酸铝胁迫下4个速生桉优良无性系的生长反应

采用砂土培育法研究不同的酸铝处理对几种桉树优良无性系（巨尾桉9号、巨尾桉12号、尾叶桉4号、韦赤桉3号）幼苗生长及膜透性等变化的影响。试验设: pH 3.0＋0 mg/L Al3+、 pH 3.0＋120 mg/L Al3+、 pH 4.0＋0 mg/L Al3+、 pH 4.0＋120 mg/L Al3+、 pH 4.8＋0 mg/L Al3+5个处理。结果表明,不同酸铝处理对4个桉树优良无性系形态、生长指标、含水率、叶绿素含量、质膜透性和脯氨酸含量等都产生不同的影响。与对照（pH 4.8＋0 mg/L Al3+）相比,pH 3.0＋120 mg/L Al3+处理对桉树幼苗的生长产生的抑制作用明显,叶、芽皱缩、变形,苗高、地径以及各器官含水率降低,质膜透性和叶绿素含量下降,桉树幼苗累积较多的脯氨酸。其中,巨尾桉广林9号对酸铝逆境的抗性优于其它3个无性系。4个桉树优良无性系抗酸铝逆境的能力强弱依次为: 巨尾桉9号巨尾桉12号 韦赤桉3号尾叶桉4号。因此,选育耐酸铝桉树无性系品系是改善南方富铝化酸性土壤林地生产力的重要策略之一。     

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。     

黔中废弃煤矿区酸性排水污染特征及对作物种苗生长的影响

通过对贵阳市花溪区麦坪乡废弃煤矿区酸性排水进行样品收集与分析,探讨煤矿酸性排水的污染特征及对作物种苗生长的影响。研究结果表明,在煤矿附近50～350m距离内溪沟水pH变化达2.35～6.3,污染物主要以SO24-、Fe、Mn为主;矸石堆洼地蓄积水完全抑制两种植物的萌发;距井口50m溪沟水和距井口30m农田水处理油菜都表现为种子发芽后发霉死亡;距井口100m处溪沟水和距井口30m农田水处理油菜和水稻的种子发芽率、幼苗鲜重和干重、发芽指数和简化活力指数与对照（蒸馏水处理）之间均存在极显著差异（P〈0.01）。煤矿酸性排水胁迫下,水稻各项指标变幅低于油菜,说明物种耐性强度为水稻〉油菜。     

低分子量有机酸作用下土壤中菲和芘的残留及形态

采用微宇宙试验方法,以菲和芘为多环芳烃(PAHs)代表物,研究了几种低分子量有机酸作用下黄棕壤中菲和芘的残留和形态。结果表明,老化60 d后土壤中菲和芘的残留含量明显减少;不施加有机酸的对照土壤中,菲和芘的残留含量为10.13和29.18 mg kg-1,去除率为87.33%和63.50%。与对照相比,供试浓度(0～64 mg kg-1)范围内,柠檬酸、草酸、酒石酸等3种低分子量有机酸作用下土壤中PAHs残留含量提高,去除率减小,表明供试条件下有机酸抑制土壤中菲和芘的降解;进一步分析发现,少量(≤4 mg kg-1)的有机酸即可对PAHs降解产生高的抑制效果。微生物降解在PAHs的去除中起重要作用,且芘比菲更抗微生物降解。供试条件下,可脱附态和有机溶剂提取态是土壤中菲和芘存在的主要形态,而结合态残留占总残留的比例很小(<8.5%)。3种有机酸均提高了土壤中可脱附态和有机溶剂提取态菲和芘的残留含量,施加有机酸使土壤中菲和芘的可脱附态含量较对照分别提高了46.67%～749.1%和1.83%～80.20%,有机溶剂提取态则提高了8.73%～375.2%和22.63%～114.3%;低分子量有机酸作用下结合态的菲和芘含量仍很小。     

