控释氮肥对水稻的增产效应及提高肥料利用率的研究

田间试验在日本山形县鹤冈市进行 ,探讨了树脂包膜类控释氮肥基施与尿素、硫铵分次施肥对单季稻的增产效应 ;应用15N示踪法研究了不同施肥处理水稻的吸氮模式及肥料利用率。结果表明 ,移栽稻以尿素与控释氮肥 (LPS-100)按 1∶1混合基施产量最高 ,分别比尿素和硫铵分次施肥增产23.6%和9.2% ;直播稻以LP-100基施产量最高 ,分别增产 9.2%和4.0% ;控释肥基施 ,水稻自移栽 (或直播 )至幼穗分化期吸氮量明显高于尿素或硫铵分次施肥。15N示踪研究表明 ,最高分蘖前水稻从尿素和硫铵基肥中吸收的氮素只占基肥氮总吸收量的 33%～ 45% ,水稻从基肥中吸收氮素可延续至抽穗期 ,而从LP-100中吸氮可持续至收获期。15N示踪法测得的氮素总回收率 ,以尿素处理最高 ,硫铵和LP-100接近 ;差减法测得的氮素总回收率以LP-100为最高 ,尿素 /LPS-100、尿素、硫铵三者接近 ;基肥的氮素回收率以LP-100硫铵 尿素。尿素 /LPS-100和LP-100一次基施 ,氮素生理效率和农学效率明显高于尿素和硫铵 ,是高产的主要原因     

对蜂蜜中主要抗褐变因子的探讨

选用ＡＧ５０Ｗ－Ｘ８阳离子交换树脂，并以批处理的方式，成功地将蜂蜜中的肽类物质与其它组合得到了分离。抗褐变实验结果清楚地表明，蜂蜜中的肽类成分完全没有抑制褐变的活性。这与以前的报道截然不同。     

钙处理桃果肉钙离子的分布及其与果实品质形成的关系

为探讨钙元素对桃果实品质、耐贮藏性的影响,确定最佳的叶面喷施钙元素的浓度,研究了喷施钙后,桃果肉组织中钙元素的分布特征、叶片叶绿素的含量以及对果实可溶性固形物含量(SSC)、大小、硬度和耐贮藏性的影响。结果表明,果肉中Ca2 的含量随着喷施钙元素浓度的提高而增加,当喷施CaCl2浓度为0.5%时叶绿素的含量最大,当喷施CaCl2浓度为1%时,SSC、果实大小和果肉硬度达到最大值;当喷施CaCl2浓度为2%时,放置3天后果实硬度最大。本研究确立了最佳的喷施浓度,为深入研究果实钙离子浓度梯度在果实品质形成方面的作用提供了依据。     

测定应力集中系数的灰色建模方法

通过对带轴肩的扭转圆轴、带双凹槽的拉伸板条、带偏心孔的纯弯曲梁等几种典型构件在应力集中处进行应变电测，利用灰色系统理论对测试数据进行累加生成处理、模型识别，建立了应变分布的灰色模型，用该模型求出了应力集中处的应力集中系数。结果表明：与目前常用的数据处理方法比较，灰色建模方法具有所需测试数据少、预测精度高等优点，非常适用于构件应力集中系数的实时测定。     

Soil compaction and forest floor removal reduced microbial biomass and enzyme activities in a boreal aspen forest soil

Soil enzymes are linked to microbial functions and nutrient cycling in forest ecosystems and are considered sensitive to soil disturbances. We investigated the effects of severe soil compaction and whole-tree harvesting plus forest floor removal (referred to as FFR below, compared with stem-only harvesting) on available N, microbial biomass C (MBC), microbial biomass N (MBN), and microbial biomass P (MBP), and dehydrogenase, protease, and phosphatase activities in the forest floor and 0–10 cm mineral soil in a boreal aspen (Populus tremuloides Michx.) forest soil near Dawson Creek, British Columbia, Canada. In the forest floor, no soil compaction effects were observed for any of the soil microbial or enzyme activity parameters measured. In the mineral soil, compaction reduced available N, MBP, and acid phosphatase by 53, 47, and 48%, respectively, when forest floor was intact, and protease and alkaline phosphatase activities by 28 and 27%, respectively, regardless of FFR. Forest floor removal reduced available P, MBC, MBN, and protease and alkaline phosphatase activities by 38, 46, 49, 25, and 45%, respectively, regardless of soil compaction, and available N, MBP, and acid phosphatase activity by 52, 50, and 39%, respectively, in the noncompacted soil. Neither soil compaction nor FFR affected dehydrogenase activities. Reductions in microbial biomass and protease and phosphatase activities after compaction and FFR likely led to the reduced N and P availabilities in the soil. Our results indicate that microbial biomass and enzyme activities were sensitive to soil compaction and FFR and that such disturbances had negative consequences for forest soil N and P cycling and fertility.     

低浓度镉对大白菜苗期生长及营养元素吸收积累的影响研究

在实验室用水培模拟轻度污染土壤,研究低浓度 Cd(5 1.μmol/L)对不同Cd耐性的4个大白菜品种苗期生长及营养元素吸收积累的影响.结果表明,低浓度Cd对耐性强的品种的生长有促进作用,对耐性差的品种的生长有抑制作用.5umol几Cd显著促进大白菜根系对S、Cu的吸收,分别增加22.0%～58.0%、45.9%～116.0%,但抑制S、Cu向地上部转运;大白菜地上部K、P、Ca、Mg、Mn、Zn含量受到Cd的较强抑制,且抑制程度存在品种差异.     

