石灰性土壤环境中缺锌机理的探讨

作者认为石灰性土壤中锌活性较低的原因,是由于碳酸盐导致土壤pH上升,在较高pH条件下氧化铁对锌的强烈固定,造成了大量专性吸附状态的氧化铁结合态锌及部份碳酸盐结合态锌,使交换态的有效锌含量很低,同时还证明:自然的石灰性土壤中,松结有机态锌与碳酸盐结合态是活性锌的直接给源,外源加入的锌仅为松结右机态锌。此外,石灰性土壤中各主要土壤的化学组份对外源锌的固定量高伛顺序为:氧化铁>有机质>粘土矿物>碳酸盐>氧化锰:对土壤中原有锌的固定作用大小依次为:粘土矿物>氧化铁>有机质>氧化锰>碳酸盐。     

Management of basiphilous dune slack communities in relation to carbonate accumulation and hydrological conditions

In dune slacks in The Netherlands, a decline of rare mesotrophic basiphilous plant species and their plant communities has been observed in combination with an increase of more productive systems with common, taller acidophilous plant species. This has been attributed to both natural and anthropogenic changes. In a humid climate with a precipitation surplus, as in The Netherlands, the calcium carbonate content of a calcareous soil increases with depth. However, soils in coastal dune slacks, may have a higher carbonate content in the topsoil horizon than in the underlying layers. Carbonates which buffer the pH can prolong the presence of mesotrophic basiphilous plant communities which are of high conservation value. To explain the occurrence of calcareous surface horizons in dune slacks, hydrological and micromorphological analyses were carried out in three dune slacks. Two slacks are situated on the Wadden Sea islands in the northern part of The Netherlands; one on Schiermonnikoog and one on Texel. The third slack is situated in the dunes on the island of Goeree in the southwestern part of The Netherlands. In all three slacks, carbonate occurs as mollusc and gastropod fragments (silt- or sand-sized) and as micritic nodules in the topsoil layer, due to aeolian deposition and sedimentation by water.In situ carbonate accumulation (calcitans and calcareous crusts) due to CO₂ release in inundated and/or capillary rise of calcareous groundwater near, or at the soil surface. Accumulation of carbonate also occurs as a result of biological activity by algae in the topsoil of the Goeree site. In general, hydrological processes maintaining high levels of calcareous groundwater are a prerequisite for the maintenance of high carbonate levels in topsoils. Such levels are necessary for the conservation and management of basiphilous pioneer vegetation.     

Are calcareous soils in uplands less prone to damage from road salting than acidic soils?

Previous studies of upland roadside soils in Cumbria, that would normally be naturally acidic, have highlighted that (a) runoff from roads subjected to long-term road salting can dramatically raise soil pH down slope in upland areas; (b) the soil pH increase dramatically changes N cycling in soils down slope, increasing mineralisation of organic matter, ammonification, ammonium leaching down slope and nitrification and nitrate leaching; (c) the increase in nitrification substantially increases nitrate leaching to down-slope rivers, and this is readily detectable in field studies; and (d) loss of soil organic matter over decades of salting is so great that organic matter is no longer substantially solubilised by high salt concentrations found in soil solution below road drains. This paper tests and supports the hypothesis that such effects are minimal for more calcareous soil ecosystems. It examines the soil and soil solution chemistry on another Cumbrian upland highway, the A686 near Leadgate, Alston. Sodium % of soil CEC values for soil transects affected by spray containing road salt are similar at both the A6 and A686 sites. However, spatial trends in calcium, magnesium, ammonium, and nitrate concentrations as well as pH differ, as a direct result of the higher weathering rate of parent material and possibly also the presence of limestone walls above both spray-affected and control transects at the A686 site.     

