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在黔中地区 ,用不同浓度的稀土液对沙梨进行叶面喷施 ,分别对生长量、粒重、单株产量 ,每 1/15公顷产量进行试验研究。试验结果表明 :施用稀土对梨树的生长及产量有较高影响 ,不同浓度 ,效果不一 相似文献
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1991年以来,承担“冀北山地应用稀土提高林果产量试验与推广”课题,试验结果表明,于苹果、山楂等主产果树,落叶松、油松、杨树等主要造林苗木,喷施稀土能显著提高果树产量、果品质量和苗木生长量。并筛选出最佳浓度和施用时间。 相似文献
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以油茶为试验材料,研究了稀土微肥对植物体叶绿素含量、可溶性蛋白质含量、核糖核酸酶的活性、光合速率、植株生长和产量的影响。结果表明,施用适量稀土微肥可以促进油茶春梢生长和叶面积增加,提高2年生叶片叶绿素、可溶性蛋白质含量,抑制核糖核酸酶的活性,增强光合速率,延缓3年生叶片的衰老,从而提高油茶的坐果率和单株产量。 相似文献
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赤霉素(GA3)、吲哚丁酸(IBA)和稀土对锥栗产量促进作用的研究 总被引:2,自引:2,他引:2
运用双因素随机区组设计方案,研究了稀土、赤霉素(GA3)和吲哚丁酸(IBA)三种植物生长调节剂对三信锥栗品种无性系产量增加的影响。结果表明:稀土微肥不员浓度喷施对产量有显著的影响,以400ppm(A1)为最佳;两种生长调节剂中,则以GA3的效果更好(B1);AB因素两种组合的混合喷施对产量的促进有交互作用,各种组合中以A1B1,即稀土浓度为400ppm,GA3浓度为50ppm的交互效应对产量的提高最显著。 相似文献
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1987~1989年在枣强县孟在村对马莲小枣在花期、果实膨大期喷施600ppm、800ppm、1000ppm浓度的稀土试验。试验结果表明,能提高马莲小枣座果率,产量及品质以喷施800ppm浓度的稀土表现最佳。 相似文献
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马尾松苗期施用稀土,不仅可以提高苗木质量,苗高增加21.5%,地径粗增加10.8%,提高Ⅰ、Ⅱ级苗5%的产量,而且具有成本低,使用方法简单,安全容易推广等优点。 相似文献
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采用随机区组田间试验进行叶面喷施。通过对100ppm、300ppm、400ppm、500ppm、700ppm和一个清水对照进行处理和分析,最后得出300ppm可以提高百粒重、座果率、单株产量。 相似文献
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【目的】测定我国北方某轻稀土尾矿库区的土壤轻稀土元素含量及植物中镧、铈元素含量和分布,分析植物对轻稀土元素镧、铈的转移系数和吸收系数,筛选镧、铈富集植物,以期发现轻稀土富集植物,为尾矿库景观生态恢复提供理论依据。【方法】以稀土尾矿库区尾矿坑的边缘绿地为研究样地,依据风向将采样点设置在东南、西北、东北和西南4个方向,从矿坑边缘由近及远依次设置在50,100和300m边坡处,共计12个采样点。利用五点采集-四分法收集0~20cm表层土壤样品,在采样点采集修复工程栽植的6种植物(梭梭、小叶锦鸡儿、花棒、胡枝子、白刺和毛白杨)地上器官和根部样品。采用ICP法测定土壤中轻稀土元素镧La、铈Ce、镨Pr、钕Nd、钐Sm、钷Pm和铕Eu含量及植物中镧和铈含量。采用N.L.Nemerow综合指数法分析轻稀土尾矿库周边土壤单因子污染指数平均值,采用生物转移系数评价植物转移效率,采用生物吸收系数评价植物吸收土壤中镧和铈的能力。【结果】轻稀土尾矿库土壤中La,Ce,Pr,Nd,Sm,Pm和Eu的平均含量分别为2762.46,5440.42,1308.42,1604.11,133.96,28.12和40.53mg·kg-1,镧、铈含量之和占测试样品轻稀土总量的72%;各方位表层土壤中轻稀土含量表现为东南>东北>西南>西北,且高于内蒙古土壤含量几何平均值(背景值)25.10~230.56倍,且各方向土壤的单因子污染指数均大于3,确定研究区土壤属重度污染;东南单因子污染指数平均值为69.06~544.10,污染值最高,西北单因子污染指数平均值为5.99~19.75,污染值最低,东北和西南单因子污染指数平均值相似;梭梭、胡枝子和白刺体内La和Ce含量均表现为地上器官>根,小叶锦鸡儿、花棒和毛白杨体内La和Ce含量均表现为根>地上器官;梭梭、胡枝子和白刺的镧、铈转移系数为1.03~1.76,胡枝子的镧、铈吸收系数为1.00~1.72,只有胡枝子的镧、铈转移系数和吸收系数均大于1。【结论】胡枝子是轻稀土元素镧、铈的富集植物,可用于轻稀土污染土壤修复,其他5种植物可作为轻稀土元素的耐受性植物应用。 相似文献
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《Forest Ecology and Management》1997,93(3):235-243
We observed seed rain and seedling emergence of a pioneer tree species, Betula maximowicziana Regel., for 5 years at various sites differing in canopy and soil surface conditions, and clarified that a buried seed bank contributed to the recruitment of B. maximowicziana seedlings. More seedlings emerged at sites where the soil surface had been disturbed than at sites where the soil surface had not been disturbed. Within each soil surface condition, the densities of the emerged seedlings were generally proportional to the densities of the seeds dispersed the previous year. However, the seedling densities were disproportionately higher than the dispersed seed densities at the sites where the soil surface had been disturbed in the previous year. Soil samples taken during different seasons indicated that B. maximowicziana maintained a persistent seed bank in the soil below 1 cm deep, while it formed a more transient seed bank in the top 1 cm of the soil. The seed rain in the previous year was the primary contributor to the establishment of B. maximowicziana seedlings in a year after a mast seed year. On the other hand, the soil seed bank had a compensational role in a year after a poor seed year. Canopy cover did not affect seedling emergence. Therefore, the previously reported lack of a persistent seedling bank of B. maximowicziana under a canopy will be partially attributed to a relatively rare soil surface disturbance in a stable stand. 相似文献
