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Greenhouse Gas Control Technologies 7#R##N#Proceedings of the 7th International Conference on Greenhouse Gas Control Technologies 5– September 2004, Vancouver, Canada | 2005

Carbon dioxide capture technology for coal fired boiler

Masaki Ijima; Kazuo Ishida; Toru Takashina; Hiroshi Tanaka; Takuya Hirata; Takahito Yonekawa

Publisher Summary This chapter discusses the consequences of the flue gas impurity removal test obtained by the capture test for CO2 from the flue gas of coal fired boilers. This process is performed using the pilot plant constructed in the Mitsubishi Heavy Industries (MHI) Hiroshima R&D center. This plant has boilers, dust separator, flue gas processing apparatuses, and the desulfurizing system of the wet limestone gypsum method (FGD). The CO2 recovery system is includes a rinse tower to remove sulfur oxides present in the flue gas, a cooling tower to cool the flue gas, an absorbing tower to capture CO2 by “KS-1 solvent,” a water washing tower to recover solvent components accompanying the flue gas from the CO2 absorbing tower, and a regenerating tower to strip CO2 by heating the solvent absorbing CO2 with steam. The purity of the CO2 captured from the flue gas of the coal fired boilers is approx. 99.8 %-dry, which meets the requirement of 95% or higher in purity generally required for CO2EOR. When the concentration of sulfur oxides flowing into the CO2 recovery system is high, the accumulation of heat stable salt, particularly sulfate, increases to cause the deterioration of the solvent. To solve this problem, sulfur oxides must be pre-processed and removed on the downstream side of the CO2 recovery system beforehand.


Journal of Physical Chemistry B | 2014

Hydration structure of CO2-absorbed 2-aminoethanol studied by neutron diffraction with the 14N/15N isotopic substitution method.

Yasuo Kameda; Hiroshi Deguchi; Hirotoshi Furukawa; Yoshiyuki Kubota; Yasuyuki Yagi; Yoshihiro Imai; Noriko Yamazaki; Noriko Watari; Takuya Hirata; Nobuyuki Matubayasi

Neutron diffraction measurements were carried out for CO2-absorbed aqueous 11 mol % 2-aminoethanol (MEA) D2O solutions (corresponding to 30 wt % MEA solution) in order to obtain information on both the intramolecular structure and intermolecular hydration structure of the MEA carbamate molecule in the aqueous solution. Neutron scattering cross sections observed for (MEA)0.11(D2O)0.89, (MEA)0.11(D2O)0.89(CO2)0.06, and (MEA)0.11(D2O)0.89(DCl)0.11 solutions with different (14)N/(15)N ratios were used to derive the first-order difference function, ΔN(Q), which involves environmental structural information around the nitrogen atom of the MEA molecule. Intramolecular geometry and intermolecular hydration structure of MEA, protonated MEA (MEAD(+)), and MEA carbamate (MEA-CO2) molecules were obtained through the least-squares fitting of the observed Δ(N)(Q) in the high-Q region and the intermolecular difference function, Δ(N)(inter)(Q), respectively. In the aqueous solution, the MEA molecule takes the gauche conformation (dihedral angle, ∠NCCO = 45 ± 3°), suggesting that an intramolecular hydrogen bond is formed. On the other hand, values of the dihedral angle ∠NCCO determined for MEAD(+) and MEA-CO2 molecules were 193 ± 4° and 214 ± 8°, respectively. These results imply that the intermolecular hydrogen bonds are dominated for MEAD(+) and MEA-CO2 molecules. The intermolecular nearest neighbor N···O(D2O) distance for the MEA molecule was determined to be 3.13 ± 0.01 Å, which suggests weak intermolecular interaction between the amino-nitrogen atom of MEA and water molecules in the first hydration shell. The nearest-neighbor N···O(D2O) distances for MEAD(+) and MEA-CO2 molecules, 2.79 ± 0.03 and 2.87 ± 0.04 Å, clearly indicate strong hydrogen bonds are formed among the amino group of these molecules and neighboring water molecules.


Archive | 2001

Amine recovery method and apparatus and decarbonation apparatus having same

Tomio Mimura; Takashi Nojo; Kazuo Ishida; Hiroshi Nakashoji; Hiroshi Tanaka; Takuya Hirata


Archive | 2006

Carbon dioxide recovery and power generation

Masaki Iijima; Takuya Hirata; Tomio Mimura; Yasuyuki Yagi


Archive | 2010

CO2 recovery system and CO2 recovery method

Hiromitsu Nagayasu; Takashi Kamijo; Takahito Yonekawa; Hiroshi Tanaka; Shinya Kishimoto; Takuya Hirata; Tatsuya Tsujiuchi; Masaru Chiyomaru; Koji Nakayama; Masahiko Tatsumi; Yasuyuki Yagi; Kazuhiko Kaibara


Energy Procedia | 2009

Current status of MHI’s CO2 recovery technology and optimization of CO2 recovery plant with a PC fired power plant

Shinya Kishimoto; Takuya Hirata; Masaki Iijima; Tsuyoshi Ohishi; Kazuo Higaki; Ronald Mitchell


Archive | 2007

METHOD AND APPARATUS FOR RECOVERING AMINE AND DECARBONATOR PROVIDED WITH THE APPARATUS

Takuya Hirata; Kazuo Ishida; Tomio Mimura; Yutaka Nakakoji; Takashi Nojo; Yuji Tanaka; 富雄 三村; 裕 中小路; 琢也 平田; 裕士 田中; 一男 石田; 貴司 野条


Energy Procedia | 2013

SO3 Impact on Amine Emission and Emission Reduction Technology

Takashi Kamijo; Yoshinori Kajiya; Takahiko Endo; Hiromitsu Nagayasu; Hiroshi Tanaka; Takuya Hirata; Takahito Yonekawa; Tatsuya Tsujiuchi


Archive | 2012

Air pollution control system and air pollution control method

Tsuyoshi Oishi; Hiroshi Tanaka; Hiromitsu Nagayasu; Takuya Hirata; Yoshinori Kajiya; Tomoki Noborisato


Archive | 2013

CO2 RECOVERY DEVICE AND CO2 RECOVERY METHOD

Hiroshi Tanaka; Hiromitsu Nagayasu; Takuya Hirata; Tsuyoshi Oishi; Takashi Kamijo

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Hiroshi Tanaka

Mitsubishi Heavy Industries

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Hiromitsu Nagayasu

Mitsubishi Heavy Industries

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Tsuyoshi Oishi

Mitsubishi Heavy Industries

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Tatsuya Tsujiuchi

Mitsubishi Heavy Industries

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Yasuyuki Yagi

Mitsubishi Heavy Industries

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Takashi Kamijo

Mitsubishi Heavy Industries

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琢也 平田

Mitsubishi Heavy Industries

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