污泥施用对林地土壤基本性质及酶活性的影响

以无锡卢村污水处理厂厌氧消化的脱水污泥为有机肥源,采用土培盆栽试验的方法,研究了不同用量污泥施用后土壤基本性质的变化及对土壤酶活性的影响。试验设计5种处理,污泥施用量和占土质量的比例分别为0（不施污泥的对照处理,CK）,30（3%）,60（6%）,120（12%）和240（24%）g·kg^-1。结果表明,污泥使用提高了土壤中养分元素和有机质的含量;黄棕壤中过氧化氢酶的活性平均比潮土中的高5.2%,随污泥用量的增加潮土中过氧化氢酶活性提高,而黄棕壤中的无明显变化;与对照相比,土壤脲酶活性在两种土壤上分别增加55.6%～122%（黄棕壤）和46.2%～67.5%（潮土）,且与土壤全氮、全磷、水解氮、速效磷和有机质（黄棕壤）和土壤全氮、水解氮和有机质（潮土）呈正相关;结果还显示污泥使用增加了土壤蔗糖酶活性,但不同污泥用量之间无明显差异。     

Distribution and possible immobilization of lead in a forest soil (Luvisol) profile*

Geochemical analyses using a sequential extraction method and lead adsorption studies were carried out in order to characterize the distribution and adsorption of lead on each genetic horizon of a Luvisol profile developed on a pelagic clayey aleurolite. Clay illuviation is the most important pedogenic process in the profile studied. Its clay mineralogy is characterized by chlorite/vermiculite species with increasing chlorite component downward. The amount of carbonate minerals strongly increases in the lower part of the profile resulting in an abrupt rise in soil pH within a small distance. The Pb content of the soil profile exceeds the natural geochemical background only in the Ao horizon, and its amount decreases with depth in the profile without correcting for differences in bulk density, suggesting the binding of Pb to soil organic matter. According to the sequential extraction analysis the organic matter and carbonate content of the soil have the most significant effect on lead distribution. This effect varies in the different soil horizons. Lead adsorption experiments were carried out on whole soil samples, soil clay fractions, as well as on their carbonate and organic matter free variant. The different soil horizons adsorb lead to different extents depending on their organic matter, clay mineral and carbonate content; and the mineralogical features of soil clays significantly affect their lead adsorption capacity. The clay fraction adsorbs 25 more lead than the whole soil, while in the calcareous subsoil a significant proportion of lead is precipitated due to the alkaline conditions. 10 and 5 of adsorbed Pb can be leached with distilled water in the organic matter and clay mineral dominated soil horizons, respectively. These results suggest that soil organic matter plays a decisive role in the adsorption of Pb, but the fixation by clay minerals is stronger.*This study was presented at the 20th European SEGH conference in Debrecen, Hungary, 2002.     

Improved soil carbonate determination by FT-IR and X-ray analysis

In forest soils on calcareous parent material, carbonate is a key component that influences both chemical and physical soil properties and thus fertility and productivity. At low organic carbon contents, it is difficult to distinguish between organic and inorganic carbon, e.g. carbonates, in soils. The common gas-volumetric method to determine carbonate has a number of disadvantages. We hypothesize that a combination of two spectroscopic methods, which account for different forms of carbonate, can be used to model soil carbonate in our region. Fourier transform mid-infrared spectroscopy was combined with X-ray diffraction to develop a model based on partial least squares regression. Results of the gas-volumetric Scheibler method were corrected for the calcite/dolomite ratio. The best model performance was achieved when we combined the two analytical methods using four principal components. The root mean squared error of prediction decreased from 13.07 to 11.57, while full cross-validation explained 94.5 % of the variance of the carbonate content. This is the first time that a combination of the proposed methods has been used to predict carbonate in forest soils, offering a simple method to precisely estimate soil carbonate contents while increasing accuracy in comparison with spectroscopic approaches proposed earlier. This approach has the potential to complement or substitute gas-volumetric methods, specifically in study areas with low soil heterogeneity and similar parent material or in long-term monitoring by consecutive sampling.     

