重金属污染对土壤有机质积累的影响

采用田间采样分析与室内培养试验相结合的方法,研究了不同重金属污染土壤中有机质积累的差异及重金属污染强度对土壤有机质矿化动态变化的影响.结果表明：污染土壤中重金属的大量积累可减弱有机物质的矿化速率,增加土壤有机质的积累.土壤中颗粒态有机质及其占总有机碳的比例随重金属积累的增加而增加;而微生物生物量碳占总碳的比例却随土壤重金属污染水平的提高而下降.污染土壤中颗粒态有机质对重金属有显著的富集,这可能是影响土壤有机物质进一步矿化的原因之一.重金属污染可改变土壤有机质的矿化速率,影响土壤有机质的积累与分配.     

基于小波变换的土壤有机质含量高光谱估测术

利用统计分析方法选取了土壤N、P、K元素含量近似而有机质含量差异较大的样本60个,通过高光谱探测分析获得样本反射率对数的一阶导数光谱,采用Bior 1.3函数进行多层离散小波分解,剔除低频近似信号和高频噪声信号,得到反映土壤理化参数的特征光谱曲线;采用相关分析筛选土壤有机质含量的显著相关波段,基于显著相关波段和特征光谱曲线分别构建土壤有机质含量高光谱多元回归估测模型;通过比较分析,确定了提取土壤有机质特征光谱的最佳小波分解尺度并构建了最佳预测模型.结果表明:提取土壤有机质特征光谱的最佳小波分解层数是9层,其次是8层和10层;基于小波9层分解特征光谱曲线的有机质含量估测模型最佳,其决定系数(R2)为0.89,比基于显著相关波段构建模型的R2增加了0.31,比基于原始光谱所构建模型的R2增加了0.10.     

基于小波变换的土壤有机质含量高光谱估测

利用统计分析方法选取了土壤N、P、K元素含量近似而有机质含量差异较大的样本60个,通过高光谱探测分析获得样本反射率对数的一阶导数光谱,采用Bior 1.3函数进行多层离散小波分解,剔除低频近似信号和高频噪声信号,得到反映土壤理化参数的特征光谱曲线;采用相关分析筛选土壤有机质含量的显著相关波段,基于显著相关波段和特征光谱曲线分别构建土壤有机质含量高光谱多元回归估测模型;通过比较分析,确定了提取土壤有机质特征光谱的最佳小波分解尺度并构建了最佳预测模型.结果表明： 提取土壤有机质特征光谱的最佳小波分解层数是9层,其次是8层和10层;基于小波9层分解特征光谱曲线的有机质含量估测模型最佳,其决定系数（R²）为0.89,比基于显著相关波段构建模型的R²增加了0.31,比基于原始光谱所构建模型的R²增加了0.10.     

一种估测土壤有机质含量的近红外光谱参数

通过系统分析我国中、东部地区5种不同类型土壤风干样本的有机质含量与近红外(1000～2500 nm)光谱反射率和一阶导数两波段构成的比值、差值及归一化指数之间的关系,构建了适合土壤有机质含量估测的光谱参数及定量反演模型.结果表明：用多元散射校正及Savitzky-Golay平滑方法对原始光谱反射率进行预处理后,其两波段组成的光谱参数与土壤有机质含量的相关性明显优于原始光谱反射率组成的光谱参数,而由上述预处理后的反射率一阶导数的两波段构成的光谱参数介于二者之间;不同类型光谱参数构成形式中,以差值指数的预测性最好,其次为比值和归一化指数;与土壤有机质含量相关程度最高的光谱参数,是以近红外合频区1883和2065 nm 2个波段的反射率经多元散射校正和Savitzky-Golay平滑后构建而成的差值指数DI(CR₁₈₈₃, CR₂₀₆₅),两者呈极显著的直线相关.经不同类型土壤的观测资料检验,模型的决定系数为0.837,均方根误差为4.06;与偏最小二乘法的全谱建模结果相比,尽管DI(CR₁₈₈₃, CR₂₀₆₅)的预测精度略低于后者,但该指数只使用了2个波段的反射率,且所建模型比较简单,能为便携式监测仪的研制提供更有效的信息,可作为一种良好的土壤有机质估测光谱参数.     

