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外文文献 英文CaCO3吸收二氧化碳

外文文献 英文CaCO3吸收二氧化碳
外文文献 英文CaCO3吸收二氧化碳

Energy

Procedia

GHGT-10

Development of post-combustion CO2 capture with CaO/CaCO3 looping

in a bench scale plant

Chin-Ming Huang, Heng-Wen Hsu, Wan-Hsia Liu, Jui-Yen Cheng, Wei-Cheng

Chen, Tzeng-Wen Wen, Wang Chen

Industrial Technology Research Institute, H s i nc h u310, T ai wa n, R.O.C

Elsevier use only: Received date here; revised date here; accepted date here

Abstract

Several systems for CO2capture using CaO as regenerable sorbent are under development at Industrial Technology Research Institute (ITRI). CaO/CaCO3 looping of carbon dioxide capture system can also be used for both pre-combustion and post-combustion carbon dioxide capture. At present, ITRI has established a post-combustion 1

kW CaO/CaCO3looping of carbon dioxide capture system device in Taiwan. The carbonator is for the bubbling fluidized bed and the calciner is for the moving bed. The device made up 0.1 kg/hour of new CaO which has been under 57 hours of continuous operation. Capture efficiencies above 99% have been obtained under realistic flue gas conditions in the carbonator reactor.

In the future, power generation, petrochemical industry and steel and iron industries

are the first to be considered for reduction of CO2 emissions. Our goal is to establish a 1 MW (5 thousand tons of CO2 every year)pilot plant in 2011, 10 to 30 MW(50 to 150 thousand tons CO2 every year)demonstration plant in 2020 and a commercial plant

in 2027 for post-combustion capture. In addition, ITRI has to research and develop the

CO2capture technologies from flue gases including Gasification or Integrated Gasification Combined Cycle (IGCC), CaO/CaCO3 looping and innovative meso-porous nanomaterials for CO2 adsorption.

? 2010 Elsevier Ltd. All rights reserved

c?2011Published by Elsevier Ltd.

Keywords: CO2 Capture; CaO /CaCO3 looping; Carbonator; Calciner; Pilot testing

doi:10.1016/j.egypro.2011.01.183

C.-M.Huang et al./Energy Procedia4(2011)1268–12751269

1.Introduction

Carbon dioxide the comes from combust ion of fossil fuel is the major contributor of the greenhouse effect. The control and decrease of anthropogenic CO2emissions from fossil fueled power plants abatement play important roles for at mospheric CO2concentration reduct ion. Generally, there are several options for atmospheric carbon dioxide concentration controlling, such as the subst itution of nuclear power for fossil fuels, power efficiency improvement of the fossil plants and the CO2capture prior to its emission. The emission controlling technology of carbon dioxide by using the sorption/desorption concept with the sorbent is a widely applied met hod for the Fluidized Bed Combustor (FBC) flue gas process. From the energy point of view, therefore, the separat ion of carbon dioxide from the emiss ion source, such as coal-fired power plants, has been considered as an effect ive mit igation option for climate change.(1,2,3)

Solid sorbents for CO2separat ion include sodium and potassium oxides, zeolites, carbonates, amine-enriched sorbent, and etc. One of them, the calcium sorbents (CaO) is used widely in fluidized bed combust ion for emiss ion control of sulfur contaminants due to its low cost. In addit ion, it has been well known that the fresh calcined lime can be carbonated rapidly by carbon dioxide at suitable temperature. Thus, the calcium-based sorbents has been suggested to be an attractive material for carbon dioxide removes due to its low cost, high adsorpt ion capacity and high reversibilit y of CO2.The mechanism of CO2capture/release of calciu m sorbent can be divided into two step, carbonat ion and calcination:

CaO+CO2àCaCO3 (1)

CaCO3àCaO+CO2 (2) The calcinat ion of CaCO3is an endothermic, mean t he forward react ion is higher temperature favorable.(4,5)

CO2separat ion from flue gas by CaO-based sorbents in fluidized bed combust ion (FBC) system is an intensively invest igated technology for the reduct ion of CO2emission.The t ypical scheme of the CO2remove process could be depicted as Figure 1.

