小流域范围土壤锰、铝形态分布及其相关性研究

分别在湖南的郴州和长沙选定两小流域(SZY和LKS),从小流域规模分析了酸雨频降区两小流域土壤的主要理化特性和土壤锰铝形态及其分布,并讨论了锰铝各形态和土壤有机质,土壤pH值之间的相关性。结果表明:在小流域SZY土壤中,各种形态的锰铝含量均高于小流域LKS土壤中对应形态的锰铝含量;在同一剖面,各种形态的锰铝含量有表土高于底土的趋势。在两小流域土壤中,除无定形锰(Mnox)外各种形态的锰铝均与土壤有机质呈正相关。铝的溶出与土壤有机质和土壤pH值有关。酸沉降能影响毒性元素铝形态的转化和淋溶。活性铝、锰形态可能富集在土壤表层或植物根际等富含有机质的区域,酸沉降或其它环境条件可能促进铝、锰形态在土壤表层或植物根际的转化和溶出,从而导致毒害。     

纳米TiO_2对土壤中Al、Fe和Mn释放及形态的影响

为了研究纳米TiO2对土壤中Al、Fe和Mn形态转化的影响,以三峡水库消落区土壤为研究对象,采用室外模拟淹水试验,分析不同浓度的2种纳米TiO2对土壤中Al、Fe和Mn释放及形态的影响。结果表明,淹水2个月后,纳米TiO2颗粒处理引起上覆水Al和Fe浓度显著升高;促进土壤残渣态和可氧化态Al的释放,且锐钛矿颗粒的作用大于金红石颗粒,高浓度锐钛矿颗粒处理导致12.31%的Al释放到水中;纳米TiO2颗粒对土壤Fe和Mn总量影响较小,但对Fe形态转化影响较大,主要表现为可还原态和可氧化态Fe转化为酸可交换态Fe,促进Fe的活化,其中低浓度金红石颗粒与高浓度锐钛矿颗粒影响相对较大;纳米TiO2颗粒对Mn形态转化影响较小,仅低浓度金红石颗粒与高浓度锐钛矿颗粒处理组促进少量可还原态Mn的转化,其他均无明显变化。因此,不同结构纳米TiO2对土壤中Al、Fe和Mn形态转化的影响存在较大差异,在进行纳米TiO2的环境风险评估时需要区别对待。     

EGCG溶液浓度与酸碱度对黄壤Al、Fe和Mn形态的影响

植物多酚可通过络合作用改变元素的存在形态。采用双因素完全随机试验设计,通过浸提试验研究表没食子儿茶素没食子酸脂(EGCG)溶液浓度、酸碱度、浓度与酸碱度互作对黄壤可溶态、游离态、无定形态和络合态铝(Al)、铁(Fe)和锰(Mn)的影响。结果表明:EGCG溶液浓度对黄壤可溶态和络合态Al、Fe、Mn及无定形态Al、Fe均产生极显著影响,EGCG溶液酸碱度对黄壤可溶态及无定形态Al、Fe、Mn均产生显著或极显著影响,EGCG溶液浓度与酸碱度对黄壤可溶态Al、Fe、Mn,无定形态和络合态Al也有极显著或显著的互作效应。相关分析结果显示,土壤中3种元素的无定形态氧化物含量与对应的可溶态氧化物含量呈显著或极显著负相关,表明EGCG溶液主要通过改变氧化物形态,特别是无定形态氧化物含量,影响元素活化,进而改变其可溶态含量;Al和Mn的活化会使土壤滤液pH降低,在pH降低幅度较大时,可能导致土壤酸化。本试验一方面为研究酸性茶园土壤酸化的来源提供了方向,另一方面也可为植物Al/Mn毒害的防治提供参考,但在利用植物多酚类物质防治土壤Al/Mn毒害的同时要处理好土壤酸化与治理毒害的关系。     