Effect of inoculant strain and organic matter content on kinetics of 2,4-dichlorophenoxyacetic acid degradation in soil.

We monitored rates of degradation of soluble and sorbed 2,4-dichlorophenoxyacetic acid (2,4-D) in low-organic-matter soil at field capacity amended with 1, 10, or 100 micrograms of 2,4-D per g of wet soil and inoculated with one of two bacterial strains (MI and 155) with similar maximum growth rates (mu max) but significantly different half-saturation growth constants (Ks). Concentrations of soluble 2,4-D were determined by analyzing samples of pore water pressed from soil, and concentrations of sorbed 2,4-D were determined by solvent extraction. Between 65 and 75% of the total 2,4-D was present in the soluble phase at equilibrium, resulting in soil solution concentrations of ca. 8, 60, and 600 micrograms of 2,4-D per ml, respectively. Soluble 2,4-D was metabolized preferentially; this was followed by degradation of both sorbed (after desorption) and soluble 2,4-D. Rates of degradation were comparable for the two strains at soil concentrations of 10 and 100 micrograms of 2,4-D per g; however, at 1 microgram/g of soil, 2,4-D was metabolized more rapidly by the strain with the lower Ks value (strain MI). We also monitored rates of biodegradation of soluble and sorbed 2,4-D in high-organic-matter soil at field capacity amended with 100 micrograms of 2,4-D per g of wet soil and inoculated with the low-Ks strain (strain MI). Ten percent of total 2,4-D was present in the soluble phase, resulting in a soil solution concentration of ca. 30 micrograms of 2,4-D per ml.(ABSTRACT TRUNCATED AT 250 WORDS)     

Effect of inoculant strain and organic matter content on kinetics of 2,4-dichlorophenoxyacetic acid degradation in soil.

We monitored rates of degradation of soluble and sorbed 2,4-dichlorophenoxyacetic acid (2,4-D) in low-organic-matter soil at field capacity amended with 1, 10, or 100 micrograms of 2,4-D per g of wet soil and inoculated with one of two bacterial strains (MI and 155) with similar maximum growth rates (mu max) but significantly different half-saturation growth constants (Ks). Concentrations of soluble 2,4-D were determined by analyzing samples of pore water pressed from soil, and concentrations of sorbed 2,4-D were determined by solvent extraction. Between 65 and 75% of the total 2,4-D was present in the soluble phase at equilibrium, resulting in soil solution concentrations of ca. 8, 60, and 600 micrograms of 2,4-D per ml, respectively. Soluble 2,4-D was metabolized preferentially; this was followed by degradation of both sorbed (after desorption) and soluble 2,4-D. Rates of degradation were comparable for the two strains at soil concentrations of 10 and 100 micrograms of 2,4-D per g; however, at 1 microgram/g of soil, 2,4-D was metabolized more rapidly by the strain with the lower Ks value (strain MI). We also monitored rates of biodegradation of soluble and sorbed 2,4-D in high-organic-matter soil at field capacity amended with 100 micrograms of 2,4-D per g of wet soil and inoculated with the low-Ks strain (strain MI). Ten percent of total 2,4-D was present in the soluble phase, resulting in a soil solution concentration of ca. 30 micrograms of 2,4-D per ml.(ABSTRACT TRUNCATED AT 250 WORDS)     

干旱荒漠区土壤有机质空间变异特征

以内蒙古阿拉善左旗为例 ,研究了干旱荒漠区土壤有机质的空间变异特征。传统统计分析结果表明 ,研究区内土壤有机质含量总体水平较低 ,平均为 6 .6 5 g/ kg;变异系数为 1.4 2 ,属强变异。在半方差结构分析和球状模型套合的基础上 ,结合普通Kriging插值方法 ,分析了土壤有机质的地统计特征。比较不同趋势效应和异向性的普通 Kriging插值的误差结果表明 ,宜考虑各向异性和二阶趋势效应。获得了研究区土壤有机质含量的等值线图 ,并分析了其空间分布规律     