Flue gas

CO

2 Figure 1 The scheme o f CO2separat ion loop by CaO-based sorbent s.

1270 C.-M.Huang et al./Energy Procedia4(2011)1268–1275

According to the ment ioned above, the carbonat ion process of calcium sorbents (CaO) with CO2is t he basis reaction for the capture technology in this high temperature CaO/CaCO3cycle system. In fact, all CaO sorbents used in this loop come from the calcinat ion process of CaCO3, at around 800~900o C. In the carbonator, the high porous CaO sorbents were treated wit h a diluted CO2 stream and further formed CaCO3at a temperature of over 600o C. Act ive sorbents were regenerated by a calcinat ion reaction at higher temperature between 850~900o C, and the CO2component were separated from the loop. After being reduced in separate (cracker) vessel, the CaCO3transfers to CaO and further returns to the carbonat ion vessel for CO2 capture.

The object ive of this research is to develop high performance sorbents for CO2uptake at high temperatures. Due to the finit e t ime of exposure and low utilizat ion of the limestone, increasing the calcium ut ilizat ion efficiency would be attractive of lowering the cost of raw materials. In this work, CaO sorbents wit h porous structure and high capacit y of CO2 was developed for carbon dioxide capture. The micrographs, surface area, pore structural, act ivit y, cycle life, and characterist ic properties of CaO sorbents were also analyzed. In addit ion, an at mospheric small pilot CaO carbonat ion/ calcinat ion system was also established for practical applicat ion of carbon dioxide separat ion.

2.Experimental

Experiments have been conducted in a 1 kW test facility built at ITRI, made up of one bubbling fluidized bed carbonator and one moving bed calciner as shown in Figure 2. The bubbling fluidized bed is 2.5 m high wit h a 0.1 m internal diameter. The moving bed is 0.9 m long wit h a 0.05 m internal diameter. Solids from the bubbling fluidized bed to moving bed have completed half of the solid circulation loop. Solids are transferred from the carbonator to the calciner by a pipe. The pipe is 0.5 m long with 1 inch internal diameter. A mixture of gas containing CO2 (air from a blower and CO2 from a cylinder) is fed into the carbonator. Note that the fluidized gas in carbonator is mixing by 85% air and 15% CO2 in the percentage of volume. The air distributor is located at the gas entrance in the carbonator. Particles size of CaCO3are distributed between 250-500μm. Silicon carbide heating rods cover surround the carbonator and the calciner, which can maintain the moving bed at the temperature 800~900and the bubbling

℃3 calcination/carbonation studies fluidized bed at the temperature 600~700. The CaCO

in these works which have two steps. One is continuous-mode operation and it makes up 0.1 kg fresh CaCO3per hour. In this mode which needs toe maintain the bubbling fluidized bed at the temperature of 600~700and the moving bed at the temperature

℃ The bubbling fluidized bed at the bottom of ΔP between 100 ~ 150 cm-H2O, 800~900.

that gas velocities are varied between 0.2-0.4 m/s. The other is batch-mode operation without making up fresh CaCO3. In this mode which need to maintain the bubbling fluidized bed at the temperature of 600~700 and the moving bed at the temperature

℃of

C.-M.Huang et al./Energy Procedia4(2011)1268–12751271

℃ The bubbling fluidized bed at the bottom of ΔP between 100 ~ 150 cm-H2O, 600~700.

that gas velocities are varied between 0.2-0.4 m/s. The agitated gas in the calcination vessel is nitrogen gas. In the same place prepare for a hole when we use steam to calcination.

Prior to starting the operation, industrial grade limestone was subjected to

℃In addition CaO decomposition in the calcination vessel at the temperature around 850.

sorbents with highly porous structure and surface area were obtained when the limestone calcinated at high temperature for 30 min. In this process, approximately 8.4 kg of CaO were fluidized in the carbonator column and contacted with CO2 to form CaCO3. 7.6 kg of CaO remain in the moving bed, buffer tanks and transport system. On other hand, concentration of CO2at the exit of the system was also determined for efficiency

estimating of CO2 capture.

Figure 2 Schematic and site photo of the bubbling fluidized bed reactor and moving bed

reactor to test CaO/CaCO3 looping at ITRI.

3.Results and Discussion

We have operation of the continuous-mode and completed the continuous test of CaO/CaCO3looping bench scale experimental system for 57 hours. The CO2capture Tefficiency is more than 99%.(raw conc. of CO2is 14~16%). Figure 3 is continuous-mode operation during 57 hours which the original CO2 concentration of carbonator flue gas inlet and outlet. From start to finish we find the concentration of CO2 in the export value of less than one instrument (TESTO-350S) of the detection limit (0.1%). Our sampling points including the top of the carbonator and cyclone outlet. Figure 4 is the CO2capture efficiency during the 57 hours in the continuous -mode operation. In this figure we can see the CO2 capture efficiency is maintained at above 99%. Figures 3 and 4 by the comparison of the inlet can be found although the CO2concentration

