宁波土壤中多环芳烃的健康风险评价

以宁波地区土壤中多环芳烃的含量调查结果为基础,采用美国能源部风险评估信息系统的暴露量化方法和美国环保局健康风险评估手册的风险表征方法,评估了土壤中16种多环芳烃对户外劳作者的健康风险。结果表明,宁波户外劳作者由于土壤中多环芳烃引起的平均非致癌危害指数为1.09×10-5,平均致癌风险值为3.17×10-7,可判定对人体健康的危害较小。宁波地区致癌多环芳烃含量最高暴露点致癌风险值为1.45×10-6,没有超过致癌风险水平上限（10-4）,说明致癌风险尚在可接受范围内。多环芳烃中苯并（a）芘对综合致癌风险贡献最大,贡献率高达65.6%,应注意防范土壤中该污染物引起的健康危害。宁波户外劳作者受到的非致癌危害和致癌风险主要由直接摄入途径和皮肤接触途径贡献,两种途径对非致癌危害和致癌风险贡献率分别达到89%和100%,呼吸摄入引起的非致癌危害和致癌风险则相对较小。     

模拟酸雨胁迫对赤红壤磷素形态特征的影响

通过田间小区模拟酸雨实验,研究酸雨胁迫下赤红壤不同磷素形态变化的方向和程度。结果表明,原位模拟酸雨影响下,一定强度（pH≥4.0）的酸雨胁迫能有效促进有效磷的释放,而当pH〈4.0强度酸雨胁迫时有效磷的释放随pH值降低逐渐受到抑制。随酸雨酸度的增强,土壤酸性磷酸酶和微生物量磷均呈现先升高后降低的变化趋势,可见一定强度酸雨胁迫能促进溶磷微生物和磷酸酶活性,而当高强度酸雨胁迫时土壤微生物活动逐渐受到抑制。无机磷组分中Al-P、Ca-P和Fe-P含量均随酸雨酸度的增强而降低,土壤O-P含量没有显著变化。相关分析发现,有效磷含量与微生物量磷、酸性磷酸酶呈极显著正相关,表明此时土壤有效磷变化与有机磷矿化关系最为密切。有效磷含量与各种形态无机磷（Al-P、O-P、Ca-P和Fe-P）含量之间也有较强的正相关性,表明土壤生态系统磷素转化是一个自我调节的动态平衡过程,且在一定条件下可以相互转化。     

Effect of Lime and Flooding on Phosphorus Availability and Rice Growth on Two Acidic Lowland Soils

Abstract

Loss of soil‐water saturation may impair growth of rainfed lowland rice by restricting nutrient uptake, including the uptake of added phosphorus (P). For acidic soils, reappearance of soluble aluminum (Al) following loss of soil‐water saturation may also restrict P uptake. The aim of this study was to determine whether liming, flooding, and P additions could ameliorate the effects of loss of soil‐water saturation on P uptake and growth of rice. In the first pot experiment, two acid lowland soils from Cambodia [Kandic Plinthaqult (black clay soil) and Plinthustalf (sandy soil)] were treated with P (45 mg P kg^?1 soil) either before or after flooding for 4 weeks to investigate the effect of flooding on effectiveness of P fertilizer for rice growth. After 4 weeks, soils were air dried and crushed and then wet to field capacity and upland rice was grown in them for an additional 6 weeks. Addition of P fertilizer before rather than after flooding depressed the growth of the subsequently planted upland rice. During flooding, there was an increase in both acetate‐extractable Fe and the phosphate sorption capacity of soils, and a close relationship between them (r²=0.96–0.98). When P was added before flooding, Olsen and Bray 1‐extractable P, shoot dry matter, and shoot P concentrations were depressed, indicating that flooding decreased availability of fertilizer P. A second pot experiment was conducted with three levels of lime as CaCO₃ [to establish pH (CaCl₂) in the oxidized soils at 4, 5, and 6] and four levels of P (0, 13, 26, and 52 mg P kg^?1 soil) added to the same two acid lowland rice soils under flooded and nonflooded conditions. Under continuously flooded conditions, pH increased to over 5.6 regardless of lime treatment, and there was no response of rice dry matter to liming after 6 weeks' growth, but the addition of P increased rice dry matter substantially in both soils. In nonflooded soils, when P was not applied, shoot dry matter was depressed by up to one‐half of that in plants grown under continuously flooded conditions. Under the nonflooded conditions, rice dry matter and leaf P increased with the addition of P, but less so than in flooded soils. Leaf P concentrations and shoot dry matter responded strongly to the addition of lime. The increase in shoot dry matter of rice with lime and P application in nonflooded soil was associated with a significant decline in soluble Al in the soil and an increase in plant P uptake. The current experiments show that the loss of soil‐water saturation may be associated with the inhibition of P absorption by excess soluble Al. By contrast, flooding decreased exchangeable Al to levels below the threshold for toxicity in rice. In addition, the decreased P availability with loss of soil‐water saturation may have been associated with a greater phosphate sorption capacity of the soils during flooding and after reoxidation due to occlusion of P within ferric oxyhydroxides formed.     