An alternative method to measure carbonate in soils by FT-IR spectroscopy

Measurements of calcium carbonate contents in soils were performed with FT-IR (Fourier transform infrared) spectroscopy and with the gas volumetric Scheibler method. To the authors’ knowledge it is the first time that carbonate was quantified in soil samples by FT-IR spectroscopy. The carbonate contents of the test soils ranged from 11.3 to 13.1%. Both methods gave similar results, however, results obtained from FT-IR spectra depend on the spectral band used for the carbonate determination. In our investigation we used the bands at 875 and 2506 cm⁻¹. In case of the band at 2506 cm⁻¹ the difference between FT-IR and Scheibler method was a factor of 1.56, in case of 875 cm⁻¹ the respective factor was 1.16. It can be concluded that FT-IR with both bands has a potential to be used in practice as substitution of the Scheibler method. The advantages of the FT-IR method are better reproducibility and the simultaneous characterization of soil organic matter in bulk samples. The disadvantage is its higher cost.     

不同剖面层次土壤磷素运移研究

以陕西杨凌地区塿土为研究对象,通过饱和稳定流土柱运移试验,测定磷酸盐(H_2PO_4~-)在不同层次土壤中的运移穿透曲线(BTC),应用CDE模型、CXTFIT软件程序对其实测穿透曲线(BTC)进行拟合求其运移参数,研究其运移规律。结果表明,磷酸盐在塿土中的运移受到土壤的强烈阻滞作用,随着CaCO_3含量增加,磷酸盐运移所受的阻滞作用增大。磷酸盐在塿土不同剖面层次中运移所受阻滞作用大小与CaCO_3含量呈极显著的正相关,r=0.9791;而与粘粒含量且成极显著的负相关、r=0.9318。磷酸盐在塿土不同土层运移所受阻滞作用大小顺序为:钙积层>堆垫表层>粘化层,其阻滞因子R值分别为:11.80～13.00,5.20～7.00,3.90～5.00。     

Lead redistribution in a mine soil treated with three manures and incubated at two different temperatures

The study of heavy metals’ redistribution between different fractions allows to know their bioavailability and mobility in soils. Soil samples were collected from a lead mine in Hamadan provinces, NW Iran. In a factorial experiment soil was treated with cow, sheep and poultry manures (20?g?kg^?1 soil) separately and incubated near field capacity at 10°C and 37°C. An untreated soil (as control) was also incubated at the same temperatures. After 0 and 120 days, a sequential extraction scheme was used to fractionate Pb of incubated samples into soluble-exchangeable (Sol-Exch), organic matter associated (AOM), carbonates associated (ACar), and residual (Res) forms. Soil Pb in Sol-Exch and AOM fractions were increased by manure application significantly. The AOM and ACar forms of Pb were higher in soils treated with the manures and incubated in lower temperature. In contrast, the Sol-Exch and Res chemical forms of Pb were higher in the soils incubated at 37°C. These results may be related to the higher calcium carbonate dissolution and organic matter decomposition because of better biological activity in the soils incubated in higher temperature. The increase of the Res fraction (stable form) in this condition may resulted in lower toxicity and mobility in soil environment.     

中国南方稻田土壤汞含量及潜在危害评价

选择我国南方水稻主产区安徽、浙江、湖南、湖北以及广西5个省,采集213个稻田土壤样品,探究我国南方稻田土壤中汞的空间分布特征与土壤理化参数(如p H值和有机质)的相关关系及汞富集的潜在危害。结果表明:不同省份的稻田土壤汞含量存在显著的差异(P0.05,n=213),含量范围是0.029~0.326 mg·kg~(-1)(干重),平均值为(0.094±0.036)mg·kg~(-1),与农用地土壤环境质量标准0.30 mg·kg~(-1)(GB15618—1995)相比,除湖北省以外均有轻度汞污染。Pearson相关性分析表明,稻田土壤中的汞含量与有机质含量呈显著正相关关系(P0.01,r=0.445),说明适度偏高的有机质有利于土壤汞的富集。不同省份稻田土壤潜在危害等级除浙江省外均在轻微到中等的范围内,浙江省的为强等级。     