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Planted forests have more than a millennium of history and represent the world's best hope for meeting global wood requirements in the twenty-first century. Advances in genetic improvement, nursery practices, stand establishment, and tending, harvesting, and manufacturing have boosted plantation yields to a higher level than at any point in history. Despite this, forest managers face a mounting challenge to demonstrate that plantation productivity is sustainable. Tackling this challenge requires a sound understanding of the principles of forest productivity, how they apply to a developing plantation, and how they are influenced by management. In this paper criticisms of plantation forestry are discussed from the basis of world experience, and examples of productivity decline are described. Obvious declines are rare, and can be attributed to poor soil management. However, ambiguities exist and controversy will continue until sustainable productivity can be demonstrated conclusively. Proposed programs aim to provide the technical base needed for sound soil management and sustainable plantation productivity. 相似文献
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Christopher Neill William A. Patterson III David W. Crary Jr. 《Forest Ecology and Management》2007,250(3):234-243
Fire is an important component of the historic disturbance regime of oak and pine forests that occupy sandy soils of the coastal outwash plain of the northeastern US. Today prescribed fire is used for fuel reduction and for restoration and maintenance of habitat for rare plant and animal, animal species. We evaluated the effects of the frequency and seasonality of prescribed burning on the soils of a Cape Cod, Massachusetts's coastal oak-pine forest. We compared soil bulk density, pH and acidity, total extractable cations and total soil carbon (C) and nitrogen (N) in unburned plots and in plots burned over a 12-year period, along a gradient of frequency (every 1–4 years), in either spring (March/April) or summer (July/August). Summer burning decreased soil organic horizon thickness more than spring burning, but only summer burning every 1–2 years reduced organic horizons compared with controls. Burning increased soil bulk density of the organic horizon only in the annual summer burns and did not affect bulk density of mineral soil. Burn frequency had no effect on pH in organic soil, but burning every year in summer increased pH of organic soil from 4.01 to 4.95 and of mineral soil from 4.20 to 4.79. Burning had no significant effect on organic or mineral soil percent C, percent N, C:N, soil exchangeable Ca2+, Mg2+, K+ or total soil C or N. Overall effects of burning on soil chemistry were minor. Our results suggest that annual summer burns may be required to reduce soil organic matter thickness to produce conditions that would regularly allow seed germination for oak and for grassland species that are conservation targets. Managers may have to look to other measures, such as combinations of fire with mechanical treatments (e.g., soil scarification) to further promote grasses and forbs in forests where establishment of these plants is a high priority. 相似文献