Accelerating Net Zero
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E1-05, First Floor, Block E
IIT Madras Research Park
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Chennai 600113, Tamil Nadu
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SHORT
SERIES
JUNE 2024
deep
dive into
CARBON CAPTURE | GREEN FUELS |
SCOPE 3 EMISSIONS | CLIMATE FINANCE
ENERGY CONSORTIUM IS AN INSTITUTE OF EMINENCE CENTER
ENERGY CONSORTIUM IS AN INSTITUTE OF EMINENCE CENTER
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OUR FOUNDING MEMBERS
ENERGY CONSORTIUM IS AN INSTITUTE OF EMINENCE CENTER
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Advanced Gas
Turbine Engine
Technologies
Energy
Storage &
Conversion
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Energy
Carbon Capture,
Utilization &
Storage
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Resilient energy
systems
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Energy
Enhancement
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Rangan Wind
Energy CoRE
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ENERGY CONSORTIUM IS AN INSTITUTE OF EMINENCE CENTER
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SHORT
SERIES
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he Energy Consortium was founded in December 2021
with a bold vision: to enable India’s journey towards a
low-carbon energy future. In this short span, we have
10 global energy majors, including those in hard-to-
abate and hard-to-electrify sectors as well as those at
the forefront of leveraging digital means for energy transition,
collaborating with us. We are now participating heavily in two major
alliances, one focused on energy storage and another on green fuels.
We are actively partnering and advising government agencies
on topics of national and international importance and have
represented the cause at the COP28 in Dubai. This has allowed us to
drive collective action at scale and emboldens us to contribute more
assertively towards the Net-Zero journey of India.
As per the Ministry of New & Renewable Energy data, India, at
the end of 2023, became 4th globally in Renewable Energy Installed
Capacity, 4th in wind power capacity and 5th in solar power capacity.
We recognize that the time has come to elevate our mission. We must
transition from just enabling progress to actively accelerating the
realization of a Net Zero future.
Together with our partners in industry and government, we
can ensure that Net Zero is not just an aspiration, but an imminent
reality for India and the world. Building on our vision, we are
now in mission mode, fully dedicated to Accelerating Net Zero at
the Energy Consortium. This commitment is reflected in our new
mission statement and our revised strategy of advancing research
in clean energy sources, including offshore wind, green hydrogen,
green fuels, and large-scale industrial electrification, while
intensifying our efforts in carbon capture, utilization and storage
(CCUS).
In this short series, we bring together four seminal topics that
are going to shape how we accelerate achieving net zero. We explore
through two topics the role that carbon dioxide capture technologies
will play and its centrality in achieving net zero, as well as the role of
green ammonia in this journey.
In addition to the role played by technology, it is also
important to unlock the decarbonization potential through
a critical analysis of the various GHG contributors and
systematically reducing not just Scope 1 & 2 emissions but
also Scope 3 emissions. Therefore, one topic specifically
explores the strategies required for addressing Scope 3
emissions. Finally, in this short series, we also explore
the key enablers for financing climate change and the
role of public-private partnerships in our fifth topic.
The global transition to a net-zero carbon
economy is not just an environmental imperative but
also an economic opportunity. By leading the charge
in clean energy innovation and carbon capture,
we are paving the way for a sustainable future that
benefits our planet and future generations.
Dr. Nikhil Tambe
CEO – Energy Consortium, IIT Madras
Adjunct Professor, Dept. of Applied Mechanics, &
Biomedical Engineering, IIT Madras
avigating net-zero is often a journey of two
steps forward and one step back. Conflicting
requirements, short-termism and despondence
over the unknowable and unplannable future
often leads to inaction on our long-term goals.
Goals are clear; however, it is the path that needs to be shown.
The Path to Decarbonization special issue by the Energy
Consortium at IIT Madras was launched during the Energy
Summit 2023 to throw some light on this journey that every
individual, organisation and country should undertake for the
sake of humanity. It talked about some of the actions leading
corporates are taking and the pathways to do more. However,
we find that we need faster action. Planet will survive and
find a new-normal, however it is humans that needs it to be in
perfect balance to avoid a pernicious fate.
Accelerating Net Zero is the second edition from the
Energy Consortium, where an attempt is made to address
critical technology and policy elements that could accelerate
this transition to net-zero. Though net-zero is a state point,
the journey is a path function that needs to be traversed with
minimal entropy generation. In this journey, there are many
solutions, which may not be clear and some, where the choices
are hard.