吉林西部不同开发年份盐碱水田土壤有机碳和碳酸盐的季节动态

水稻土是中国主要的耕作土壤,在陆地土壤碳循环研究中具有重要现实意义。针对吉林西部水田土壤的特征,将无机碳库纳入土壤碳库研究,以典型灌区前郭县为例,野外采集盐碱地和已开发5、15、25、35、55年的5种不同水田表层土壤,建立实验样地,在水稻生长的幼苗期、分蘖期、长穗期和结实期采集土壤样品,用TOC仪分别测试表层土壤有机碳和碳酸盐含量,分析其季节动态规律和开发年份特征。结果表明：吉林西部盐碱水田土壤有机碳呈现“减-增-减”的季节变化规律,水稻生长的幼苗期和分蘖期有机碳含量下降,长穗期含量上升,结实期含量下降,碳酸盐季节变化规律与其相反,二者季节变化呈显著负相关;经历一个生长季后,开发5、15、25、35、55年的土壤有机碳含量分别增加了2.98%、3.53%、3.66%、2.72%、2.30%,碳酸盐含量分别增加了4.07%、2.15%、1.08%、1.61%、11.36%,说明研究区水田生长期具有碳汇作用;与未开发盐碱地相比,开发的5、15、25、35、55年生长季土壤平均总碳量分别增加了89.81%、121.03%、137.22%、188.28%,有机碳含量分别增加了284.28%、392.00%、456.37%、559.08%、666.06%,碳酸盐含量分别降低了13.49%、22.84%、32.23%、43.53%、62.40%;开发年份越长,水田土壤总碳和有机碳含量越高,碳酸盐含量越低;总碳的增加来自有机碳的增加;盐碱地开发有利于土壤碳汇。水稻生长期温度和降雨量影响土壤有机碳和碳酸盐季节变化。     

铅在紫色土—水稻体系中的植物效应及形态

本文研究了酸性、中性及石灰性紫色土中铅的水稻效应、形态特征及有效性。酸性与石灰性紫色土中水稻分别在含铅量1000、2000mg/kg时出现明显受害,中性紫色土在4000mg/kg时亦无明显影响。水稻各部位含铅量是酸性>石灰性>中性紫色土,并与添加铅呈显著正相关,且其大小顺序为根>茎叶>糙米。铅90％以上积累于水稻根部;施铅使土壤中无效铅比例下降。有效性较高的铅形态比例上升。交换态、碳酸盐态或弱结合态铅含量较高的土壤上,水稻反应大。用有效态铅为指标有可能使不同土壤铅临界浓度比较接近一致。     

几种统计学方法在环境影响因子辨识中的应用

分析比较了相关分析法、多元线性回归法与逐步回归法在环境影响因子辨识中的功能异同点。以甘肃省白银市为例 ,用 3种统计学方法对城郊土壤 -作物系统重金属污染影响因子进行判别 ,提出了研究区土壤污染修复方案选择指标的建议     

Sorption of heavy metals on organic and inorganic soil constituents

Sorption of heavy metals to organic matter and mineral soil constituents can hardly be separated experimentally. Here we studied the retention capacity of organic matter and minerals from soils in a long-term field experiment in which the organic carbon content had been altered, but the mineral phase had remained constant over time. The sorption of Cu, Cd and Zn showed a non-additive contribution of soil organic matter and minerals to the sorption capacity of soil. Sorption on organic matter exceeded mineral sorption from 6 to 13 times. This is the first time that sorption to soil organic matter is quantified in bulk soils.     

绿黄隆、甲黄隆在江苏省农区5种土壤中残留活性的研究

采用改进的玉米主根长土培生测法，研究绿黄隆、甲黄隆在江苏省典型农区土壤中残留活性。结果表明，两种除草剂在５种土壤中剂量与玉米主根长抑制率之间皆达极显著相关，土壤ｐＨ和有机质含量是主要影响因素，碱性轻质土壤中活性较高，酸性重质土壤中活性较低，活性大小顺序为：黄潮土＞高沙土＞砂姜黑土＞滨海盐土＞太湖水稻土。     