三峡库区小江流域消落带土壤Zn各形态有效性及缓变型地球化学灾害分析

通过分析三峡库区小江流域消落带土壤Zn全量、形态及有效性,并基于缓变型地球化学灾害数学模型,研究了区域内土壤Zn的缓变型地球化学灾害特征。结果表明:研究区域内全量Zn的平均值为123.88 mg/kg,高于国家土壤环境质量一级标准,但明显低于二级标准。Zn的酸溶态、可还原态、可氧化态、残渣态平均值占全量平均值的百分比分别为2.93%、4.42%、8.71%和83.94%,有效态占4.51%。酸溶态、可还原态、可氧化态与有效态相关性密切;可还原态和可氧化态含量对有效态含量贡献较大。在小江流域消落带的土壤中Zn具有缓变型地球化学灾害特征,土壤中Zn有可释放总量向次生相态释放转化的趋势,其缓变型地球化学灾害临界值为130.67 mg/kg,32%的土壤样品具有爆发Zn缓变型地球化学灾害的可能性。     

酸沉降对地表生态系统的影响I.土壤中铝的活化与迁移

土壤中Al的活化与迁移是酸沉降对地表生态系统最突出的影响之一,也是土壤缓冲酸沉降的重要过程。因此土壤中Al的活化迁移过程成为研究和预测地表酸化及其生态效应的关键环节。然而由于土壤系统和Al形态的复杂性,目前的模式并不能充分与实验室和野外的数据相吻合。本文从Al的形态、释放机制和在土壤剖面中迁移过程等方面对近年来的研究工作进行综述和评价,并在此基础之上对今后的研究工作提出展望。     

腐殖质对白浆土中Fe、Mn、Al形态转化及磷生物有效性的影响

在三江平原布置长期试验，研究连年施用有机肥后土壤腐殖质变化及其对白浆±Fe、Mn、Al形态转化及磷生物有效性的影响。结果表明，施用牛粪后土壤腐殖质含量升高，且以松结态腐殖质的增长为主；土壤的DTPA提取态和有机络合态Fe、Mn、Al含量上升，使土壤有效态磷含量上升。因此，生物措施是治理白浆土，促进土壤磷素养分有效性上升，增大土壤缓冲容量和抗逆性的有效措施。     

氮添加对巴音布鲁克高寒湿地土壤无机磷形态的影响

为探究在全球气候变化敏感区的干旱区高寒湿地上,氮添加对土壤无机磷形态的影响。在保护良好的巴音布鲁克高寒湿地沼泽(S)、沼泽草甸(SM)和草甸(M)布设野外原位试验,依据巴音布鲁克草原氮沉降量,设置0(CK),8(N1),16(N2) kg·N/(hm²·a)的施氮量,研究短期氮添加对高寒湿地土壤无机磷形态的影响。结果表明:(1)高寒湿地土壤全磷含量平均为1.09 g/kg,总无机磷平均为492.71 mg/kg,而总无机磷平均占全磷的45.67%。(2)3种湿地类型土壤无机磷主要以Ca—P形态存在,在Ca—P中以Ca₁₀—P为主,占无机磷含量的50.27%~64.69%。S区土壤Al—P、Fe—P含量显著高于SM和M区,SM区Ca₂—P、Ca₈—P、O—P含量显著高于S和M区,M区土壤Ca₁₀—P含量显著高于S和SM区。(3)氮添加显著影响高寒湿地土壤各形态无机磷的含量,氮添加下,S和SM区土壤Al—P含量较CK显著增加了9.92%~17.35%,而Ca₈—P含量显著降低3.18%~9.36%。[JP]S和M区土壤Fe—P含量显著降低了3.18%~9.36%,S区土壤Ca₂—P含量显著降低了10.31%。氮添加下3种湿地类型土壤O—P含量均显著增加,较CK显著增加21.83%~25.94%。(4)土壤pH、有机碳、碱解氮和速效钾均是影响无机磷形态的重要因子。不同湿地类型土壤无机磷形态含量存在显著差异,氮添加显著改变了土壤各无机磷形态含量,主要是通过增加土壤中难利用无机磷(O—P)含量,使高寒湿地土壤的供磷潜力降低。研究结果有助于预测未来氮沉降持续增加背景下全球高寒湿地土壤无机磷形态的变化趋势。     