In this edition, a few such examples such as the role of
CCUS in net-zero or the understanding of scope 3 reporting
are explored in detail. The role of capital as a catalyst in this
acceleration is presented as a framework to be built. Now, the
pathways are becoming visible and with other ingredients
falling in place, we wish the acceleration towards net-zero hits
escape velocity. Happy reading!
Dr. Satyanarayanan Seshadri
Faculty Head, Energy Consortium, IIT Madras
Associate Professor, Dept. of Applied Mechanics &
Biomedical Engineering, IIT Madras
FOREWORD
PREFACE
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CONTENTS
Role of CCUS in net-zero transition
Rajnish Kumar
08
Advances in Ammonia and its role as a
green fuel for net zero
Kothandaraman Ramanujam
18
Unlocking India’s decarbonization potential through a
critical analysis of scope 3 emissions
Rahul Muralidharan and Nikhil S Tambe
28
Public private partnership: a key enabler for financing
climate change
Ajay Patil and Aayushee Singh
40
Copyright @IIT Madras.
All rights reserved.
Hari J Subramani, Chevron Tech Ventures
Arun Ranganathan, Infosys
M. Venkatachalam, NLC India Ltd.
INDUSTRY
ADVISORS
Dr. Nikhil S Tambe
Srivatsan S
EDITORIAL
BOARD
Authors
iStock/Getty Images
PHOTOS
Francis J
CREATIVE
HEAD
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ClimeWorks carbon
dioxide direct air capture
facility in Reykjavik,
Iceland.
Picture courtesy:
Nikhil S Tambe
CARBON CAPTURE
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Role
of CCUS in
Net Zero
Transition
Prof. Rajnish Kumar
Department of Chemical Engineering,
IIT Madras
hile role of renewables, solar, wind, hydro/waves,
hydrogen etc. including nuclear would ensure a cleaner
future. Current energy need, and proposed GDP growth
in many parts of the world could not be achieved without
ensuring implementation of CCUS. In general, people
around the world are aware of the effect of rising CO2 in the atmosphere
and resulting global warming. Prime challenge for the scientific
community is to educate people that the scale at which CCUS has to be
implemented has no parallel in the history of human kind. Significant
effort is required to identify a solution which is not only economical but
also sustainable at the scale it has to be delivered.
In 2023, not a single electricity producing commercial plant around the
world has been able to demonstrate CCUS in its entirety.
CCUS is essentially a three-step process, the first step is to capture the
carbon dioxide at its source;
1. Point source capture (or separation) of CO2 from its associated
gases (mostly N2, as the other toxic gases which are at a much lower
concentration has already been captured) from industries like steel
manufacturing, cement manufacturing, electricity production etc.
For CO2 capture the most mature process is use of mono-ethanol amine
(MEA, or a derivative of this molecule) for CO2 capture. An alternate route
which uses solid adsorbent/absorbent like, carbon nanotubes (CNT), metal
organic framework (MoF) etc. has not been proven at this scale. Some
Innovative solutions also exists (hydrates, ionic liquids etc.) which are being
tested at lab/pilot scale. If one talks about the most mature process which
utilizes a chemical solvent (like MEA) to capture CO2 from its associated
gases, the biggest challenge is in recycling and regeneration of MEA,
assuming that the corrosion issues could be handled appropriately. Some
of the major concerns are regeneration cost, loss of active material during
regeneration, and significantly large losses of water from cooling towers
and other operations. If one talks about CNT, and MoF like materials for
CO2 capture, corrosion is not an issue, however, generation of such
material itself at such a scale is a big challenge. MEA based processes are
being implemented for demonstration around the world, with a typical cost
of USD 30-50 per ton of CO2 captured. This only captures the process cost
of CO2 capture from using MEA based solvent. However, if one looks at the
raw material (i.e. MEA itself) it has its own CO2 footprint. MEA is produced
from reacting ammonia and ethylene oxide, thus, production of these two
chemicals should also be decarbonised and the cost of the same should
appropriately be added in the overall CO2 capture cost.