1272 C.-M.Huang et al./Energy Procedia4(2011)1268–1275

changes over time are different, but outlet of the CO2 concentration are lower than the detection limit of carbon dioxide capture efficiency carbonator to maintain more than 99%. The CO2 can not through reactor after a long period of operation. Maybe add CaO 0.1kg per hour, excessive need to be reduced. Therefore carbonator CaCO3/CaO ratios inside the cover in determining the quantity of CaO becomes extremely important. Therefore need to operate the batch experiments. In addition to excessive so as to make up for capture efficiency can be maintained above 99%. Abanades et al. (2009) issued a 30kW test facility in the paper referred to two interconnected circulating fluidized bed reactors capture efficiency of 88%.(6)Although both are fluidized beds, but ITRI's carbonator is bubbling fluidized bed reactor and CSIC-INCAR's carbonator is circulating fluidized bed reactor. CSIC-INCAR the carbonation reactor furnace gas velocities is varied between 1.5-3.5 m/s compared with ITRI of gas velocities is varied between 0.2-0.4 m/s faster, CaO and CO2 may be insufficient reaction time caused by the difference between each other. ITRI's reaction time is about 5-10 seconds and CSIC-INCAR's

reaction time is about 0.9-2 seconds.

concentration of carbonator flue gas inlet and outlet.

Figure 4 It is CO2 capt ure efficiency during 57 hours in the continuous -mode

operation.

Figure 5~8 are 4 times the previous batch-mode operation. Figure 5 is the first cycle in the batch-mode operation of calcination/carbonation studies. In this figure we can find the beginning of the whole system CaO weighed 15 kg in 400 minutes when the carbonator maintained more than 80% capture efficiency. The first cycle's breakthrough curve reached below capture efficiency 10% after about 670 minutes. Figure 6 is the second cycle in the batch-mode operation of calcination/carbonation studies. In this figure we can find the beginning of the whole system CaO weighed 15 kg in 230 minutes when the carbonator maintained more than 80% capture efficiency. The second cycle's breakthrough curve reached below capture efficiency 10% after about 690 minutes. Figure 7 is the third cycle in the batch-mode operation of calcination/carbonation studies. In this figure we can find the beginning of the whole system CaO weighed 15 kg in 105 minutes when the carbonator maintained more than 80% capture efficiency. The third cycle's breakthrough curve reached below capture efficiency 10% after about 400 minutes. Figure 8 is the fourth cycle in the batch-mode operation of calcination/carbonation studies. In this figure we can find the beginning of the whole system CaO weighed 15 kg in 115 minutes when the carbonator maintained more than 80% capture efficiency. The fourth cycle's breakthrough curve reached below capture efficiency 10% after about 370 minutes.

The third cycles and the fourth cycles results are different from the thermogravimetric analyzer (TGA). Figure 9 shows the TGA data recorded CaCO3 at high temperature of conversion vs time. CaCO3 of the conversion by the TGA was reduced when calcination / carbonation cycle increased. The third cycle and the fourth cycle have the same result, so there are other reasons for that. Perhaps the particle size of the change is a likely cause. Table 1 is first to fourth cycles the particle size of the batch-mode operation. CaCO3of the part icle size during repeated experiment will become smaller in Table 1. CaCO3's and the fourth cycle's particle size are the same, perhaps it can be increased the capture efficiency.

Figure 5 Fir st cycle of bat ch-mo de

operat io n.Figure 6 Second cycle of bat ch-mo de

o peration.

C.-M.Huang et al./Energy Procedia4(2011)1268–12751273

Figure 7 Third cycle o f bat ch-mode

operat io n.Figure 8 Fourt h cycle of batch-mode

o peration.

one: Taiwan, part icle size 0.25-0.5 mm. Calcinat ion t emperature 850 °C, 30 min, N2:100 cc/min; car bonat io n temperat ure 650 °C, 40 min, CO2:100 cc/min.

Table 1 Fir st to fourth cycles t he part icle size of t he batch-mode operat io n.

Cycle First Second Third Fourth Original Mean Size(μm) 275.86 192.83 187.46 184.81 262.53 Median Size(μm) 252.13 195.20 190.63 186.76 255.00 Std. Dev.(μm) 128.76 120.33 86.53 63.08 385.15 4.Future work

The results presented above determine to use CaO/CaCO3 looping to capture CO2 is a viable technology. And a lot of new information published by other authors from their laboratory which identified with these results. As we recognized during the batch-mode operation with the problems and get the right to add, we'll continue to batch-mode 1274 C.-M.Huang et al./Energy Procedia4(2011)1268–1275

C.-M.Huang et al./Energy Procedia4(2011)1268–12751275 operation test. Now ITRI is able to stabilize the bubble fluidized bed operation but the moving bed operation is not stable. ITRI will be the end of the year is expected to change the rotary kiln calciner and the use of oxy-fuel to provide heat. The test facility will continue to be used to obtain more data after the calciner is finished changes. ITRI and Taiwan Power Company are planning to build 1MW scale pilot in 2011. These data will provide this pilot.