滩涂土壤有机碳空间分布与围垦年限相关性分析

中国具有治理和修复潜力的滨海滩涂盐土面积约为2000hm2。滨海滩涂盐土作为新成土壤,土体发育不明显、理化性状差、肥力水平低下。该文通过对东台境内表层土壤有机碳的采样分析,在ArcGIS地理信息系统及SPSS16.0系统平台上,利用地统计分析模块中的克里格法分析东台市表层土壤有机碳的空间变异规律,并分析不同滩涂围垦年限下表层土壤有机碳、总氮、pH值、EC1:5的变化特征及其相关关系,结果显示滨海表层土壤有机碳含量与总氮、围垦年限呈极显著正相关,相关系数r分别为0.959和0.749,与pH值、电导率EC1:5呈极显著负相关,相关系数r分别为-0.478和-0.649。围垦3a以上表层土壤有机碳可增加0.24%左右,总氮质量分数增加0.02%左右;围垦时间大于52a,有机碳质量分数自0.1%增加到1.6%,全氮质量分数自0.03%增加到0.12%,养分等级也相应从6级增加到3级。该文研究表明,滨海盐土随着围垦年限的增长,土壤碳储量与总氮含量随之增加、pH值与EC1:5随之降低,耕地质量也相应提高。     

根系及盐分含量对农田土壤干缩裂缝发育规律的影响

为研究不同根系含量和盐分含量土壤表面干缩裂缝的发育规律,该文提出了一套基于数字图像处理的裂缝几何参数提取方法,分析裂缝形态随含水率的变化规律。结果表明:随着含水率的降低,不同根系含量条件下裂缝面积密度和长度密度的差异显著(P0.05),裂缝发育稳定时根系含量越大,面积密度越小,长度密度越大。盐分质量分数为2.0%的土壤试样在整个干燥过程中裂缝面积密度明显比其他低盐分含量的试样高。当含水率27%时,盐分含量对土壤裂缝面积密度的影响差异明显,不同盐分含量的土壤裂缝面积密度和长度密度均差异显著(P0.05),说明盐分含量越大,稳定时土壤裂缝面积密度越大,长度密度越小。该成果对指导开裂土壤的农田灌溉具有重要的实践意义。     

黑土区土壤侵蚀厚度对土地生产力的影响及其评价

为了研究黑土区土壤侵蚀厚度对土地生产力的影响,采用盆栽试验,人为剥离黑土表层0、5、10、15、20、25和30 cm土壤以模拟侵蚀厚度不同的耕层土壤,分析土壤侵蚀厚度对土壤理化性质、大豆生物性状和水分利用效率等指标的影响。并对TOPSIS(technique for order preference by similarity to ideal solution)模型进行改进,用于评价侵蚀厚度不同的土壤的土地生产力。结果表明:土壤全N、碱解N、全P、速效P、有机质含量和土壤田间持水率均随侵蚀厚度的增加而递减,土壤容重随侵蚀厚度的增加而递增。土壤侵蚀厚度对大豆生长有显著影响,随着侵蚀厚度的增加,大豆减产率呈"S型"曲线递增,产量、耗水量呈"Z型"曲线递减,水分利用效率呈指数曲线关系递减。改进的TOPSIS模型对不同侵蚀厚度下土地生产力的评价结果较为理想,计算的土地生产力指数随土壤侵蚀厚度的变化呈"Z型"曲线,与大豆产量的变化趋势相同,且二者呈指数函数关系,决定系数达0.996,均方根误差为0.65。研究结果可为黑土区土壤侵蚀防治提供理论依据。     

黄土高原丘陵区退耕还林地土壤碳氮库的动态变化(英文)