降水酸度对马尾松根际环境中铝形态的影响

为了探明降水酸度对植物根际环境中铝形态的影响,以马尾松为例,采用根箱栽培、配制不同pH值的模拟酸雨以室外模拟酸雨喷淋法研究马尾松根际及非根际土壤中铝形态的特征及规律.研究结果表明:酸雨对土壤中铝化合物具有溶蚀作用,可促进土壤里活性铝离子(Al3+)溶出,并且酸雨pH值越低,活性铝离子累积溶出量越大,溶出的铝所形成的铝形态在马尾松根际土壤与非根际土壤以及根际不同土层之间存在一定差异,马尾松根际pH值和根系分泌物协同影响铝形态的动态变化.根际土壤中有机铝结合态含量增加.交换态铝含量则稍稍下降.     

腐殖质对白浆土中Fe、Mn、Al形态转化及磷生物有效性的影响

在三江平原布置长期试验，研究连年施用有机肥后土壤腐殖质变化及其对白浆±Fe、Mn、Al形态转化及磷生物有效性的影响。结果表明，施用牛粪后土壤腐殖质含量升高，且以松结态腐殖质的增长为主；土壤的DTPA提取态和有机络合态Fe、Mn、Al含量上升，使土壤有效态磷含量上升。因此，生物措施是治理白浆土，促进土壤磷素养分有效性上升，增大土壤缓冲容量和抗逆性的有效措施。     

淹水还原条件下红壤中葡萄糖及腐殖酸对铁锰形态的影响

通过设置不同的葡萄糖/腐殖酸配比模拟还原性土壤体系,考察长期(约74 d)淹水培养过程中铁锰元素在土壤溶液/矿物相中的分布形态演变。结果表明:在淹水培养初期,葡萄糖的添加可以促进铁锰离子的还原溶出,同时土壤中可交换态和酸可提取态铁、以及可交换态锰的含量也会随之增加;而腐殖酸的添加则会促进土壤中可氧化态铁/锰含量的升高。随着培养时间的增加,铁锰离子浓度及各个土壤提取形态的铁锰含量大多呈现降低趋势,铁锰元素逐渐转化成提取性更低的矿物形态。因此,淹水环境中铁锰还原溶出-分布形态演变受到土壤中有机物质种类和含量的显著影响,呈现出不同的金属移动性和生物有效性。     

Distribution of rare-earth (Y,La, Ce) and other heavy metals in the profiles of the podzolic soil group

Along with Fe and Al, many heavy metals (Mn, Cr, Zn, Cu, and Ni) show a markedly pronounced eluvial-illuvial redistribution in the profiles of soils of the podzolic group. The intensity of the redistribution of the bulk forms of these metals is comparable with that of Fe and exceeds that of Al. Although the podzolic soils are depleted of rare-earth metals, the latter respond readily to soil podzolization. The inactive participation of Al is explained by an insignificant portion of the active reaction-capable fraction. Podzolization does not influence the profile distribution of Sr and Ba. The leaching degree of heavy metals such as Mn, Cr, Zn, Ni, and Zr is noticeably higher in the sandy podzols than in the loamy podzolic soils. Leaching of heavy metals from the podzolic horizons is of geochemical importance, whereas the depletion of metals participating in plant nutrition and biota development is of ecological importance. The leaching of heavy metals is related to the destruction of clay particles in the heavy-textured podzolic soils; the effect of the soil acidity on the leaching of heavy metals is less significant.     