Direct air capture (DAC) is a technology which many believes is a way
to go, the proponent of this approach takes a futuristic view. It is argued
that producing fossil fuels and capturing CO2 from its utilization is an
endless trap, rather one should stop using fossil fuels all together! This
approach ensures no anthropogenic CO2 emission into the atmosphere (at
least not from use of fossil fuel). Sometime in future when there is no CO2
emission from point source, DAC would ensure that all the CO2 which has
been emitted by humans (so far) could be captured directly from air, and
its concentration could be brought down to 350-400 PPM level. However,
capture of PPM level CO2 from a gas stream is not going to be trivial, and
this process could be prohibitively expensive, current cost is close to 200
USD per ton for captured CO2. Further, the material/chemical required to
capture PPM level CO2 (from air) is currently quiet immature, and actual
cost of the process will not be evident unless one does a proper life cycle
analysis of this approach.
The second step in CCUS involves utilization of captured CO2.
Here one has to realise that an electricity production plant or a cement
manufacturing unit produces tonnes of CO2 every day!
2. Transporting the captured, relatively purer CO2 (which comes
from step 1) to the utilisation site where CO2 could be processed (with a
hydrogen rich source, or H2) and converted to a liquid chemicals. Some of
the typical chemicals are methanol, dimethyl ether, formic acid, aviation
fuels etc.
However, if one looks
at the raw material
(i.e. MEA itself) it has
its own CO2 footprint.
MEA is produced from
reacting ammonia
and ethylene oxide,
thus, production of
these two chemicals
should also be
decarbonised and
the cost of the same
should appropriately
be added in the overall
CO2 capture cost
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In principle, the captured CO2 could be converted into fuels or
chemicals which would help cut down the requirements of fresh fossil
fuels. And if all the emitted CO2 is captured, one day there would be
no requirement of fossil fuel exploitation. Gaseous fuels to liquid fuel/
chemical (GTL) has been an age old research topic, idea of GTL was to
convert methane rich natural gas to liquid fuel like gasoline which could
be transported easily thus cutting down on CO2 emission associated with
natural gas storage and transport. However, challenge in conversion of CO2
to a fuel or chemical has one additional bottleneck, fresh source of green
hydrogen which could technically convert CO2 into a useful hydrocarbon
for utilization as a fuel. One has to thus identify what works better, a pure
hydrogen economy (where no hydrogen would be wasted on CO2 to create
a circular economy), or integrate hydrogen economy to circular economy
where captured CO2 is converted back to a value-added chemical or fuel.
Hydrogen for both these economies will essentially come from the same
source, a possible solution is simultaneously running both the economies.
As of today, there are many demonstration plants which exist around
the world to convert CO2 (or CO) to methanol and DME, or aviation fuel.
However, production cost is prohibitively high and these plants operates
for demonstration purpose alone.
Tons of CO2 however being captured in step-1 can’t be converted
into useful chemicals, one has to look at the thermodynamics of the
conversion process to understand the energy requirements to convert
all these CO2 into a chemical. Further, the cost of CO2 coming out of DAC
could be as high as 200 - 1000 USD per ton and considering that when one
adds similarly priced green hydrogen in the mix to produce a commodity,
the end product can’t be used for mass market application. This perhaps
suggests that it could be more economical to sequester the captured CO2
rather converting the same to a chemical/commodity.
3. Majority of the CO2 which could not be converted (in step-2) has to
be transported to the sequestration sites. While this step may look costly
as there is no value addition, it is a fact that there is no use of such a large
quantity of CO2 and one has to invest in CO2 pipelines for transportation of
these to sequestration sites.
The sequestration sites could be one of these; deep coal bed
reserves, depleted oil and gas field, saline aquifers, basalt rocks under
the earth or unconsolidated sediments deep inside the sea-bed where the
existing water in the pores of these sediments would convert into solid
CO2 hydrates making it thermodynamically stable for geological time
scale. Each of these sites have certain advantages and disadvantage and
a significant research efforts and field trials has to be done to identify
the challenges which would allow one to come-up with a well-informed
solution. Any solution should be full proof (with continuous monitoring of
sequestered CO2) and should have sufficient capacity to sequester billions
of tons of CO2 for geological time scale. Currently most of the CO2 pipelines
are being used to transport CO2 for EOR application which basically
allows one to scale-up the process for sequestration of tons of these CO2 in
geological sites.
PATH FORWARD:
Since the amount of CO2 utilized and sequestrated is directly proportional
to the amount of CO2 captured. Thus, the first step i.e. CO2 capture should
be the prime focus and looking at the scale, measuring sustainability of the
process should be the prime importance. The materials/chemicals which
are supposed to capture tons of these CO2 are very few, one such molecule
mono-ethanolamine (MEA, or a variation of this material), which has been
proven at large scale through demonstration units, industries who have
implemented these solutions for demonstration should come out with a
report on challenges which were faced. Other processes which are directly
or indirectly not related to MEA have only been demonstrated at lab scale.
