A Landscape Level Analysis of Potential Excess Nitrogen in East-Central North Carolina,USA

The role of soil colloids and their potential to co-transport agrochemicals in subsurface soil environments was evaluated in aleaching experiment utilizing large soil monoliths. The monolithswere created by hydraulically driving steel pipe sections (50 cm diameter × 50 cm length) into Maury silt loam (fine, mixed, mesic Typic Paleudalf) and Loradale silt loam (fine, silty, mixed mesic Typic Argiudoll) soils. Water dispersible colloids fractionated from the Bt horizons of the above soilswere spiked with 3 mg L^-1 atrazine (2-chloro-4-ethylamino-6-isopropylamine-s-triazine) and 10 mg L^-1 zinc (Zn), and after a twenty-four hour equilibration were applied into the monoliths at eight hour intervals using 500 mL pulse applications. Solutions containing atrazine and Znwithout added colloids were applied to separate monoliths from each soil to represent control treatments. Colloid, atrazine, andZn recoveries in the eluent varied greatly with respect to soiltype. Colloid recovery in the Loradale monoliths averaged 65.1 ± 26.5%, with maxima approaching the input level, while in the Maury monoliths the average recovery was low (5.7 ± 6.2%) and never exceeded 25% of the input level. Atrazine eluted from the two monoliths averaged 40.3 ± 12.5% (Loradale) and 29.0 ± 20.0% (Maury), with considerable enhancement in the presence of colloids, especially in the Loradale soil. In contrast, the elution of Zn averaged 3.0 ±3.2%, in the Loradale monoliths and rarely exceeded control concentrations in the Maury monoliths, suggesting a stronger retardation of Zn over atrazine within the soil matrix, especially when colloid transport was deterred. Settling-rateexperiments at varying pH and electrical conductivity (EC) valuessuggested that the transport of Maury colloids may have been hindered due to flocculation within the monoliths, while the Loradale colloids remained stable throughout the leaching experiment. Although the presence of colloids enhanced atrazineelution in all monoliths, the actual amount of atrazine transported bound to either colloid type was minimal, suggestingmainly physical exclusion transport processes. In contrast, stronger chemisorption of Zn to colloid surfaces than the soil matrix appeared to enhance the transport of Zn by both colloids.     

草萘胺在五种土壤及其胶体上的吸附行为

土壤胶体是土壤中颗粒最细小的部分,由于具有巨大的比表面积和较高的吸附容量,是环境中污染物的重要吸附剂,直接影响到污染物的归趋和生物有效性.本文采用批次吸附试验的方法,研究了农药草萘胺在黄棕壤等5种土壤及土壤胶体上的吸附行为.结果表明,草萘胺在供试土壤及胶体上的吸附均能很好地符合Freundlich方程;与本体土壤相比,...     

土壤胶体理化性质对其稳定性和可移动性的影响研究

采用长春市具有代表性的阶地农田的黏壤土、河漫滩的细砂土和黄土台地的粉壤土为基质,以提取的土壤胶体为对象,采用实验室模拟方法研究了土壤胶体理化性质对其稳定性和可移动性的影响。研究结果表明3种土壤胶体的临界絮凝浓度(CFC),与伊利石/蒙脱石矿物含量成反比并随着矿物含量的增大而降低,可能是因为伊利石/蒙脱石矿物是易絮凝矿物,水化驱动力及水化后的不稳定性较大;去除游离氧化铁后的农土去铁胶体提高了稳定性,而黄土去铁胶体和河土去铁胶体降低了稳定性,主要是由不同的土壤胶体去除游离氧化铁后性质改变程度不一样引起的;去除有机质后的农土去有机质胶体、黄土去有机质胶体和河土去有机质胶体降低了CFC,并且降低程度是与土壤胶体的有机质含量成反比。     