Bulk sediment bioassays with five species of fresh-water oligochaetes

The fluxes of metals (Na, K, Ca, Mg, Fe, Mn, Al, Cu, Zn, Pb, Cd, Cr, and Ni) in two spruce forest soils in S. Sweden were quantified using the lysimeter technique. Amounts in precipitation (dry and wet), throughfall, litterfall and annual accumulation in biomass were also quantified, as well as stores in soil and biomass. The metal concentrations of the soil solutions varied greatly according to season. The leaching of some metals (Fe, Cu, Pb, Cr, and organic forms of Al) was associated with the leaching of organic matter. These complexes were leached from the A horizon in considerable amounts. They were precipitated in the upper B horizon and only small amounts were transported further downward. By contrast, the leaching of Na, Mg, Ca, Mn, Cd, Zn, Ni, and inorganic forms of Al increased with increasing soil depth. The concentrations of these metals also increased with increasing soil solution acidity. The highest concentrations were often found at the transition to the C horizon. The amounts of Na, K, Mg, Ca, Mn, Al, Zn, Cd, Cr, and Ni leached from the rooting zone were found to be larger than the amounts deposited from the atmosphere, the main source of these metals being the mineral soil. The reverse was true of Ph, Cu, and Fe, the sink being the upper part of the B horizon.     

红壤中铝的形态

以改进的连续分级提取方法,用１ｍｏｌ／Ｌ,ＫＣｌ,０．２ｍｏｌ／Ｌ,ＨＣｌ,０．１ｍｏｌ／Ｌ Ｎａ４Ｐ２Ｏ７（ｐＨ８．５）,ＤＣＢ溶液,０．３３ｍｏｌ／Ｌ,柠檬酸钠和０．５ｍｏｌ／Ｌ ＮａＯＨ为提取剂,把红壤中可提取的非晶态铝区分为交换态铝,肿附态无机羟基铝,有机配合态铝,氧化铁结合态铝,层间铝和非晶态铝硅酸盐。     

N Leaching from Small Upland Headwater Catchments in Southwestern Norway

We investigated nitrogen leaching and input-output budgets from 12 small, upland headwater catchments with differing fractions of peat, heather and bare rock in SW Norway. A close relationship was found between annual inorganic nitrogen loss and the fractional cover bare rock explaining 74% of the variation. It was not possible to distinguish between the N leaching from the peat and heather dominated catchments in this investigation. Nitrate loss was negatively correlated to the C/N ratio of the soil organic horizon. Lowest soil C/N ratios of the soil organic surface horizon occurred in catchments receiving the highest amounts of N deposition. Our data for Norwegian moorland are in agreement with previous investigations relating soil C/N ratio and N leaching in forest soils. Runoff from the catchments showed a seasonal pattern in NO₃ ^? concentrations. The low values during the summer are presumably due to increased biological activity (plant uptake and immobilization by soil microbes). The winter and spring NO₃ ^? concentrations in 2001 in all catchments were much higher than in 2000, perhaps due to soil freezing.     

外源铜和镍在土壤中的化学形态及其老化研究

采用连续提取法测定了外源铜和镍进入田间土壤后的化学形态分布,比较研究了这2种重金属在3种不同类型土壤(红壤,水稻土和潮土)中随老化时间的形态转化和分布.结果表明,外源铜以残留态(40%～60%)和EDTA可提取态(40%)为主;随老化时间,EDTA可提取态、易还原锰结合态及铁铝氧化态向残留态转化;外源镍在酸性红壤中以可交换态(40%)和残留态(30%～50%)为主,在中性水稻土中以EDTA可提取态(30%)和残留态(30%～50%)为主,在碱性潮土中以铁铝氧化态(20%)和残留态(40%)为主.随老化时间,水溶态、可交换态、EDTA可提取态等向残留态转化.土壤pH较低时水溶态和可交换态含量较高,但是同时随老化时间的降低量也明显;pH较高时有利于易还原锰结合态和有机质结合态的转化.     

Distribution of aluminum in black spruce saplings growing on two New Brunswick forest soils with contrasting acid sulfate sorption