不同施氮量对水稻氮素吸收与分配的影响

运用15N示踪法研究了不同施氮量对两个品种水稻（4007和武运粳15）干物质积累量与其对15N吸收及分配的影响。结果表明,当施氮量超过N 150 kg/hm2时, 两个品种水稻子粒产量均不再显著增加。4007在4个施氮量下(N 100,150,200和 250 kg/hm2)分别比无氮区增产22.3%,36.9%,43.2%和38.1%;武运粳15分别增产10.6%,18.8%,27.1%和21.5%。同一施氮量下,4007子粒中15N累积量显著高于武运粳15,但茎叶和根中没有差异。增加施氮量降低了15N在水稻子粒中的分配比例,但提高了茎叶中15N的分配比例。15N在根中的分配比例不受施氮量和品种的影响。研究结果还表明,同一施氮量下,4007对肥料氮的总体利用率要比武运粳15高3～6个百分点。     

灌溉策略及氮肥施用对设施番茄产量及氮素利用的影响

以传统水肥管理为对照,根据根层氮素实时监控技术与氮素供应目标值指标,对秋冬季设施番茄生育期进行氮肥追施优化管理,同时结合小管出流的方式比较研究采用每次灌溉至田间持水量及固定灌额两种策略对设施番茄产量及氮素追施调控的影响。结果表明,传统灌溉方式下,优化氮素处理保证了番茄产量,与传统氮肥处理相比,追施的氮肥数量减少了48%;在番茄的主要生育时期内,采用每次灌溉至田间持水量及固定灌额处理的灌溉量分别比传统灌溉处理减少46%和30%;采用同样指标所推荐的氮肥追施数量也分别减少14%和10%,明显减少土壤–蔬菜体系中氮素的表观损失,减轻了由于过量施氮而对环境造成的影响。     

Nitrogen fertilizer–induced mineralization of soil organic C and N in six contrasting soils of Bangladesh

A 90‐day laboratory incubation study was carried out using six contrasting subtropical soils (calcareous, peat, saline, noncalcareous, terrace, and acid sulfate) from Bangladesh. A control treatment without nitrogen (N) application was compared with treatments where urea, ammonium sulfate (AS), and ammonium nitrate (AN) were applied at a rate of 100 mg N (kg soil)^–1. To study the effect of N fertilizers on soil carbon (C) turnover, the CO₂‐C flux was determined at nine sampling dates during the incubation, and the total loss of soil carbon (TC) was calculated. Nitrogen turnover was characterized by measuring net nitrogen mineralization (NNM) and net nitrification (NN). Simple and stepwise multiple regressions were calculated between CO₂‐C flux, TC, NNM, and NN on the one hand and selected soil properties (organic C, total N, C : N ratio, CEC, pH, clay and sand content) on the other hand. In general, CO₂‐C fluxes were clearly higher during the first 2 weeks of the incubation compared to the later phases. Soils with high pH and/or indigenous C displayed the highest CO₂‐C flux. However, soils having low C levels (i.e., calcareous and terrace soils) displayed a large relative TC loss (up to 22.3%) and the added N–induced TC loss from these soils reached a maximum of 10.6%. Loss of TC differed depending on the N treatments (urea > AS > AN >> control). Significantly higher NNM was found in the acidic soils (terrace and acid sulfate). On average, NNM after urea application was higher than for AS and AN (80.3 vs. 71.9 and 70.9 N (kg soil)^–1, respectively). However, specific interactions between N‐fertilizer form and soil type have to be taken into consideration. High pH soils displayed larger NN (75.9–98.1 mg N (kg soil)^–1) than low pH soils. Averaged over the six soils, NN after application of urea and AS (83.3 and 82.2 mg N (kg soil)^–1, respectively) was significantly higher than after application of AN (60.6 mg N (kg soil)^–1). Significant relationships were found between total CO₂ flux and certain soil properties (organic C, total N, CEC, clay and sand content). The most important soil property for NNM as well as NN was soil pH, showing a correlation coefficient of –0.33** and 0.45***, respectively. The results indicate that application of urea to acidic soils and AS to high‐pH soils could be an effective measure to improve the availability of added N for crop uptake.     

Differential and successive effects of residue quality and soil mineral N on water-stable aggregation during crop residue decomposition

Residue quality has been shown to influence soil water-stable aggregation (WSA) during crop residue decomposition, but there is still little information about its interactive effect with soil mineral N availability. The aim of this study was to determine the effect of soil mineral N on WSA during the decomposition of two high-C/N crop residues (wheat straw with C/N = 125.6 and miscanthus straw with C/N = 311.3). The two crop residues were combined with three mineral N addition rates (0, 60, and 120 mg N kg⁻¹ dry soil). Respiration, soil mineral N content, and WSA (expressed as mean-weight diameter, MWD) were measured on several dates during a 56-d incubation. The effect of decomposing crop residues on WSA followed two phases. (i) Between 0 and 7 d, the increase in WSA was related to intrinsic residue quality with higher decomposability of the wheat straw resulting in higher WSA. (ii) Thereafter, and until the end of the experiment, mineral N addition rates had a predominant but negative influence on WSA. In this second phase, the average MWD of residue-treated soils was 0.92, 0.55, and 0.44 mm for the 0, 60 and 120 mg N kg⁻¹ dry soil addition rates, respectively. Mineral N addition which did result in higher crop residue decomposition did not lead to higher WSA. WSA during crop residue decomposition is therefore not simply positively related to the induced microbial activity, and changes in microbial community composition with differential effects on WSA must be involved. The impact of high-C/N crop residues inputs on WSA, initially assumed to be low, could actually be strong and long-lasting in situations with low soil mineral N content.