离子强度及pH对不同类型土壤中胶体释放的影响

采用实验室土柱纵向淋溶法,研究了离子强度及pH变化对常熟乌栅土原状、扰动土柱以及东北黑土、江西红壤扰动土柱土壤胶体释放的影响。结果表明离子强度变化对我国不同类型土壤胶体释放影响不同：淋洗液电解质为NaCl时,对于常熟乌栅土以及东北黑土,离子强度减小促进胶体的释放,反之抑制胶体的释放;对于江西红壤,离子强度变化对土壤胶体释放则不产生影响。淋洗液电解质为CaCl2条件下,土壤胶体的释放量低于淋洗液为NaCl,且离子强度变化对三种土壤胶体的释放均不产生明显影响。相同条件下,常熟乌栅土及东北黑土胶体释放量远远大于江西红壤,pH变化则对上述类型土壤胶体释放的影响不明显。研究结果有助于进一步阐明水化学条件的变化对我国不同类型土壤胶体释放的影响规律。     

土壤胶体在不同饱和度土壤介质中的释放与淋溶行为研究

采用饱和与非饱和填充土柱纵向淋溶研究方法,结合对流弥散模型方程（CDE）对穿透曲线的拟合计算,全面考察了土壤介质水饱和度、土壤水pH/离子强度、土壤孔隙水流速和土壤胶体颗粒大小对天然土壤胶体在实际土壤介质中释放、沉积迁移行为的影响。分别获取胶体扩散系数和阻滞因子值,定量说明实验中水化学、水动力学等条件的作用影响力。结果显示,介质不饱和条件不利于胶体的释放和淋溶;高pH和低离子强度条件对土壤胶体释放与迁移有利;淋溶过程的间断干扰,可以促使土壤胶体的增量淋溶释放;淋溶强度及胶体颗粒粒径大小,能够影响胶体穿透时间和穿透浓度峰值大小。     

2,4-D 对铜在乌栅土胶体和红壤胶体上吸附的影响

应用批平衡法研究了农药2,4-D对Cu在乌栅土胶体和红壤胶体上吸附的影响。结果表明,Cu在两种土壤胶体上的吸附等温线均符合Langmuir方程,Cu在乌栅土胶体上的吸附量较其在红壤胶体上的吸附量要高;在pH3.0～6.7范围内,两种土壤胶体对Cu的吸附量均随溶液pH的升高而升高。2,4-D增加了Cu在土壤胶体上的吸附,2,4-D的浓度越高,Cu的吸附量越大,这主要是由于2,4-D的存在显著增加了平衡液的pH,从而增加了土壤胶体表面所带负电荷量。     

褐土碳酸钙结核的胶体特性研究

碳酸钙是黄土母质发育土壤的重要胶结物质，对土壤团粒结构的形成具有重要作用。本文采集了碳酸盐褐土中的碳酸钙结核，采用物理分散法和化学分散法分别提取得到褐土碳酸钙结核纳米颗粒和褐土碳酸钙结核胶体，并以工业纳米碳酸钙作为对照对其胶体特性进行研究。采用X射线衍射仪、zeta电位仪和动态光散射仪对褐土碳酸钙结核胶体和工业纳米碳酸钙的矿物组成、zeta电位和胶体稳定性进行了表征。结果表明：褐土碳酸钙结核胶体、褐土碳酸钙结核纳米颗粒和工业纳米碳酸钙的初始颗粒直径分别为224.24、88.01和98.50 nm，而褐土碳酸钙结核胶体和褐土碳酸钙结核纳米颗粒的多分散度高于工业纳米碳酸钙。褐土碳酸钙结核胶体中方解石含量为70.3%，其次含有石英、长石和伊利石等矿物；褐土碳酸钙结核纳米颗粒主要含有方解石和伊利石，含量分别为48%和45%。3种碳酸钙胶体表面均带负电荷，其zeta电位绝对值均随着溶液pH的增大而增大。褐土碳酸钙结核胶体在NaCl和CaCl₂溶液中的临界聚沉浓度分别为538.01 mmol/L和2.08 mmol/L，褐土碳酸钙结核纳米颗粒在NaCl和CaCl₂溶液中的临界聚沉浓度为82.18 mmol/L和1.11 mmol/L，而工业纳米碳酸钙的临界聚沉浓度为80.37 mmol/L和1.59 mmol/L。3种碳酸钙胶体的矿物组成差异是引发其凝聚行为差别的内在原因，化学分散剂的表面修饰作用、颗粒直径大小和溶液化学条件也是影响胶体稳定性的重要因素。本文研究结果表明，碳酸钙胶体的可变电荷特性可能是其具有胶结特性的本质原因，其对石灰性土壤团聚体结构的影响还需要进一步深入研究。     