土壤酸化与油菜锰毒关系研究

对湖北省的主要旱地土壤种植多茬作物后油菜生产锰毒的原因进行了研究。结果表明,供试土壤pH值较原土样下降了1．0个单位。除石灰性土壤外,其它中酸性土壤交换性锰明显增加,造成油菜对锰吸收过量,同时由于吸收过程中锰铁拮抗作用的存在,植株在土壤锰毒发生后吸收的铁量下降,使体内锰铁比上升。     

Effect of acid rain on the fractionation of heavy metals and major elements in contaminated soils

Acid rain is a serious environmental problem worldwide. In the present study, we investigated the effect of acid rain (1:1 equivalent basis H₂SO₄:HNO₃) at pH values of 2.0, 4.0 and 7.0 on the fractionation of heavy metals (Cd, Cu, Fe, Mn, Ni, Pb and Zn) and major elements (K, Na, Ca, and Mg) in contaminated calcareous soils over a 2084 h period. Heavy metals and major elements in soil samples were fractionated before and after 2084 h kinetic release using a sequential extraction procedure. Before kinetic studies the predominant fractions of K, Na, Ca, Mg, Cd and Ni were mainly associated with carbonate fraction (CARB), whereas Fe, Mn and Zn were associated with the Fe–Mn oxide fraction (Fe–Mn oxide). The highest percentage of Pb and Cu were found in the exchangeable (EXC) and organic matter (OM) fractions, respectively. After kinetic study using different simulated acid rain solutions, the major fractions of heavy metals (expect of Cu) and Na was the same as before release. Upon the application of different acid rain solutions, K and Mg were found dominantly in Fe–Mn oxide fraction, whereas Ca was in the EXC fraction. The results provide valuable information regarding metal mobility and indicated that speciation of metals (Cu and Zn) and major elements in contaminated calcareous soils can be affected by acid rain.     

土壤固相不同组分对镉,锌吸持的研究

本文选用三种不同类型的土壤，用连续提取法依次去除土壤固相中碳酸盐（石灰性土壤）、锰、有机质、无定型氧化铁和晶型氧化铁组分，制得分离某一组分或某几个组分后的土壤钙饱和的样品，藉此研究土壤固相各组分对重金属Ｃｄ和Ｚｎ吸持的影响，研究结果表明，不同土壤去除某一组分或多个组分后对Ｃｄ和Ｚｎ吸持的影响是不同的，土壤固相中组分的相互作用可能是其主要原因。     

Effects of organic matter on the specific adsorption of heavy metals by soil

The adsorption of heavy metals on soil from the Neihu Landfill Site in Taipei City was investigated in order to assess the groundwater pollution problems. The effects of soil organic matter and the behaviors of organic complexing ligands like EDTA and humic acid to the overall adsorption process were studied and discussed. For explaining the results, the pH value of soil system and the properties of the soil/aqueous interface were chosen as two significant and interacted factors for discussion. The concept of the specific adsorption mechanism was also demonstrated and discussed. The results showed that the complexing ligands existing in soil liquid phase have more influences than natural organic matter does. The competitive sequences of different organic matter contents indicated that organic functional sites preferentially bind with Cu and Cd. The presence of EDTA and humic acid which formed ligandlike complexes will reduce Cd adsorption efficiency. These effects will induce mobility and the fate of heavy metals in soils, such as bioavailability.     

Assessing the potential for lead release from road dusts and soils

Lead release from several soil and road dust samples -- obtained from various locations in the London Borough of Greenwich -- has been investigated as a function of acid and chloride addition. The work shows that lead retention in dust samples is primarily dependent upon buffer capacity, which in turn appears to be related to carbonate content. The continuing addition of acid eventually overcomes the buffer capacity of the system. At this point lead is rapidly released. For the soils investigated buffer capacities appear to be small and in these cases lead is readily released. The supplementary addition of chloride to the samples can have contrary effects upon release. For the dust samples chloride enhances lead release due, presumably, to the formation of chloro--lead complexes. However for one soil sample chloride hinders lead release possibly by binding anionic chloro--lead complexes to anionic exchange sites formed by the protonation of surface hydroxyl groups in the soil matrix.