphate were examined for two soils (Patua loam and Tokomaru silt loam) which differed in their adsorption capacities for sulphate.
Incubation of soils with either CaCO₃ (0–600 mmol kg⁻¹) or phosphate (0-208 mmol kg⁻¹) resulted in a two- to five-fold increase in the net negative charge and a similar decrease in the adsorption of sulphate. The effect of either lime or phosphate addition on both the surface charge and sulphate adsorption was more pronounced for the allophanic Patua soil than for the Tokomaru soil containing mainly vermiculite.
In a column experiment, liming induced the leaching of sulphur either by the desorp-tion of adsorbed sulphate or by the mineralization of organic sulphur. During a miscible displacement study, addition of either CaCO₃ or phosphate resulted in an early breakthrough of sulphate in the leachate. In a pulse experiment, in which soils were incubated with sulphate (3.12 mmol kg⁻¹) for 1 week and subsequently leached with water, more added sulphate was lost in the leachate of the soils previously incubated with either CaCO₃ or phosphate.     

磷酸盐吸附对可变电荷土壤正负电荷的影响

本文研究了华南地区不同类型的可变电荷土壤，并对磷酸盐的吸附量和吸附磷后土壤的正、负电荷的变化，以及ｐＨ和游离氧化铁对这种变化的影响进行了研究。结果表明，土壤吸磷量与土壤游离氧化铁含量成良好的正相关。土壤吸磷后正电荷减少，负电荷增加，土壤电荷量与吸磷量之间呈抛物线状相关。吸附１摩尔磷酸盐对土壤净负电荷的贡献在０．３－１．０摩尔之间。土壤中的游离氧化铁使吸附的磷对土壤负电荷的贡献减少。     

电渗析与酸淋洗模拟紫色土酸化的效果比较

为了比较电渗析与酸淋洗试验模拟紫色土酸化的效果,在重庆地区采集了不同pH(5.00和7.06)的2个紫色土,分别进行不同天数(1,2,5,7,10天)的电渗析和酸淋洗试验处理,并分析了试验处理前后土壤的酸度特征和交换性盐基成分含量变化。结果表明,在整个10天的淋溶处理过程中,2种紫色土的pH均无显著变化,说明紫色土具有一定的酸缓冲能力,短期的酸雨淋溶不能实现紫色土的严重酸化。而采用电渗析处理10天后,中性紫色土和酸性紫色土的pH分别降低3.4和1.1个单位。在整个电渗析处理过程中,土壤的交换性酸含量显著升高,盐基离子大量淋失。电渗析可以实现对紫色土的快速酸化处理。2种紫色土中,电渗析处理后中性紫色土的酸化程度大于酸性紫色土。这是由于中性紫色土的表面负电荷量更高,导致更多致酸离子吸附在土壤胶体表面,最终造成中性紫色土的酸化程度更加严重。因此,电渗析处理比酸雨淋溶处理对紫色土酸化效果更好,且可用于紫色土的酸化机理研究。进一步结合2种方法的技术可操作性,认为电渗析法是研究紫色土酸化问题的一种有效技术手段。     

土壤电化学性质的研究Ⅲ.红壤胶体的电荷特征

土壤胶体的电荷性质,与土壤的一系列物理化学性质有密切关系。红壤的某些与肥力有关的物理化学性质,与其它类型土壤有所不同。例如,它的阳离子交换量较小,而阴离子吸附量则较大,分散性较弱,胀缩性也较小。红壤在物理化学性质方面的这些特点,大多是由其胶体的电荷特点所引起。     

Effect of organic amendments on the retention and mobility of imazaquin in soils

The influence of two organic amendments consisting of an urban waste compost (SUW) and a commercial amendment from olive mill wastes (OW) was assessed on the sorption properties and leaching of the ionizable herbicide imazaquin on four soils with different physicochemical characteristics. A loamy sand soil (CR), a loam soil (P44), a silt loam soil (AL), and a clay soil (TM), with low-medium organic matter contents, were chosen. Sorption-desorption experiments were performed on the original soils and on a mixture of these soils with the organic amendments at a rate of 6.25% (w/w). These mixtures were used just after preparation and after aging for 3 months. Imazaquin adsorption was higher on AL soil because of its high content of amorphous iron oxides, whereas it was related to the soils' organic matter (OM) contents on TM and CR soils and to acid pH on P44 soil. Addition of exogenous OM to soils caused a decrease in the adsorption of the herbicide with the only exception of CR soil, due to blocking of adsorptive surfaces and/or equilibrium pH rise. The extent of this decrease was dependent only on the nature of the added amendment on AL soil. The adsorbed amounts of imazaquin on aged organic fertilized soils were usually fairly close to that on original soils. Results of soil column experiments indicate that addition of exogenous organic matter cannot be considered as a regular practice for retarded movement of imazaquin.     