酒石酸对黏粒矿物上酸性磷酸酶吸附及活性的影响

采用平衡批处理法,研究了模拟根系分泌物——酒石酸溶液的浓度(0~80 mmol L-1)、pH(2.5~7.0)对酸性磷酸酶在针铁矿、高岭石及黄棕壤和砖红壤胶体(<2μm)上的吸附及比活性影响。结果表明,当酒石酸浓度由0 mmol L-1(作为对照)升高至80 mmol L-1时,酸性磷酸酶在供试土壤胶体和矿物表面的吸附量先急剧降低(0~5mmol L-1之间),后逐渐达到平衡;以羟基化表面为主的针铁矿对酸性磷酸酶的吸附百分率受酒石酸浓度的影响最大,吸附百分率从对照的96.2%降至80 mmolL-1酒石酸浓度时的33.7%,其他以层状铝硅酸盐矿物为主的供试土壤胶体和高岭石则受影响较小,吸附百分率从对照的76.3%~60.6%降至80 mmol L-1酒石酸浓度时的56.2%~41.6%。酸性磷酸酶在酒石酸体系中的最大吸附pH点均在该酶的等电点酸侧,这可能与酒石酸对矿物表面的电荷性质改变有关;酒石酸体系中,针铁矿上酸性磷酸酶的比活性远高于其它供试土壤胶体,该酶的最适比活性点随胶体类型的不同而无变化或有所高移。     

土壤胶体对砂质土柱中草萘胺迁移的影响

采用室内砂柱模拟试验方法研究了红壤和黑土两种土壤胶体对草萘胺在砂质土柱中迁移的影响。结果表明,整个淋滤过程中红壤和黑土胶体的回收率比较高,分别达到66．76％和74．75％;胶体促进了草萘胺在砂质土柱中的迁移,与对照相比（无胶体）,加入红壤和黑土胶体后草萘胺的回收率分别提高了9．82％和10．63％。但是吸附在胶体上迁移的草萘胺数量比较少,只占到迁移总量的1．15％（红壤）和1．68％（黑土）,物理非平衡机制可能在迁移过程中起支配作用。     

Weathered Fly Ash Does Not Affect Soil And Biosolid Carbon Mineralization

Fly ash and biosolid wastes can be mixed and applied to soil as a means of disposal. A significant decline in soil respiration following waste application indicates restricted activities of functional microbial populations. Weathering decreases salinity and neutralizes alkalinity in fly ash, but there is little information on the effects of unweathered fly ash and biosolid mixtures on soil carbon (C) mineralization. The objective of this study was to determine the effects of a weathered fly ash–limestone scrubber residue (LSR) mixed with an aerobically digested biosolid on soil respiration in a laboratory incubation study. Biosolids significantly increased carbon dioxide (CO₂) production (p < 0.05), but up to 6.75% (w/w) fly ash did not. Mean total C mineralization was 770 mg CO₂‐C kg^?1 soil in the control and 3,810 mg CO₂‐C kg^?1 soil in the 6.75% (w/w) biosolid treatment. Fly ash with neutral pH and low salinity appears unlikely to affect soil and biosolid C mineralization.     

Transport and re-entrainment of soil colloids in saturated packed column: effects of pH and ionic strength

Purpose

Colloid migration in subsurface environments has attracted considerable attention in recent years because of its suspected role in facilitating transport of strongly adsorbed contaminants to groundwater. The influence of bulk solution pH or ionic strength on model colloid (i.e., latex microsphere, amorphous silica colloids) transport is well established, while little attention has been paid to water-dispersible soil colloids. In this study, saturated packed columns were conducted to explore the mechanism of transport and fate of water-dispersible soil colloids and facilitating transport of Cu during transients in solution chemistry.