Due to lack of investment and insufficient focus, scale-up of the material
synthesis has not been demonstrated, this is perhaps the other bottleneck
of step-1 as far as point source capture is concerned.
Any solution should
be full proof (with
continuous monitoring
of sequestered CO2)
and should have
sufficient capacity
to sequester billions
of tons of CO2 for
geological time scale
Talking about step-2, public perception for CO2 utilization is very
positive, this makes one to believe that we can emit as much CO2 as we
want, all of these could be converted into useful products. In reality,
90% of CO2 utilization solution has been demonstrated to work with
pure CO2, and pure CO2 could only be made available once it has been
captured from point sources (or directly from the air) as discussed in
step-1. CO2 utilization if possible could lead to a circular economy where
CO2 being emitted from industries would be converted to make chemicals
and fuels, thus, reducing the demand of fresh fossil fuel. A mature
circular economy envisions that all the process energy requirements
for conversion of CO2 to hydrocarbon would come from solar or other
renewable energy resources. In theory this is possible, however, in
reality, time and investment required to achieve renewable energy based
economy may not be realistic. Step-3, CO2 sequestration has very poor
public perception, significant work is required to build a positive public
perception for this step. Even in industry, sequestration is looked upon as
money down the drain, and industries are reluctant to invest sufficient
money on this crucial step of CO2 sequestration without which net zero
by 20XX would remain a dream. In absence of positive public perception,
and poor encouragement from industry (and government) around
the world, research on CO2 sequestration has suffered significantly.
Further, not many field trial has been done to study CO2 sequestration,
as investment is prohibitively high and land lease or site lease for such
activities are mired with multi-level govt. and non-govt. clearances. In
short, a holistic road map to achieve mini targets are necessary, and a
significant investment in all the three steps discussed at the start of this
document would be necessary.
IITM EFFORTS FOR CCUS:
IITM has been working with solid adsorbent as active ingredient for
the removal of CO2 from flue gases, basically from a point source which
typically is 10-15% CO2 mixture along with N2 and O2. Such point source
capture of CO2 is relevant for coal fired power plants, cement industries,
steel manufacturing etc. One of the focus of such studies are the kinetics
of CO2 capture and separation efficiency of carbon dioxide from flue gas
mixture. Kinetics of such capture does not get much attention; however,
this is one of the biggest bottlenecks in scale-up of any laboratory process
to pilot plant scale and eventually for commercialization. Next biggest
challenge which pertains to regeneration of the absorber/adsorber has
been studied in detail using state of the art analytical facilities like SEM,
PXRD, and FTIR spectroscopy to gain mechanistic insights. Such detailed
analysis on regeneration and reusability of active ingredient is essential
for a robust process. Some of these active ingredients were eventually used
for a pilot scale demonstration which is currently running.
A number of methods can be used to capture carbon dioxide (CO2)
from its mixture; adsorption, absorption, and membrane separation etc.
However, when it comes to capturing CO2 from a rich mixture of CO2 (more
than 25% CO2 in the stream), such mixtures are typically available after
gasification of coal, in bio-methane production and could also be very
relevant to future cement industries, one prefers a physical absorption/
adsorption. One such physical and novel process is gas separation using
gas hydrates formation and dissociation cycle. One of the major advantages
of using gas hydrates process is use of water as a working medium
to separate gases. Water needed in this process could be saline water,
effluent water or fresh water. Hydrate based process for CO2 separation
from its mixture has been studied extensively. However, a commercially
viable hydrate based CO2 separation process demands a rapid hydrate
formation rate. Higher solubility of hydrate forming guest in water and
larger contact area between the hydrate formers and water. These factors
reduces the mass transfer resistance, resulting in faster hydrate formation
rate (faster kinetics) and allows one to scale-up the process for pilot plant
demonstration. Research groups at IITM has given new patented reactor
designs and suitable additives to ensure scale-up of the process of gas
One of the major
advantages of using
gas hydrates process
is use of water as
a working medium
to separate gases.