Zinc sorption–desorption by two Andepts: effect of pH and support medium

Laboratory experiments were carried out to evaluate the effect of pH, ionic strength and electrolyte composition on zinc sorption–desorption by two Andepts from the Canary Islands (Spain). At the natural soil pH, the soils exhibited little net negative surface charge and small Zn sorption capacities. More than 75% of the sorbed Zn was apparently strongly bonded. The pH greatly influenced the sorption–desorption reactions. Sorption increased with increasing pH, and retention increased abruptly at pH > 6.0. Sorption also occurred at pH values below the point of zero charge (PZC) of the soils, when most of the surface sites are positively charged. Desorption decreased continuously with rising pH and became a trace at pH > 6.0. An increase in the ionic strength of the background electrolyte decreased Zn sorption and enhanced the amount of sorbed metal that could be subsequently released. In the two soils, Zn sorption diminished somewhat in the K and Ca electrolytes as compared with the Na electrolyte. However, this did not happen at small Zn loadings. Desorption was not affected by the type of electrolyte and cation used. The results are consistent with chemisorption being responsible for most of the sorption. The results also suggested a strong affinity sorption or even precipitation at high pHs.     

Ionic strength effects on surface charge and adsorption of phosphate and sulphate by soils

Two surface soils (Patua and Tokomaru) of contrasting mineralogy were incubated with several levels of either CaCO₃ or HC1. The effects of ionic strength on pH, on surface charge, and on the adsorption of phosphate and sulphate were measured in three concentrations of NaCl. The pH at which the net surface charge was zero (point of net zero charge—PZC) was 1.8 for the Tokomaru soil and 4.6 for the Patua soil: differences that can be related to mineralogical composition. There was an analogous point of zero salt effect (PZSE) that occurred at pH 2.8 for the Tokomaru soil and at 4.6 for the Patua soil. The presence of permanent negative charge in the Tokomaru soil resulted in an increase in PZSE over PZC. The effect of ionic strength on adsorption varied greatly between phosphate and sulphate. For phosphate, there was a characteristic pH above which increasing ionic strength increased adsorption and below which the reverse occurred. This pH (PZSE for adsorption) was higher than the PZC of the soil and was 4.1 for the Tokomaru soil and 5.3 for the Patua soil. In contrast, increasing ionic strength always decreased sulphate adsorption and the adsorption curves obtained in solutions of different ionic strengths converged above pH 7.0. If increasing ionic strength decreases adsorption, the potential in the plane of adsorption must be positive. Also, if increasing ionic strength increases adsorption, the potential must be negative. This suggests that, depending upon pH, phosphate is adsorbed when the potential in the plane of adsorption is either positive or negative, whereas sulphate is absorbed only when the potential is positive.     

不同土壤钾素淋溶特性的初步研究

通过室内土柱淋溶试验,研究降雨情况下不同土壤钾素的淋溶特性及其与土壤性质的关系,结果表明:未施钾的自然土壤,在降雨量较小时(87 mm),决定钾素淋溶状况的主要土壤因子是土壤质地,质地越轻,K+淋溶量越大;降雨量较大时(435 mm),决定钾素淋溶状况的主要因子则为速效钾,田间速效钾含量愈大,淋溶风险愈大。外源钾施入土壤后,在降雨量较小时(87 mm),钾素淋溶状况主要受土壤粉粒和缓效钾的影响,粉粒含量和缓效钾越大,淋溶量越小;降雨量较大时(435 mm),钾素淋溶状况主要受全钾和缓效钾的影响,其值越大淋溶量越小。在降雨量充足、田间排水不畅的情况下,短时间内(2 h)土壤钾肥表观淋出率仅与粉粒含量呈显著负相关关系,土壤的质地是影响钾淋溶主要因子;长时间(24 h)淋溶后钾肥表观淋出率则与土壤pH、粉粒、全钾、缓效钾和长石含量均呈显著负相关关系,其中全钾和粉粒的影响作用最大。