Materials and methods

Water-dispersible soil colloids were fractionated from a Cu-contaminated soil sample. Transport of soil colloidal suspensions was conducted with varying pH and ionic strengths, and then, re-entrainment of those retained colloids after completion the transport experiments was conducted by changing pore water solution transient ionic strength and pH conditions. Meanwhile, transport and fate of the Cu strongly adsorbed on the soil colloids were determined under different ionic strength conditions.

Results and discussion

The transport behavior of soil colloids in porous media was found to depend on the pH and ionic strengths of bulk solution. An increase in solution ionic strength and decrease in solution pH resulted in greater deposition which was revealed by the collision efficiency (??). It increased from 0.15 to 1.0 when solution composition changed from 0 to 50?mM NaNO₃ and decreased dramatically from 1.0 to 0.035 as the solution pH converted from 2.97 to 8.94. The results were in agreement with Derjaguin?CLandau?CVerwey?COverbeek theory. Upon stepwise reduction in ionic strength of eluting fluid or enhancement in its pH, a sharp release of colloids retained in the column occurred in each step. Meanwhile, the value of FRE _NaOH that reveals the effect of NaOH solution at pH?11 on the mobilization of retained colloids deposited in the primary minimum increased from 38.6% to 64.6% when the ionic strength of bulk solution changed from 0 to 50?mM NaNO₃ and decreased from 86.7% to 35.8% as the solution pH from 2.97 to 8.94. In addition, the transport and fate of the Cu strongly adsorbed on soil colloids were highly consistent with the results of soil colloids.

Conclusions

The colloid collision efficiency (??) decreased as the pH of bulk solution increased and increased as the ionic strength of bulk solution increased in saturated columns packed with pure quartz sand, and NaOH solution at pH?11 poses a predominant role on mobilization of the retained colloids deposited in the primary minimum. Meanwhile, the strongly adsorbed Cu on soil colloids almost cannot be detached from its carrier under the competition of coexisted cations in the bulk solution and cotransport with its carrier under different ionic strengths.     

中性盐和pH对红壤、砖红壤胶体交换性酸的影响

In the present work, the exchangeable acidity of a red soil colloid and a latosol colloid at different pH during reacting with four neutral salts was measured. The results show that the exchangeable acidity increased with increasing amounts of the neutral salts added, and the relation between them was almost linear. When the amount of the neutral salt added was lower than a certain value, the slope of the line was high, and the slope turned low when the amount exceeded that value, so there was a turning point in each line. The addition amounts of the neutral salts for the turning points were affected by the cation species of the neutral salts, but pH had less effect on them. After the turning points occurred, the exchangeable acidity of the red soil colloid still gradually increased with the addition amounts of the neutral salts, but that of the latosol colloid did not increase any more. The exchangeable acidity in NaClO₄, KClO₄ and NaCl solutions increased at first, and then decreased with increasing pH, that is to say, peak values appeared. The peak positions of the exchangeable acidity in relation to pH changed with neutral salt solutions and were affected by the surface characteristics of the soil colloids, but not affected by the amounts of the neutral salts added. The exchangeable acidity in the Ba(NO₃)₂ solution increased continuously with increasing pH. The exchangeable acidity of the red soil colloid was obviously larger than that of the latosol colloid.     

Relation of Relative Colloid Stability Ratio and Colloid Release in Two Lead-Contaminated Soils

