992 resultados para 345.05


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土壤呼吸是森林生态系统碳循环的重要组成部分,对土壤呼吸的主要组分根系呼吸和土壤微生物呼吸进行分离并量化,对于了解土壤碳释放规律、估算生态系统土壤碳的年际通量以及预测气候变化条件下根系或土壤微生物对土壤碳释放格局的影响具有重要意义。本文采用挖壕法测定辽东山区蒙古栎林、杂木林和胡桃楸林的土壤表面CO2通量,并同步分析土壤水热因子及土壤有机质、N含量、根系生物量、土壤酶活性、土壤微生物生物量等。研究结果表明:(1)辽东山区次生林0-10cm土壤有机质含量为9.29-18.15%,全氮含量为0.43-0.90%,pH值为5.67-6.19;次生林生长季细根生物量平均为152.61- 447.79 g/m2,粗根生物量平均为255.42-507.42 g/m2,根系总量平均为540.93-955.22 g/m2;土壤酶活性季节变化明显,且具垂直分布特征,蒙古栎林的土壤转化酶、淀粉酶和脱氢酶活性最高,胡桃楸林最低,胡桃楸林过氧化氢酶活性相对最大;土壤微生物量碳、氮的季节变化呈明显的单峰曲线并与土壤温度相关,土壤微生物量碳氮之间具显著相关性(P<0.05)。(2)次生林土壤总呼吸、根呼吸和土壤微生物呼吸具明显的日、季变化规律,生长季根呼吸贡献相对较低,胡桃楸林根呼吸贡献率为34.0-34.8%,蒙古栎林为17.9-28.4%,杂木林为14.7-35.3%;土壤微生物呼吸贡献率为66.0-85.3%,高于根呼吸贡献率,说明辽东山区次生林土壤微生物呼吸决定土壤总呼吸的变化趋势。(3)土壤呼吸与地下5cm土壤温度呈指数函数关系,土壤总呼吸的Q10值为1.29-2.30,微生物呼吸的Q10值为1.28-2.09,根呼吸的Q10值为1.29-3.72;土壤总呼吸、微生物呼吸、根呼吸与土壤含水量均无明显相关关系;蒙古栎林根呼吸与细根生物量显著相关,杂木林根呼吸与粗根生物量及根系总生物量显著相关,胡桃楸林根呼吸与根系生物量总量显著相关(P<0.05);微生物呼吸与淀粉酶、转化酶、脱氢酶、过氧化氢酶均无显著相关性(除胡桃楸林与过氧化氢酶显著相关);微生物呼吸与土壤微生物量碳、氮均呈显著线性相关关系(P<0.05)。(4)蒙古栎林土壤总呼吸、根呼吸、土壤微生物呼吸年际碳释放量分别为572.78、147.78和425.59 g C m-2a-1,杂木林分别为403.12、108.92、297.51 g C m-2a-1,胡桃楸林分别为519.47、173.75、345.72 g C m-2a-1;生长季和非生长季通过根呼吸释放的碳量均小于分解土壤有机质的微生物呼吸释放的碳量,非生长季次生林土壤碳释放量为39.21-152.04 g C m-2a-1,占全年呼吸总量的10-29%,说明冬季土壤碳释放量不能忽略。

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For (Ti1-xVx)(2)Ni (x = 0.05,0.1,0.15,0.2 and 0.3) ribbons, synthesized by arc-melting and subsequent melt-spinning techniques, an icosahedral quasicrystalline phase was present, either in the amorphous matrix or together with the stable Ti2Ni-type phase. With increasing x values, the maximum discharge capacity of the alloy electrodes increased until reached 271.3 mAh/g when x = 0.3. The cycling capacity retention rates for these electrodes were approximately 80% after a preliminary test of 30 consecutive cycles of charging and discharging.

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The electrical, magnetic and transport properties of Zn doped polycrystalline samples of Sr2Fe1-xZnxMoO6 ( x = 0, 0.05, 0.15 and 0.25) with the double perovskite structure have been investigated. The subtle replacement of Fe3+ ions by Zn2+ ions facilitates the formation of a more ordered structure, while further substitution leads to disordered structure because of the presence of a striped phase. Analysis of the x-ray powder diffraction patterns based on Rietveld analysis indicates that the replacement of Fe3+ by Zn2+ ions favours the formation of Mo6+ ions. The spin-glass behaviour can be explained on the basis of the competition between the antiferromagnetic superexchange and the ferromagnetic double-exchange interaction. The low-field magnetoresistance was moderately enhanced at x = 0.05, and its origin was found to be the competition between the decrease of the concentration of the itinerant electrons and the weaker antiferromagnetic superexchange in the antiphase boundaries. An almost linear negative magnetoresistance in moderate field has been observed for x = 0.25. A possible double-exchange mechanism is proposed for elucidating the observations; it also suggests a coexistence of (Fe3+, Mo5+) and (Zn2+, Mo6+) valence pairs.