Two adjacent soils with contrasting sulfate sorption were examined in terms of (i) water-soluble and ion-exchangeable Al, Fe, Ca, Mg, K, Mn and Zn, (ii), water- and bicarbonate-extractable sulfate, (iii) Truog-extractable P, (iv) dithionite-extractable Al, Mn and Fe and (v) treatment response to irrigation with simulated acid precipitation. The biomass of 8 year old black spruce saplings growing on the soils, and the distributions of Al, Fe, Ca, Mg, K, Mn, P and Zn within these plants, were also examined. The soils were well to moderately-well drained, with the mineral soil exposed by site preparation prior to planting. The exposed soil underneath individual saplings was treated with acid sulfate solutions (75 mm containing 2 to 50 mg L^?1 H₂SO₄) applied during each of three consecutive growing seasons. The results indicate that Al, much like Fe, Ca, Mn and Zn, accumulated with time in the foliage, but K, Mg and P were highest in young plant tissues. Much of Al and Fe taken up remained in the fine roots. Aluminum uptake increased with the amount of dithionite-extractable Al (free Al oxide) in the soil. Growth of the black spruce saplings was not visibly affected by readily accessed Al in each soil, or by acid irrigation.Instead, growth was restricted by factors other than soil Al and acid irrigation in spite of (i) low soil pH, (ii) high levels of exchangeable Al, and (iii) high levels of Al in fine roots. Sulfate retention across and within the two soils was positively correlated with free Al oxide. The two soils responded to acid irrigation by accelerated silicate weathering and enhanced ion leaching. Sulfate sorption reduced these effects.     

An assessment of EDTA as an extractant of organic-complexed and amorphous forms of Fe and Al in soils

EDTA solutions proposed as selective extractants of amorphous and organic forms of Fe and Al in soils and synthetic materials were tested. Extraction of Fe and Al from some soil samples continued at a decreasing rate beyond 120 days. For some soil samples and synthetic materials the amounts of Fe and Al extractable by EDTA (90 days) were markedly lower than those extractable by acid ammonium oxalate (2 h). Extraction of samples for 1 h with EDTA was shown to release amounts of Fe and Al far below those considered to be complexed with organic matter. The EDTA extraction procedures tested should not replace either acid ammonium oxalate for estimating amorphous forms of Fe and Al or pyrophosphate for estimating organic forms of Fe and Al in soils.     

Impact of Soil Sorption Characteristics and Bedrock Composition on Phosphorus Concentrations in two Bohemian Forest Lakes

Phosphate (PO₄-P) sorption characteristics of soils and bedrock composition were determined in catchments of two mountain lakes, Ple?né Lake (PL) and ?ertovo Lake (CT), situated in the Bohemian Forest (Czech Republic). The aim was to explain higher terrestrial P export to mesotrophic PL compared to oligotrophic CT. Concentrations of Al and Fe oxides were the dominant parameters affecting soil ability to adsorb PO₄-P. Depending on concentrations of Al and Fe oxides, P sorption maxima varied from 9.7 to 70.5 mmol kg^?1 and from 7.4 to 121 mmol kg^?1 in organic and mineral soil horizons, respectively. The catchment weighted mean PO₄-P sorption capacity was 3.4 mol m^?2 and 11.9 mol m^?2 in the PL and CT soils, respectively. The higher PO₄-P sorption capacity in the CT catchment was predominantly associated with higher pools of soil and Fe oxides. The CT bedrock (mica schist) released one order of magnitude less P than the PL bedrock (granite) within a pH range of catchment soils (pH_CaCl2 of 2.5–4.5). The higher ability of PL bedrock to release P and the lower ability of PL soils to adsorb PO₄-P thus contributed to the higher terrestrial P loading of this lake.     

钢铁工业区降尘对周边土壤的影响

分别在南京的两个钢铁厂收集降尘并采集周边表土,并用ICP-AES和磁化率仪分析得到16种元素含量和表土、地面尘的磁化率。结果表明,两个钢铁工业区的大气降尘的年沉降通量分别为190t km-2a-1和407 t km-2a-1,这可能会影响着周边地区土壤的形成;Al、K、Na、Ti、V在降尘中的含量显著低于表土,而Ca,Fe,Zn,Mn,Pb,Cu在降尘中含量要显著高于表土;表土的磁化率除水田外均大于100×10-8m3kg-1,并且地面尘的磁化率要远远高于表土的磁化率。研究表明,钢铁工业区降尘对其周边土壤中污染元素的积累有明显影响,突出地表现在土壤表层重金属含量升高,而磁化率可以很好地表征这种表聚的特点。