Potential release of soil colloids into groundwater has attracted considerable attention because of their association with heavy metals. Much effort has been focused on using colloid-deposition-based parameters (batch experiment) to predict colloid release in soils (column experiment), though they are two separate processes. In this paper, relative colloid stability ratio was estimated and used to relate to colloid release in soils. Changes in colloid release with incubation times were measured in two lead-contaminated soils. Colloid stability ratio (W) is defined as the ratio of the colloid flocculation rate of a suspension under normal observation conditions (slow flocculation) to the rate under rapid flocculation conditions. Assuming that colloid flocculation rate is related to changes in light absorbency of a solution, relative colloid stability ratio (RW) was estimated by dividing the rate of absorbency change of soil suspension observed in 0.06 M NaCl (slow flocculation) by that in 0.01 M CaCl₂ (rapid flocculation) electrolyte solutions. Both colloid release and R W changed randomly with incubation times in both soils. However, colloid release generally increased as RW increased with correlation coefficients of 0.67–0.89. This result suggests that the overall colloid release from these soils was related to RW, even though they are different conceptually. However, research is needed to further develop the concept of using relative colloid stability ratio to predict colloid release in soils.     

铬与对氯苯胺的交互作用对其在土壤胶体上的反应的影响

Adsorption of Cr(VI) and p-chloroaniline on three typical soil colloids and pH influence were studied using batch equilibrium method.Both of Cr(VI) and p-chloroaniline adsorption on the colloids could be well described by general adsorption simulation equations,The adsorption processes changed with media pH.When Cr(VI) and p-chloroaniline coexisted on soil colloids,their interactions could be observed in a certain pH range to be accompanied with Cr(VI) reduction,which clearly suggested that a surface catalytic reaction occurred in this system.Soil colloid acted as an effcient catalyst for the interaction of Cr(VI)and p-chloroaniline.The pH values at which no interaction was observed were 4.0,4.5and 5.0 for the colloids of indigotic black soil,yellow-brown soil and latosol,respectively,Capillary electrophoresis used to analyze p-chloroaniline provided a high separation efficiency and short separation time,and needed no more extensive pretreatment of samples.     

2︰1和1︰1型黏土矿物胶体凝聚中Hofmeister效应的比较研究

土壤胶体是土壤具备肥力与生态功能的物质基础,土壤胶体凝聚与分散影响着土壤中一系列微观过程和宏观现象。采用动态光散射技术比较研究三种碱金属阳离子(Li+、Na+、K+)引发不同类型黏土矿物(2︰1型蒙脱石和1︰1型高岭石)胶体凝聚中的Hofmeister效应。研究发现,Li+、Na+、K+作用下蒙脱石、高岭石胶体的凝聚速率、临界聚沉浓度及活化能都存在明显差异,表现出强烈的Hofmeister效应。当电解质浓度为20 mmol·L–1时,K+引发蒙脱石胶体凝聚的速率为66.61 nm·min–1,远高于Na+、Li+引发蒙脱石胶体凝聚速率(5.93、4.41 nm·min–1);而与之对应的临界聚沉浓度则呈现K+(蒙脱石21.8 mmol·L–1、高岭石34.6 mmol·L–1)低于Na+(蒙脱石57.6 mmol·L–1、高岭石85.8 mmol·L–1)低于Li+(蒙脱石81.8 mmol·L–1、高岭石113.9 mmol·L–1)规律,胶体凝聚中活化能可合理解释此现象。电解质浓度为25 mmol·L–1时,Li+、Na+、K+引发蒙脱石、高岭石胶体凝聚的活化能分别为1.97 kT、1.43 kT、0 kT和2.94 kT、1.71 kT、0.49 kT,说明蒙脱石、高岭石胶体凝聚过程中Hofmeister效应序列均为Li+相似文献   

非均质性对保守溶质及蒙脱石胶体在饱和多孔介质中运移的影响

选取2种粒径玻璃珠构建6种不同构型的柱子(2个均质和4个非均质),研究了饱和条件下多孔介质构型对保守溶质和蒙脱石胶体运移的影响。结果表明:在2种均质介质中,保守溶质的穿透曲线相似且对称,蒙脱石胶体在大粒径玻璃珠中的移动性更强。当介质中存在大孔隙通道时,优先流现象的出现会加速保守溶质和蒙脱石胶体的迁移,大孔隙通道与周围介质交界面越大保守溶质和蒙脱石胶体的拖尾现象越明显且穿透峰较低。在大、小粒径玻璃珠均匀混合填装的柱子中,保守溶质穿透曲线形状与均质柱子相似,蒙脱石胶体的移动性介于大、小粒径玻璃珠均匀填装的柱子之间。蒙脱石胶体在玻璃珠分层填装的柱子中,大粒径与小粒径交界面区域会有更多的蒙脱石胶体滞留。研究表明非均质性对保守溶质和蒙脱石胶体在土壤和地下环境中的运移过程有重要的影响。     

