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International Journal of Greenhouse Gas Control
journal homepage: www.elsevier.com/locate/ijggc
Process simulation and parametric sensitivity study of CO
2
capture from
115 MW coal–fired power plant using MEA–DEA blend
Chikezie Nwaoha
a,
⁎
, David W. Smith
b
, Raphael Idem
a
, Paitoon Tontiwachwuthikul
a
a
Clean Energy Technologies Research Institute (CETRI), Faculty of Engineering and Applied Science, University of Regina, SK, S4S 0A2, Canada
b
Saskatchewan Power Corporation (SaskPower), 2025 Victoria Avenue, Regina, SK, S4P 0S1, Canada
ARTICLE INFO
Keywords:
CO
2
capture
Monoethanolamine (MEA)
Diethanolamine (DEA)
Process simulation
ProMax
®
4.0
Parametric sensitivity
Amine vaporization
ABSTRACT
This study used ProMax
®
4.0 process simulator (rate–based model) to conduct a parametric sensitivity of carbon
dioxide (CO
2
) capture from a 115 MW coal–fired power plant (Boundary Dam 3 power plant) using mono-
ethanolamine (MEA) and diethanolamine (DEA) blend. Saskatchewan Power Corporation (SaskPower), Canada
provided the flue gas composition used in this study. The validated simulation was used to determine the effects
of some process variables (independent process variables) on different dependent process variables. The in-
dependent process variables are flue gas temperature (T
FG
,
o
C), lean amine temperature (T
LA
,
o
C), lean amine
flow rate (F
LA
, tonne/day), lean amine concentration difference (C
MEA–DEA
, kmol/m
3
) and reboiler temperature
(T
REB
,
o
C). The dependent process variables are MEA and DEA vaporization from the absorber, CO
2
absorption
efficiency (%), regeneration energy (GJ/tonne CO
2
), rich amine loading (RAL, mol CO
2
/mol amine) and lean
amine loading (LAL, mol CO
2
/mol amine). Amine degradation was investigated by the O
2
absorption rate (tonne
O
2
/day), NO absorption rate (tonne NO/day) and NO
2
absorption rate (tonne NO
2
/day). The vaporization rates
of MEA (tonne MEA/day) and DEA (tonne DEA/day) were also investigated. The contribution of amine and
water make–up costs, regeneration energy, pump electrical energy, blower electrical energy and compressor
electrical energy towards variable operating expenditure (V–OPEX) were also investigated. Results showed that
NO also contributes to amine degradation. From the parametric analysis it was observed that T
REB
has the
greatest influence on most of the dependent process variables. It was also discovered that the regeneration
energy, compressor electrical energy and amine, water make–up cost and cooling water contributed 82.5%,
12.3%, 1.1%, 0.9% and 0.5% of the V–OPEX respectively.
1. Introduction
Carbon dioxide (CO
2
) capture from coal–fired power plants has
gained huge interest globally because of its large emission of CO
2
.
According to the International Energy Agency, most of the 2015 CO
2
emissions in the energy sector were contributed by coal (IEA, 2016).
Coal, being an abundant domestic resource in many countries, has
historically been the favored fossil fuel for electricity generation. There
are several technologies for capturing CO
2
from large industrial sources
namely absorption, adsorption, membrane, and cryogenic technology.
Considering these available technologies, the absorption process using
reactive amine solvents is the most matured and capable of achieving
90% CO
2
capture (Rao and Rubin, 2002, 2006; Abu-Zahra et al., 2007;
Rochelle, 2009). The benchmark amine solvent for CO
2
capture is the
primary amine monoethanolamine (MEA). However, it is accompanied
by high corrosion rate, high energy for solvent regeneration, solvent
degradation, emissions and vaporization (Dinca and Badea, 2013; Stec
et al., 2015; Dux and Schallert, 2016; Fytianos et al., 2016; Nguyen
et al., 2010; Nwaoha et al., 2017a). This has led to blending amine
solvents in order to maximize their individual CO
2
capture potentials
(Chakravarty et al., 1985). Tertiary amines (like methyldiethanolamine,
MDEA) and/or sterically hindered amines (like 2–amino–2–-
methyl–1–propanol, AMP) are blended with very reactive polyamines
(piperazine, PZ; diethylenetriamine, DETA etc.) in order to improve
absorption–desorption efficiencies (Idem et al., 2006; Zhao et al., 2017;
Artanto et al., 2014; Nwaoha et al., 2016a,b; Zhang et al., 2017; Khun
Wai et al., 2018).
Currently there are two commercial amine–based CO
2
capture
plants integrated in coal–fired power plants, the first is the 115 MW
Boundary Dam plant in Saskatchewan, Canada commissioned in Fall
2014 with the capacity to capture 1 million tonne CO
2
/year
(SaskPower, 2018). The second is the Petra Nova facility commissioned
in January 2017 which has the capacity to capture CO
2
from the
240 MW slipstream of the flue gas from WA Parish Unit 8, Texas, United
https://doi.org/10.1016/j.ijggc.2018.06.006
Received 6 November 2017; Received in revised form 22 May 2018; Accepted 6 June 2018
⁎
Corresponding author.
E-mail addresses: nwaoha2c@uregina.ca, chikezienwaoha@live.co.uk (C. Nwaoha).
International Journal of Greenhouse Gas Control 76 (2018) 1–11
1750-5836/ © 2018 Elsevier Ltd. All rights reserved.
T