高原鼠兔对高寒草甸土壤有机质及湿度的作用

为探讨高原鼠兔对土壤理化性质的作用, 本研究于2005年8月, 采用灼烧和烘干法, 分别测定了高原鼠兔栖息及被灭杀地区土壤有机质含量及湿度。结果表明： 高原鼠兔栖息地区, 0～5 cm及6～10 cm土壤层有机质含量和湿度均极显著或显著高于被灭杀地区; 11～30 cm 土壤层, 二者无显著的差异;31～50 cm土壤层, 有机质含量差异极显著, 而土壤湿度则无显著差异。说明, 高原鼠兔活动可增加高寒草甸土壤表层有机质含量和湿度, 进而改变土壤理化性质, 促进生态系统物质循环。     

Salinity affects microbial activity and soil organic matter content in tidal wetlands

Climate change‐associated sea level rise is expected to cause saltwater intrusion into many historically freshwater ecosystems. Of particular concern are tidal freshwater wetlands, which perform several important ecological functions including carbon sequestration. To predict the impact of saltwater intrusion in these environments, we must first gain a better understanding of how salinity regulates decomposition in natural systems. This study sampled eight tidal wetlands ranging from freshwater to oligohaline (0–2 ppt) in four rivers near the Chesapeake Bay (Virginia). To help isolate salinity effects, sites were selected to be highly similar in terms of plant community composition and tidal influence. Overall, salinity was found to be strongly negatively correlated with soil organic matter content (OM%) and C : N, but unrelated to the other studied environmental parameters (pH, redox, and above‐ and below‐ground plant biomass). Partial correlation analysis, controlling for these environmental covariates, supported direct effects of salinity on the activity of carbon‐degrading extracellular enzymes (β‐1, 4‐glucosidase, 1, 4‐β‐cellobiosidase, β‐D‐xylosidase, and phenol oxidase) as well as alkaline phosphatase, using a per unit OM basis. As enzyme activity is the putative rate‐limiting step in decomposition, enhanced activity due to salinity increases could dramatically affect soil OM accumulation. Salinity was also found to be positively related to bacterial abundance (qPCR of the 16S rRNA gene) and tightly linked with community composition (T‐RFLP). Furthermore, strong relationships were found between bacterial abundance and/or composition with the activity of specific enzymes (1, 4‐β‐cellobiosidase, arylsulfatase, alkaline phosphatase, and phenol oxidase) suggesting salinity's impact on decomposition could be due, at least in part, to its effect on the bacterial community. Together, these results indicate that salinity increases microbial decomposition rates in low salinity wetlands, and suggests that these ecosystems may experience decreased soil OM accumulation, accretion, and carbon sequestration rates even with modest levels of saltwater intrusion.     

Dynamic responses of aboveground biomass and soil organic matter content to grassland restoration

基于1983年开始的改良恢复长期观测试验, 研究了在排除干扰的围封保护下, 不同恢复改良措施对内蒙古退化羊草(Leymus chinensis)草原群落地上生物量和土壤有机质含量动态变化过程的影响, 改良恢复措施包括浅耕翻、耙地和自然恢复。结果表明: (1)地上生物量在前期(1983-1991年)的动态变化特征为自然恢复处理显著低于浅耕翻处理, 耙地处理与其余两个处理没有显著差异。中期(1992-2006年)各处理之间无显著差异; 后期(2007-2014年)为自然恢复>耙地>浅耕翻, 且自然恢复与浅耕翻处理之间有显著差异。(2) 0-10 cm土壤有机质含量在前期的动态变化特征为浅耕翻>耙地>自然恢复, 且处理之间有显著差异, 自然恢复、浅耕翻、耙地处理相对1983年土壤有机质分别增加了21%、45%、37%; 中期和后期自然恢复处理显著大于浅耕翻处理, 耙地处理介于两个处理之间且与二者没有显著差异。中期自然恢复、浅耕翻、耙地处理有机质含量相对1983年分别增加了61%、46%、57%, 后期分别增加了67%、51%、62%。(3) 10-30 cm土壤有机质在前期浅耕翻>自然恢复>耙地, 且各处理之间有显著差异; 中期和后期各处理之间无显著差异。总之, 应依据恢复目标的不同, 选择不同的改良措施。在短时间尺度上, 浅耕翻有利于退化羊草草原生产力和土壤有机碳的快速恢复, 而长时间尺度上自然恢复和耙地的效益更明显。     