我国几种主要土壤胶体的NH4+吸附特征

本文讨论我国几种主要土壤胶体的NH₄⁺吸附特征。土壤胶体对NH₄⁺的吸附符合两种表面Langmuir方程。土壤胶体对NH₄⁺的结合能力强弱顺序是:黄棕壤>黑土、(土娄)土>红壤>砖红壤,而NH₄⁺的解吸率大小顺序与此相反。Langmuir吸附方程参数K₁与土壤胶体的粘粒矿物组成有关,并与土壤胶体对NH₄⁺的相对偏好性(A值)呈正相关。Langmuir参数(M₁+M₂)与土壤胶体的CEC呈正相关,去有机质(OM.)前后△K₁与△OM.呈反相关。去有机质可增加土壤胶体对NH₄⁺的偏好性。土壤胶体的NH₄⁺吸附和解吸特征决定于其组成和表面性质,并受有机无机复合作用的影响。永久电荷吸附位对NH₄⁺的偏好性较强,而可变电荷吸附位则较弱。     

不同耕作方式对紫色水稻土团聚体及有机碳分布的影响

The effect of different tillage systems on the size distribution of aggregates and organic carbon distribution and storage in different size aggregates in a Hydragric Anthrosol were studied in a long-term experiment in Chongqing, China. The experiment included three tillage treatments： conventional tillage with rotation of rice and winter fallow （CT-r） system, no-till and ridge culture with rotation of rice and rape （RT-rr） system, and conventional tillage with rotation of rice and rape （CT-rr） system. The results showed that the aggregates 0.02-025 mm in diameter accounted for the largest portion in each soil layer under all treatments. Compared with the CT-r system, in the 0-10 cm layer, the amount of aggregates 0.02 mm was larger under the RT-rr system, but smaller under the CT-rr system. In the 0-20 cm layer, the organic carbon content of all fractions of aggregates was the highest under the RT-rr system and lowest under the CT-rr system. The total organic carbon content showed a positive linear relationship with the amount of aggregates with diameter ranging from 0.25 to 2 mm. The storage of organic carbon in all fractions of aggregates under the RT-rr system was higher than that under the CT-r system in the 0-20 cm layer, but in the 0-60 cm soil layer, there was no distinct difference. Under the CT-rr system, the storage of organic carbon in all fractions of aggregates was lower than that under the CT-r system; most of the newly lost organic carbon was from the aggregates 0.002-0.02 and 0.02-0.25 mm in diameter.     

胶体态磷和溶解态磷在不同土壤磷饱和度稻田土壤中形态分布

Soil dissolved phosphorus (P) and colloidal P mobilization could be closely related to the degree of phosphorus saturation (DPS). Effects of a wide range of DPS on the distributions of dissolved P and colloidal P in a paddy soil profile were investigated in this study. Dissolved P and colloidal P in water-dispersible soil colloid suspension increased obviously with increasing DPS. The change point of DPS was at 0.12 by using a split-line model. Above the value, dissolved P (3.1 mg P kg-1 ) in soil profile would increase sharply and then transfer downward. Compared with dissolved P, colloidal P was the dominant fraction (78%-91%) of P in soil colloid suspension, and positively related to DPS without a significant change point. The high release of colloids in subsoils with low DPS was attributed to the low ionic strength and high pH value in subsoils. The DPS also had a significant and positive correlation with electrical conductivity (EC), but it showed a negative correlation with pH value. However, the concentration of colloidal P was not greatly correlated to the pH value, EC and optical density of the soil colloid suspension. The results indicated that DPS was an important factor that may affect the accumulation and mobilization of water-extractable colloidal P and dissolved P.