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71.
从生物质原料的工业分析结果和木质素含量两个角度出发,分析了二者对生物质炭化的影响.对生物质炭化原料进行选择,认为木材类生物质适合作为生物质炭化的原料,可加强对树木枝条、锯末及薪炭林的炭化;为实现生物质炭化的工业化,还应设计利用烟气余热等热源来热解生物质的换热器,这项设计需知道生物质热解需热量.运用热重-差示扫描(TG-DSC)同步热分析仪对选用的木屑进行热解实验并利用DSC曲线对木屑炭化需热量进行分析.结果表明,木屑炭化终温为500℃时(初始温度为40℃),需热量为491kJ/kg.提出DSC曲线在工业用热解换热器传热设计和校核中的应用方法. 相似文献
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本文从产品用途、生产现状及现行技术存在的问题、市场消费概况等方面,对环氧丙烷产品进行了全面阐述,为从事该产品的生产或后续加工者提供较详细的资料。 相似文献
74.
Enhancing the carbon sink in European agricultural soils: including trace gas fluxes in estimates of carbon mitigation potential 总被引:7,自引:0,他引:7
Pete Smith Keith W. Goulding Keith A. Smith David S. Powlson Jo U. Smith Pete Falloon Kevin Coleman 《Nutrient Cycling in Agroecosystems》2001,60(1-3):237-252
The possibility that the carbon sink in agricultural soils can be enhanced has taken on great political significance since
the Kyoto Protocol was finalised in December 1997. The Kyoto Protocol allows carbon emissions to be offset by demonstrable
removal of carbon from the atmosphere. Thus, forestry activities (Article 3.3) and changes in the use of agricultural soils
(Article 3.4) that are shown to reduce atmospheric CO2levels may be included in the Kyoto emission reduction targets. The European Union is committed to a reduction in CO2 emissions to 92% of baseline (1990) levels during the first commitment period (2008–2012). We have shown recently that there
are a number of agricultural land-management changes that show some potential to increase the carbon sink in agricultural
soils and others that allow alternative forms of carbon mitigation (i.e. through fossil fuel substitution), but the options
differ greatly in their potential for carbon mitigation. The changes examined were, (a) switching all animal manure use to
arable land, (b) applying all sewage sludge to arable land, (c) incorporating all surplus cereal straw, (d) conversion to
no-till agriculture, (e) use of surplus arable land to de-intensify 1/3 of current intensive crop production (through use
of 1/3 grass/arable rotations), (f) use of surplus arable land to allow natural woodland regeneration, and (g) use of surplus
arable land for bioenergy crop production. In this paper, we attempt for the first time to assess other (non-CO2) effects of these land-management changes on (a) the emission of the other important agricultural greenhouse gases, methane
and nitrous oxide, and (b) other aspects of the ecology of the agroecosystems. We find that the relative importance of trace
gas fluxes varies enormously among the scenarios. In some such as the sewage sludge, woodland regeneration and bioenergy production
scenarios, the inclusion of trace gases makes only a small (<10%) difference to the CO2-C mitigation potential. In other cases, for example the no-till, animal manure and agricultural de-intensification scenarios,
trace gases have a large impact, sometimes halving or more than doubling the CO2-C mitigation potential. The scenarios showing the greatest increase when including trace gases are those in which manure
management changes significantly. In the one scenario (no-till) where the carbon mitigation potential was reduced greatly,
a small increase in methane oxidation was outweighed by a sharp increase in N2O emissions. When these land-management options are combined to examine the whole agricultural land area of Europe, most of
the changes in mitigation potential are small, but depending upon assumptions for the animal manure scenario, the total mitigation
potential either increases by about 20% or decreases by about 10%, shifting the mitigation potential of the scenario from
just above the EU's 8% Kyoto emission reduction target (98.9 Tg C y−1) to just below it. Our results suggest that (a) trace gas fluxes may change the mitigation potential of a land management
option significantly and should always be considered alongside CO2-C mitigation potentials and (b) agricultural management options show considerable potential for carbon mitigation even after
accounting for trace gas fluxes.
This revised version was published online in August 2006 with corrections to the Cover Date. 相似文献
75.
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从空调箔成型过程及质量要求出发,通过对DC--热轧及连续轧两种工艺生产的空调箔进行对比,认定DC--热轧工艺较优,并对其工艺进行优化。 相似文献
77.
珠江上游南北盘江喀斯特地区土地石漠化的成因及生态恢复模式 总被引:3,自引:0,他引:3
分析了珠江上游南北盘江喀斯特地区土地石漠化的形成机理:一是广布的碳酸盐岩成土物质含量低,母岩与土壤之间粘着力差,成土速度慢;二是地表与地下双层水文地质结构,水土分离,干旱缺水严重;三是植物生境严酷,生长缓慢,覆盖率低;四是超载的人口压力引发的滥采滥伐、陡坡开荒,导致严重的水土流失,是该地区土地石漠化最关键的因素。同时探究了珠江上游南北盘江喀斯特地区主要的生态恢复模式:一是以小流域为单元,山、水、田、林、路综合治理的模式提高生态容量;二是以农村能源建设为主线促进生态修复的模式提高生态休养时间;三是以培育替代产业促进农业人口转移的模式减少生态负荷;四是以有序、规范的资源开发模式减少生态干扰。 相似文献
78.
79.
文中分析了吕梁西部五大流域水利工程现状及存在问题。论述了其滩地、水地开发目标及建设内容,并进行了可行性分析。 相似文献
80.
Assessment of Sediment and Pollutants in Buyo Lake,Ivory Coast,Using SWAT (Soil and Water Assessment Tool) Model 总被引:2,自引:0,他引:2
Tanoh Jean-Jacques Koua Jean Patrice Jourda Kan Jean Kouame Kouao Armand Anoh 《化学与化工:英文版》2013,(11):1054-1059
The changes in land use in the last 30 years in the territory of agro-forest watershed of Lake Buyo resulted in significant sediment into the lake. Sediments are a preferred means of transportation for certain pollutants, like phosphorus in excess. By mapping the source areas of erosion, the authors can determine the risk areas and help to prioritize interventions in the territory. This mapping is done using the SWAT (soil and water assessment tool) model. Several types of data, including topography, land use, soil and climate data are needed to run the model. In this paper, all different steps are presented, from the designing of HRU (hydrological response units), basic units to run the SWAT model until the simulations. The establishment of HRU has three main stages: space discretization, land use and soil data integration and HRU distribution: (1) space discretization which consist in extracting the limits and the water network of the watershed from the DEM (digital elevation model) and in subdividing them into sub-basins; (2) land use and soil data integration: it consists in digitizing the physical maps of land use and of soils under Mapinfo 7.5 and in keeping them in "shape" format; (3) HRU distribution: it leads to subdivide the sub-watersheds in small units that combine a single soil type and one type of land use. It appears from this study to obtain 23 sub-watersheds and 71 HRU. Once the HRU designed, it is necessary to integrate climate data, data on physico-chemical characteristics of soils and agricultural practices, before starting the simulations. This will allow the model to assess the risk of sedimentation and eutrophication of the lake using the MUSLE (modified universal soil loss equation) and phosphorus cycle. 相似文献