几种胡敏酸还原容量的表征与比较

还原容量(RC)是衡量胡敏酸(HA)还原特性的重要指标。采用饱和H2振荡法和土壤溶液法对HA分别进行化学和微生物预处理,分别以硝酸铁(Fe(NO3)3)、柠檬酸铁(FeCit)作电子受体,测定了三种HA(上海巨枫SH,天津光复TJ,缙云山JY)的本底还原容量(NRC),化学还原容量(CRC),微生物还原容量(MRC)。对不同电子受体条件下、不同初始状态和不同种类的胡敏酸的RC进行比较。结果表明：三种HA中,以缙云山土壤提取的胡敏酸RC值最高,还原容量最大,分别为20.21?0.26mmolc mol-1C (NRC)、26.02?1.12mmolc mol-1C (CRC)和29.29?1.56mmolc mol-1C (MRC)。两种电子受体中,采用Fe(NO3)3得到的RC明显高于在FeCit条件下。另外,溶液态HA的RC明显高于固态。由此证明胡敏酸还原容量是一个相对量;其容量大小不仅和自身结构、性质有关,也受到HA初始形态和不同电子受体的影响。对比三个还原容量指标发现CRC和MRC显著大于NRC,而CRC和MRC之间无明确大小关系,因此用CRC来表征HA被微生物还原后的还原容量(MRC)还需作进一步验证。     

Effects of Irrigation Patterns and Nitrogen Fertilization on Rice Yield and Microbial Community Structure in Paddy Soil

Water and nitrogen (N) are considered the most important factors affecting rice production and play vital roles in regulating soil microbial biomass, activity, and community. The effects of irrigation patterns and N fertilizer levels on the soil microbial community structure and yield of paddy rice were investigated in a pot experiment. The experiment was designed with four N levels of 0 (N0), 126 (N1), 157.5 (N2), and 210 kg N ha-1 (N3) under two irrigation patterns of continuous water-logging irrigation (WLI) and water-controlled irrigation (WCI). Phospholipid fatty acid (PLFA) analysis was conducted to track the dynamics of soil microbial communities at tillering, grain-filling, and maturity stages. The results showed that the maximums of grain yield, above-ground biomass, and total N uptake were all obtained in the N2 treatment under WCI. Similar variations in total PLFAs, as well as bacterial and fungal PLFAs, were found, with an increase from the tillering to the grain-filling stage and a decrease at the maturity stage except for actinomycetic PLFAs, which decreased continuously from the tillering to the maturity stage. A shift in composition of the microbial community at different stages of the plant growth was indicated by principal component analysis (PCA), in which the samples at the vegetative stage (tillering stage) were separated from those at the reproductive stage (grain-filling and maturity stages). Soil microbial biomass, measured as total PLFAs, was significantly higher under WCI than that under WLI mainly at the grain-filling stage, whereas the fungal PLFAs detected under WCI were significantly higher than those under WLI at the tillering, grain-filling, and maturity stages. The application of N fertilizer also significantly increased soil microbial biomass and the main microbial groups both under WLI and WCI conditions. The proper combination of irrigation management and N fertilizer level in this study was the N2 (157.5 kg N ha-1) treatment under the water-controlled irrigation pattern.     