土壤含水量、pH及有机质对DMPP硝化抑制效果的影响

采用室内模拟培养试验方法,研究了土壤含水量(40％、60％和80％田间最大持水量)、pH(4、7、10)及有机质(原土和去除有机质)对3,4-二甲基吡唑磷酸盐(DMPP)在潮棕壤中硝化抑制效果的影响.结果表明:随土壤含水量的降低,DMPP的降解趋于缓慢,硝化抑制效应增强.不同土壤pH处理下,以pH为10的处理硝化抑制效果最好,DMPP的存留量最高,pH为7和4处理硝化抑制效果较低,DMPP存留量较少.去除有机质可延长DMPP的存留时间,显著降低土壤表观硝化率.     

草原群落生物量和土壤有机质含量对改良措施的动态响应

基于1983年开始的改良恢复长期观测试验, 研究了在排除干扰的围封保护下, 不同恢复改良措施对内蒙古退化羊草(Leymus chinensis)草原群落地上生物量和土壤有机质含量动态变化过程的影响, 改良恢复措施包括浅耕翻、耙地和自然恢复。结果表明: (1)地上生物量在前期(1983-1991年)的动态变化特征为自然恢复处理显著低于浅耕翻处理, 耙地处理与其余两个处理没有显著差异。中期(1992-2006年)各处理之间无显著差异; 后期(2007-2014年)为自然恢复>耙地>浅耕翻, 且自然恢复与浅耕翻处理之间有显著差异。(2) 0-10 cm土壤有机质含量在前期的动态变化特征为浅耕翻>耙地>自然恢复, 且处理之间有显著差异, 自然恢复、浅耕翻、耙地处理相对1983年土壤有机质分别增加了21%、45%、37%; 中期和后期自然恢复处理显著大于浅耕翻处理, 耙地处理介于两个处理之间且与二者没有显著差异。中期自然恢复、浅耕翻、耙地处理有机质含量相对1983年分别增加了61%、46%、57%, 后期分别增加了67%、51%、62%。(3) 10-30 cm土壤有机质在前期浅耕翻>自然恢复>耙地, 且各处理之间有显著差异; 中期和后期各处理之间无显著差异。总之, 应依据恢复目标的不同, 选择不同的改良措施。在短时间尺度上, 浅耕翻有利于退化羊草草原生产力和土壤有机碳的快速恢复, 而长时间尺度上自然恢复和耙地的效益更明显。     

土壤有机质模型的比较分析

土壤有机质作为土壤C库,其含量和动态变化对全球C循环、土壤肥力、土壤质量和健康起着重要作用。SOM模型利用经验性的假设和已有数据对土壤有机质含量和动态变化进行模拟,尤其是可以对无法取得足够必要数据的试验进行模拟,所以SOM模型成为定量研究土壤有机质积累分解的重要手段,利用SOM模型有助于对土壤有机质分解机理的研究,并且可通过SOM模型对土壤CO2排放量、植物生产量进行预测。同时也可对农业管理措施做出评估,文中对几种SOM模型进行了概述,尤其对有影响的RothC模型和CENTURY模型进行了比较分析。     

土地利用方式对土壤有机质的影响

通过对地带性常绿阔叶林、杉木人工林、农田、竹林等不同土地利用方式下土壤有机质总量、活性有机质及其组分的研究,发现土地利用方式对土壤有机质和活性有机质各组分的影响差异显著,其中阔叶林含量最高,杉木人工林低于阔叶林,竹林和农田最低。这些差别主要是由于凋落物的数量、质量以及各种管理措施不同所致。     

Primary oxidation of organic matter in the soil

Summary The course of respiration rate during glucose decomposition in a soil sample was studied. The whole process of oxidation (mineralization) is divided into two principal parts: the primary oxidation which occurs while the substrate is still present and the secondary oxidation after the disappearance of the substrate. The primary oxidation brought about by two different components: the oxidative component represents the sum of enzyme activity present originally in the soil sample, and the assimilative component is built up during the process by synthesis of microbial enzymes. The size of the oxidative component is correlated with the biological potency of soil. Sometimes, an intermediary stage can be observed at the beginning of the secondary oxidation. A method is given for enumeration of the proportions of the two components involved in primary oxidation. The biochemical and pedological meaning of these data is discussed.     