Water needed in
this process could
be saline water,
effluent water or
fresh water. Hydrate
based process for
CO2 separation from
its mixture has been
studied extensively
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hydrate based process. Currently, a large 30 litres demonstration of this
process is operational at IITM which has demonstrated a modular design
for separation of CO2 from a rich gas mixture with reasonable kinetics
which operates in continuous mode like a PSA approach. Talking about
PSA, IITM has done extensive work on carbon dioxide capture using
MoF/ZIF, activated carbon-based adsorbents, Zeolite materials etc. for
adsorption of CO2 rich and CO2 lean gas mixtures. Further, solid materials
which chemically binds to CO2 has also been studied in detail for direct air
capture application. An end to end solution for direct air capture has been
demonstrated and an operational pilot plan exist in the campus.
As discussed above, captured carbon dioxide needs to be either
utilized or sequestrated. CO2 utilization is a very rich research field,
and IITM has developed quiet a number of such processes where at
laboratory scale CO2 to methanol, formic acid, methane and other higher
hydrocarbon through carbon -carbon coupling has been demonstrated.
CO2 utilization processes have difficulty in scale-up and IITM is looking
forward to demonstrate such processes at large scale, however, this
is still on going. However, a significant work on fundamental science
and demonstration of CO2 sequestration demonstrations have been
done at IITM. Carbon dioxide sequestration is defined as storage of
anthropogenic CO2 in geological formations either permanently or for
geologically significant time periods. Depleted oil and gas reservoirs,
saline aquifers, unmineable coal beds and deep-sea beds are geological
formations that can be used for long-term CO2 sequestration. India has a
complex and diverse geology. Much of the geology of present-day India is
a result of volcanic eruptions dating back to prehistoric eras. The Indian
subcontinent is mantled with the remnants of at least five continental
flood basalt provinces that occurred between the middle Proterozoic to
the late Cretaceous-early Tertiary eras. The geographical land area of
India can be divided into three parts: The Deccan Trap (youngest of the
five continental flood basalt provinces), Gondwana and Vindhayan. The
Deccan Trap is acknowledged to be one of the largest volcanic features
on Earth. It presently occupies around half a million square kilometers
of western and central India and southernmost. Such sediments are
also prominently found under the sea-bed and could be a rich source of
CO2 sequestration. An alternative solution exist in the form of injecting
CO2 in either gaseous or liquid form 100-500 m beneath the seabed and
sequester it in the form of clathrate hydrates within the bounds of
the gas hydrate stability zone (GHSZ). CO2 storage in the form of solid
hydrates under the sea-bed is promising, as 1 m3 of CO2 hydrate can store
120–160 m3 of CO2 gas at STP. Studies like, effects of water salinity and
clay on CO2 hydrate formation to comprehend the effect of electrolyte and
capillary effects on the interlayer pores have been studied in laboratory
scale at IIT Madras. These studies have also helped in determining
the appropriate CO2 injection depth for hydrate formation in such
unconsolidated sediments in the deep sea. Further, IITM researchers
have investigated different kinetic promoters with porous silica gel, silica
sand, pumice stone etc. to concluded that certain additives could improve
the efficiency of such sequestration by influencing the induction time and
in improving the degree of hydrate formation. A pilot scale demonstrator
for CO2 sequestration was developed at IIT Madras which is equipped
with mild fracking setup, injection wells (both vertical and horizontal)
for liquid/gaseous CO2 injections. This unit not only the measures the
rate and quantity of CO2 sequestrated at conditions similar to sub-
sea environment, it also could study the stability of sequestered CO2.
Multiple options for efficient CO2 sequestration was demonstrated and It
was also identified that the sequestered CO2 could be stable upto 10-12 oC
rise in sub-sea temperature.
FIGURE 1. Demonstration of a multi-bed reactor for CO2 capture using Gas-Hydrates Formation and Dissociation Cycle
FIGURE 2. Demonstration of point source CO2 capture in a mobile container unit
The Deccan Trap
(youngest of the five
continental flood
basalt provinces),
Gondwana and
Vindhayan. The
Deccan Trap is
acknowledged to be
one of the largest
volcanic features on
Earth. It presently
occupies around
half a million square
kilometers of western
and central India and
southernmost
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FIGURE 3. Direct Air Capture Demonstration at IIT Madras
FIGURE 4. Demonstration of CO2 sequestration 100-500 m below the sea-bed.
*The longer version of this document has been published elsewhere, please follow the DOI link
https://doi.org/10.1021/acsengineeringau.4c00013
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