模拟酸雨条件下海泡石对污染红壤镉、铅淋溶的影响

采用填充土柱淋溶试验研究不同pH值模拟酸雨和海泡石添加量对重金属污染红壤Cd、Pb淋溶的影响.结果表明,Cd在酸雨pH值较低时累积淋溶量较大,Pb的累积淋溶量随酸雨pH值的降低逐渐增加,pH值为3.5处理的Pb总累积淋溶量显著高于其他pH值处理(高出54.9％).与对照相比,模拟酸雨pH值为3.5时,添加5 g/kg和10 g/kg海泡石处理Cd的总累积淋溶量明显增加(分别增加24.6％和26.3％),而Pb的总累积淋溶量分别显著降低34.7％和25.7％;酸雨pH值为4.5时,添加5 g/kg和10g/kg海泡石处理降低了Cd的累积淋溶量(分别降低13.0％和1.4％),而Pb的淋溶量随海泡石添加量的增加而降低,10 g/kg海泡石处理的Pb总累积淋溶量显著下降17.6％;pH值为5.5和6.5时,海泡石处理Cd累积淋溶量均有所下降,而对Pb的淋溶无显著降低效果.酸雨酸性强度的增大增加了Cd、Pb的淋溶风险,且Pb比Cd敏感.添加海泡石可有效减少酸雨对土壤中Pb的淋溶,但其对Cd淋溶的影响受酸雨酸性强度的影响.     

小麦耐热及热敏感基因型在高温胁迫下膜透性及膜脂组分的差异

高温逆境下,植物膜透性的增加导致细胞代谢紊乱并诱导热激基因表达.脂肪酸是构成生物膜的主要物质,饱和脂肪酸的含量及饱和程度高,有利于保持膜在高温时的流动性和稳定性.本研究利用小麦(Triticum aestivum)耐热基因型TAM107和热敏感基因型中国春(CS)为对象,研究了高温胁迫对膜透性、叶绿素荧光参数Fv/Fm、膜脂组分及其相关脂肪酸去饱和酶基因(FAD7)表达的影响,结果表明,高温胁迫下,两基因型膜透性均增加,膜脂中的三烯脂肪酸含量下降,但TAM107变化幅度明显高于中国春,在脂肪酸水平上说明耐热小麦品种的膜系统较热敏感品种对高温逆境有较强的耐受性;中国春比TAM107中FAD7的表达对高温更加敏感,这直接影响了热胁迫前后膜脂中三烯脂肪酸含量的变化,在转录水平上说明了耐热小麦基因型较热敏感基因型对高温逆境有较强的耐受性.三烯脂肪酸含量在热胁迫前后的变化可作为一种新的耐热鉴定指标.     

Absorption spectra of humic acids

For the purpose of explaining the forming process of soil humic acids, the author determined the absorption spectra of various humic acids. From soils and peats which were pretreated with 5% HCl at 70°C for 30 minutes or from those which were not, humic acids were extracted by treating with 0.5% NaOH at boiling temperature for 30 minutes. In these humic acids, the one which is extracted after acid pretreatment is provisionally designated as SrL humic acid and the other as L humic acid. The supernatant alkaline solutions obtained by centrifuging the above mentioned extracts were acidified with hydrochloric acid, and precipitated humic acids were filtered and washed with water until Cl' free. Humic acids were dissolved in 0.1% NaOH and ultrafiltered using collodion membrane. The filtrates were acidified with hydrochloric acid and humic acids were collected by centrifuging, transferred on the filter paper, washed with dilute hydrochloric acid and water successively, then air-dried and pulverized.     

Studies on the properties of organic matfer in buried humic horizon derived from volcanic ash

To investigate the relationship between the change of humus property and time factor, the humus composition in the buried humic horizons with the age from 28,000 years B.P. to the present was studied, according to the method presented by Kumada et al. (7).

The fH decreased with the elapse of time and in case of most of humus in the buried humic horizons with the age over 10,000 years, the fH became lower than 40 and were in the form of so-called ‘combined’ humus.

When 3,000-4,000 years have passed since the surface soil buried, the humic acid first moved . to ‘combined form.’ Second, after over 10,000 years, the fulvic acid moved to ‘combined form.’

The humification of ‘free’ humic acid proceeded with the elapse of time till around 5,000 years but of 'combined' humic acid till around 7,000 years. Both the humification-degree of ‘free’ humic acid after around 5,000 years and of ‘combined’ humic acid after around 7,000 years decreased. The humification-degree of ‘free’ and ‘combined’ humic acid from the samples with the age about 15,000 years B.P. to 28,000 years B.P. may be the same.