5.Conclusion

CaO/CaCO3looping is very promising concept for post-combustion CO2capture application. This work has shown that the bubble fluidized bed carbonator, works as a high effective CO2 absorber when it can maintain enough CaO in the carbonator. Particle size, CaO increase number and CaCO3/CaO ratios associated to the operation of the carbonator are relatively important. Pilot results from a 1 kW test facility designed, constructed and operated by ITRI have important viability of the operation. Projects have plan to add many experiments and get experience and design data for the 1 MW scale pilot.

6.Acknowledgement

The authors would like to acknowledge the support from the Energy Fund of Ministry of Economics Affairs, Taiwan.

7.References

- [1] Shimizu T, Hirama T, Hosoda H, Kitano K, Inagaki M, Tejima K. A twin fluid-bed reactor for removal of CO2 from combustion processes. Transactions of IChemE

1999;77(partA):62–8.

- [2] Salvador C, Lu D, Anthony EJ, Abanades JC. Enhancement of CaO for CO2 capture in an FBC environment. Chemical Engineering Journal 2003;96:187–195.

- [3] Abanades JC, Anthony EJ, Wang J, Oakey A. Fluidized bed combustion systems integrating CO2 capture with CaO. Environmental Science and Technology

2005;39:2861–6.

- [4] Prasannan PC, Ramachandran PA, Doraiswamy LK. A model for gas–solid reactions with structural changes in the presence of inert solids. Chemical Engineering Science 1985;40:1251–1261.

- [5] Duo W, Sevill JPsK, Kirkby NF, Clift R. Formation of product layers in solid–gas reactions for removal of acid gases. Chemical Engineering Science 1994;49:4429–4442. - [6] Abanades JC, Alonso M, Rodríguez N, González B, Grasa G, Murillo R. Capturing CO2 from combustion flue gases with a carbonation calcination loop. Experimental results and process development, Energy Procedia 2009;1:1147-1154.

英文文献翻译

中等分辨率制备分离的 快速色谱技术 W. Clark Still,* Michael K a h n , and Abhijit Mitra Departm(7nt o/ Chemistry, Columbia Uniuersity,1Veu York, Neu; York 10027 ReceiLied January 26, 1978 我们希望找到一种简单的吸附色谱技术用于有机化合物的常规净化。这种技术是适于传统的有机物大规模制备分离,该技术需使用长柱色谱法。尽管这种技术得到的效果非常好,但是其需要消耗大量的时间,并且由于频带拖尾经常出现低复原率。当分离的样本剂量大于1或者2g时,这些问题显得更加突出。近年来,几种制备系统已经进行了改进,能将分离时间减少到1-3h,并允许各成分的分辨率ΔR f≥(使用薄层色谱分析进行分析)。在这些方法中,在我们的实验室中,媒介压力色谱法1和短柱色谱法2是最成功的。最近,我们发现一种可以将分离速度大幅度提升的技术,可用于反应产物的常规提纯,我们将这种技术称为急骤色谱法。虽然这种技术的分辨率只是中等(ΔR f≥),而且构建这个系统花费非常低,并且能在10-15min内分离重量在的样本。4 急骤色谱法是以空气压力驱动的混合介质压力以及短柱色谱法为基础,专门针对快速分离,介质压力以及短柱色谱已经进行了优化。优化实验是在一组标准条件5下进行的,优化实验使用苯甲醇作为样本,放在一个20mm*5in.的硅胶柱60内,使用Tracor 970紫外检测器监测圆柱的输出。分辨率通过持续时间(r)和峰宽(w,w/2)的比率进行测定的(Figure 1),结果如图2-4所示,图2-4分别放映分辨率随着硅胶颗粒大小、洗脱液流速和样本大小的变化。