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利用高温固相法合成了 Y1.95-xGdxSiO5:Eu0.05(x=0.6mol%)荧光体。结构测定表明所合成的荧光体为单斜晶系的X2型Y2SiO5相,空间群为B2/b。真空紫外光谱表明:随着Gd3+含量的增加,在192um附近,出现了Gd+的激发峰,且此峰的强度随着Gd3+含量的增加而增大;同时位于150~185nm之间的基质吸收带的强度也增大;而位于200~300nm之间的Eu的电行迁移带的强度却随着Gd3+含量的增加而降低。

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本文研究了“Bi(BiF_3~-)/La_(0.95)Pb_(0.05)F_(2.95)/Pt”元件的气敏性质。元件的电动势与氧分压对数呈线性关系,温度升高,响应时间变短。20℃,在所测的范围内,电动势与空气中氢分压呈对数关系:E=E_0-961gPH_2(mV);敏感电极反应归结为局域电流或称作混合电势机理。元件对空气中1000Pa 氢气的90%响应时间仅用15S。元件对 CO 也有一定的敏感性能,但对甲烷、丁烷、乙炔等不具敏感性能。

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本文研究了Ce_(0.95)Ca_(0.05)F_(3-x)固体电解质及其氧传感器的制备和性质。在150℃时,Po_2在10~(-2)~10~(-1)MPa范围内传感器件的电位变化正比于Po_2的对数值。同时研究了不同参比电极和敏感电极对传感性能的影响。以Bi+BiF_3为参比电极时,EMF值稳定较快;当Pd作为敏感电极时,传感元件的响应较快;以RuO_2作敏感电极时,传感器件较灵敏。文章还讨论了敏感机理。

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Sea water samples were collected in the East China Sea in March and April, 2005, and three-dimensional fluorescence of dissolved organic matter was measured by fluorescence excitation-emission matrix spectroscopy. The position, number and intensity of fluorescence peak in the spectra and the relations of the peaks were analyzed to determine the type, distribution and origin of the fluorescence dissolved organic matter. Seven types of fluorescence peaks were detected from the samples. There are protein-like fluorescence peaks B with Ex(max)/Em(max) = 275/300 nm, D with Ex(max)/Em(max) = 225/295-305 nm, T with Ex(max)/Em(max) = 280/345 nm, and S with Ex(max)/Em(max) = 225-240/320-350 nm, two humic-like peaks A with Ex(max)/Em(max) = 250-255/410-455 nm and C 335-345/410-440 ran, and marine humic peak M with Ex(max)/Em(max) = 305 nm/400-420 nm. Peaks B, S and A appeared in all surveyed area. Peaks T and D appeared in the north of the surveyed area. Peaks M and C only appeared in a few stations. In the surface layer, the source of the fluorescence dissolved organic matter might be the fresh water outflow of the Yangtze River, while the fluorescence dissolved organic matter in the middle layer had double sources from the Yangtze River and the phytoplankton. The good correlationships of different fluorescence peaks showed the same source or some relationship between the protein-like and the humic-like fluorescence dissolved organic matter.

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A study was conducted on grass mixtures that included smooth bromegrass (SB) + drooping wild ryegrass (DW), smooth bromegrass + Siberian wild ryegrass (SW) + crested wheatgrass (CW) and smooth bromegrass + Siberian wild ryegrass + drooping wild ryegrass + crested wheatgrass in the alpine region of Qinghai-Tibetan Plateau. The study was conducted from 1998 to 2000 to investigate the effects of N application rates and growing year on herbage dry matter (DM) yield and nutritive values. Herbage DM production increased linearly with N application rates. The effect of N application on DM yields was greater (P < 0.05) in the 2nd and 3rd production years than in the establishment year. Dry matter yields of SB + SW + CW and SB + SW + DW + CW can reach as high as 15 000 kg ha(-1) at 345 kg ha(-1) N rate in the 3rd growing year. With increased N application rates, crude protein (CP) contents and 48 h in sacco DM degradability of grasses increased (P < 0.05). No effect (P > 0.05) of N application was detected on organic matter (OM) and acid detergent fibre (ADF) concentration. It can be concluded that for increased biomass production in the alpine region of the Qinghai-Tibetan Plateau, a minimum of 345 kg N ha(-1) should be applied to grass stands in three split application of 115 kg N ha(-1), in early June, early July and late July

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A system for visual recognition is described, with implications for the general problem of representation of knowledge to assist control. The immediate objective is a computer system that will recognize objects in a visual scene, specifically hammers. The computer receives an array of light intensities from a device like a television camera. It is to locate and identify the hammer if one is present. The computer must produce from the numerical "sensory data" a symbolic description that constitutes its perception of the scene. Of primary concern is the control of the recognition process. Control decisions should be guided by the partial results obtained on the scene. If a hammer handle is observed this should suggest that the handle is part of a hammer and advise where to look for the hammer head. The particular knowledge that a handle has been found combines with general knowledge about hammers to influence the recognition process. This use of knowledge to direct control is denoted here by the term "active knowledge". A descriptive formalism is presented for visual knowledge which identifies the relationships relevant to the active use of the knowledge. A control structure is provided which can apply knowledge organized in this fashion actively to the processing of a given scene.

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Second letter to nephew, Daniel Avery Whedon from Daniel D. Whedon dated May 16, 1881.

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Letter from Daniel D. Whedon to nephew. One of two dated May 16, 1881.

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Handwritten letter from T. Merritt to Rev. Epaphras "Kible[sic]" regarding the latter's desire for Merritt to take on his preaching circuit citing ailing health. Dated May 12, 1801.