为了揭示坡耕地退化土壤植被恢复后土壤中碳(C)、氮(N)运移规律,采用植被次生演替空间序列代替时间序列的方法,研究了黄土丘陵沟壑区纸坊沟流域不同植被恢复模式下的C、N库及其相互关系在土壤剖面的时空变化。结果表明退化农地的造林显著地促进了CO2的固存,恢复了土壤N的可获得性,进而降低了N不足对可持续的CO2固存的限制。植被恢复显著地促进了0~60 cm土壤有机碳(soil organic carbon,SOC)和总氮(total nitrogen,TN)的积累,而只有在高于一定的恢复时间阈值(如26 a)下,促进了SOC库和TN库间的线性相关性。在土壤剖面上,SOC和TN库、SOC/TN库比以及SOC-TN间的线性相关性均随着土壤深度的增加而降低。与自然恢复相比,人工林在短期内具有CO2固存的优势,但由于随着恢复时间的增加,SOC增幅越来越大于TN增幅的事实,表明造林对碳固存的可持续性需在一个较长的时段下来评估,尤其需要关注20 cm以下层土壤。研究结果为黄土高原的生态修复和减缓温室效应提供了理论依据。     

土壤优先流运动的活动流场模型分形特征参数计算

活动流场模型分形特征参数控制着优先流的产生和发展,因此准确获得活动流场模型分形特征参数值对提高模型的模拟预测精度具有重要意义。该研究采用染色示踪方法,将优先流流场从流动背景中显示出来,通过数字图像分析和采样分析获得优先流流场和流场内土壤含水率的分布模式,根据活动流场模型本构方程拟合活动流场模型分形特征参数值;针对3种常见的入渗后染色区内土壤含水率分布模式,分别提供了相应的活动流场模型分形特征参数的计算方法。研究结果显示,1）由于入渗后土壤水重分布的影响,活动流场区域和染色区域在整个入渗深度范围并不完全重合,因此仅可选择活动流场与染色区域相重合深度范围内受土壤初始含水率影响较小的数据来拟合活动流场模型分形特征参数值;2）土壤质地对入渗后染色区内土壤含水率的分布模式有显著影响,细质地土壤中入渗后染色区土壤含水率沿入渗方向逐渐减小,粗质地土壤中入渗后染色区土壤含水率沿入渗方向先增大后减小。     

Some characteristics of the humus in soil types (part 3) composition groups of humus

In most literature on soil, the term humus has been used as synonymous with soil organic matter, on the other hand, it has been applied to a portion of soil organic matter that has decomposed and has lost the structure of the original matter, from which it has derived. Scheffer and Schachtschabel ¹⁾ defined the humus not synonymously with soil organic matter, but, in a broad sense, as all the dead organic substances which are accumulated on the soil surface as well as in the soil layer, and undergo continually decomposition, alteration, and synthetic reactions. According to them, the composition groups of humus are divided into non-humic and humic, and the latter group is sub-divided into (1) fulvic acid and humo-lignin acid, (2) humic acid, (3) humin, and (4) humus coal. Some natures of these composition groups of humus are shown in Table 1.     

Role of active aluminum in the formation of water-stable macroaggregates

Soil structure is determined by the arrangement of particles in soil and the particles of sand, silt, and clay bind together into aggregates of various sizes by organic and inorganic materials. Structural stability which is the ability of the aggregates and pores to remain intact when subjected to stress, markedly affects crop production and soil erosion (Tisdall 1996). Since water, either directly as rainfall or as surface runoff is the main agent of aggregate breakdown, in the analyzes of stable soil aggregation, the term water-stable aggregation is generally used (Lynch and Bragg 1985). Water-stable aggregates have been divided into micro aggregates < 0.25 mm dia.) and macro aggregates (> 0.25 mm dia.) (Edwards and Bremner 1967; Tisdall and Oades 1982). Microaggregates show a relatively high stability against physical disruption (Edwards and Bremner 1967). On the other hand, macro aggregates are sensitive to soil management (Tisdall and Oades 1982).

There are many reports on the relationships between the aggregate stability and the soil physicochemical properties. For example, significant correlations were found between the aggregate stability and the amounts of organic C (Tisdall and Oades 1982), total N, and carbohydrates or the CEC (Chaney and Swift 1984). However, most of these studies were conducted in non-volcanic ash soils. Volcanic ash soils are widely distributed in Japan and are very important soils for crop production. The objective of this study was, therefore, to obtain more information on the relationship between the degree of macro aggregation and the soil physicochemical properties in non-volcanic and volcanic ash soils.