外文翻译 - 英文

The smart grid Smart grid is the grid intelligent (electric power), also known as the "grid" 2.0, it is based on the integration, high-speed bidirectional communication network, on the basis of through the use of advanced sensor and measuring technology, advanced equipme nt technology, the advanced control method, and the application of advanced technology of decision support system, realize the power grid reliability, security, economic, efficient, environmental friendly and use the security target, its main features include self-healing, incentives and include user, against attacks, provide meet user requirements of power quality in the 21st century, allow all sorts of different power generation in the form of access, start the electric power market and asset optimizatio n run efficiently. The U.S. department of energy (doe) "the Grid of 2030" : a fully automated power transmission network, able to monitor and control each user and power Grid nodes, guarantee from power plants to end users among all the nodes in the whole process of transmission and distribution of information and energy bi-directional flow. China iot alliance between colleges: smart grid is made up of many parts, can be divided into:intelligent substation, intelligent power distribution network, intelli gent watt-hourmeter,intelligent interactive terminals, intelligent scheduling, smart appliances, intelligent building electricity, smart city power grid, smart power generation system, the new type of energy storage system.Now a part of it to do a simple i ntroduction. European technology BBS: an integration of all users connected to the power grid all the behavior of the power transmission network, to provide sustained and effective economic and security of power. Chinese academy of sciences, institute of electrical: smart grid is including all kinds of power generation equipment, power transmission and distribution network, power equipment and storage equipment, on the basis of the physical power grid will be modern advanced sensor measurement technology, network technology, communication

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文献综述怎么写 1) 什么是文献综述? 文献综述是研究者在其提前阅读过某一主题的文献后,经过理解、整理、融会贯通,综合分析和评价而组成的一种不同于研究论文的文体。 2) 文献综述的写作要求 1、文献综述的格式 文献综述的格式与一般研究性论文的格式有所不同。这是因为研究性的论文注重研究的方法和结果,而文献综述介绍与主题有关的详细资料、动态、进展、展望以及对以上方面的评述。因此文献综述的格式相对多样,但总的来说,一般都包含以下四部分:即前言、主题、总结和参考文献。撰写文献综述时可按这四部分拟写提纲,再根据提纲进行撰写工作。 前言,要用简明扼要的文字说明写作的目的、必要性、有关概念的定义,综述的范围,阐述有关问题的现状和动态,以及目前对主要问题争论的焦点等。前言一般200-300字为宜,不宜超过500字。 正文,是综述的重点,写法上没有固定的格式,只要能较好地表达综合的内容,作者可创造性采用诸多形式。正文主要包括论据和论证两个部分,通过提出问题、分析问题和解决问题,比较不同学者对同一问题的看法及其理论依据,进一步阐明问题的来龙去脉和作者自己的见解。当然,作者也可从问题发生的历史背景、目前现状、发展方向等提出文献的不同观点。正文部分可根据内容的多少可分为若干个小标题分别论述。 小结,是结综述正文部分作扼要的总结,作者应对各种观点进行综合评价,提出自己的看法,指出存在的问题及今后发展的方向和展望。内容单纯的综述也可不写小结。 参考文献,是综述的重要组成部分。一般参考文献的多少可体现作者阅读文献的广度和深度。对综述类论文参考文献的数量不同杂志有不同的要求,一般以30条以内为宜,以最近3-5年内的最新文献为主。 2、文献综述规定 1. 为了使选题报告有较充分的依据,要求硕士研究生在论文开题之前作文献综述。 2. 在文献综述时,研究生应系统地查阅与自己的研究方向有关的国内外文献。通常阅读文献不少于30篇,且文献搜集要客观全面 3. 在文献综述中,研究生应说明自己研究方向的发展历史,前人的主要研究成果,存在的问题及发展趋势等。 4. 文献综述要条理清晰,文字通顺简练。 5. 资料运用恰当、合理。文献引用用方括号[ ]括起来置于引用词的右上角。 6. 文献综述中要有自己的观点和见解。不能混淆作者与文献的观点。鼓励研究生多发现问题、多提出问题、并指出分析、解决问题的可能途径,针对性强。 7. 文献综述不少于3000字。 3、注意事项 ⒈搜集文献应尽量全。掌握全面、大量的文献资料是写好综述的前提,否则,随便搜集一点资料就动手撰写是不可能写出好的综述。 ⒉注意引用文献的代表性、可靠性和科学性。在搜集到的文献中可能出现观点雷同,有的文献在可靠性及科学性方面存在着差异,因此在引用文献时应注意选用代表性、可靠性和科学性较好的文献。 ⒊引用文献要忠实文献内容。由于文献综述有作者自己的评论分析,因此在撰写时应分清作者的观点和文献的内容,不能篡改文献的内容。引用文献不过多。文献综述的作者引用间接文献的现象时有所见。如果综述作者从他人引用的参考文献转引过来,这些文献在他人

生物英文文献.doc

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