外源氧化铁对水稻土中有机酸含量的影响

在水稻土泥浆中添加Fe(OH) 3 可显著降低乙酸浓度 .在新鲜水稻土样品中 ,由于添加Fe(OH) 3导致对乙酸的竞争消耗 ,在培养 5d后 ,乙酸浓度降至 10～ 2 0 μmol·L-1的稳态浓度 ,而此刻对照中的乙酸浓度仍在 12 0 0 μmol·L-1以上 .在乙酸产生量较低的土壤中 ,添加Fe(OH) 3 可完全消耗体系中的乙酸 ,并导致产CH4过程的完全被抑制 .添加纤铁矿同样可使乙酸浓度显著减少 ,但作用效果不如无定形氧化铁 .添加赤铁矿可造成培养初期 (10d以内 )乙酸的大量积累 ,但并不引起产CH4量的增大 .添加Fe(OH) 3 、纤铁矿及铝取代针铁矿 ,能引起厌氧培养的水稻土中丙酸浓度的降低 ,其抑制效率为Fe(OH) 3 >纤铁矿 >铝取代针铁矿 .新鲜土样和经过 11周厌氧处理后的土样中 ,有机酸种类和含量有较大差别 .     

植被恢复对侵蚀红壤可溶性有机质含量及光谱学特征的影响

为了解植被恢复对侵蚀红壤可溶性有机质含量及结构特征的影响, 以福建省长汀县河田镇植被恢复后的侵蚀红壤及对照裸地为研究对象, 对两试验地0-60 cm深土壤中可溶性有机质的含量及光谱学特征进行了比较研究。结果表明: 侵蚀红壤植被恢复后, 土壤可溶性有机碳含量显著提高, 在土表到60 cm深度的6个10 cm土层中, 植被恢复土壤可溶性有机碳含量分别提高为对照裸地相应土层的5.6、4.7、4.6、3.1、2.4及2.2倍。可溶性有机氮含量在两试验地之间的差异在各土层中不一致。植被恢复各土层侵蚀红壤可溶性有机质的芳香化指数显著高于对照裸地, 荧光发射光谱腐殖化指数略高于对照裸地, 植被恢复后的侵蚀红壤与对照裸地间荧光同步光谱腐殖化指数无明显差异。荧光同步光谱图中, 两试验地侵蚀红壤可溶性有机质的吸收主要为类蛋白质及芳香性脂肪族荧光基团的吸收。傅里叶红外光谱结果显示, 与对照裸地相比, 植被恢复后的侵蚀红壤土壤可溶性有机质中官能团种类更多, 且含有更多芳香碳及羧基碳。两试验地土壤可溶性有机质均表现为芳香化及腐殖化程度随土层的加深而降低。相关性分析显示, 土壤可溶性有机质的芳香化及腐殖化指数与土壤碳氮总量有极显著正相关关系。总之, 侵蚀红壤经植被恢复后, 土壤可溶性有机碳含量及可溶性有机质的芳香化指数显著提高, 可溶性有机质的腐殖化指数略有增大, 可溶性有机质结构更复杂, 更不易被分解, 因此有利于土壤肥力的恢复。     

F污染桑叶对家蚕繁殖力的影响

对不同抗Ｆ性蚕品种的幼虫短期添食梯度浓度ＮａＦ研究Ｆ对桑蚕生殖的影响,结果表明,只要个体能正常羽化产卵,Ｆ对怀卵数、产卵数、产卵率和孵化率都无明显影响,低浓度的Ｆ对强抗Ｆ性品种蚕的生殖似有促进作用;但５龄期添食高浓度的Ｆ可引起怀卵数、产卵数和孵化率下降;Ｆ主要港集在马氏管、中肠等组织中,蚕卵中Ｆ的含量极低