https://www.google.com.au/amp/s/bravenewclimate.com/2013/01/16/zero-emission-synfuel-from-seawater/amp/

Zero emission synfuel from seawater
 Barry Brook
4 years ago

* <https://bravenewclimate.files.wordpress.com/2011/10/jm.jpg>Guest post*
 by John Morgan
<http://en.search.wordpress.com/?q=%22John+Morgan%22+site:bravenewclimate.com&t=comment>
. *John runs R&D programmes at a Sydney startup company. He has a PhD in
physical chemistry, and research experience in chemical engineering in the
US and at CSIRO. He is a regular commenter on BNC*.

You can follow John on *Twitter*@JohnDPMorgan
<https://twitter.com/JohnDPMorgan>

———————————–
Introduction

Liquid hydrocarbons account for about one third of fossil carbon dioxide
emissions
<http://en.wikipedia.org/wiki/Carbon_dioxide_in_Earth%27s_atmosphere#Sources_of_carbon_dioxide>,
and while transition to electric vehicles is possible for some passenger
transport, it is simply not feasible to substitute for liquid fuel in most
long haul transport, aviation, or agricultural and industrial prime movers.
Synthesizing fuel from carbon dioxide extracted from air is possible in
principle but horrendously expensive.  Yet, if we are to achieve CO2 levels
of 350 ppm from our current 392 ppm, CO2removal from the biosphere appears
necessary.

Two papers published last year described a new approach to zero emissions
synfuel, looking at direct carbon dioxide extraction from seawater.  The
new insight in these papers is that CO2 is very soluble in seawater, where
the concentration is about 140 times higher than in the atmosphere. This
could make seawater extraction a lot cheaper than direct air capture.

The work was done by the US Navy
<http://jrse.aip.org/resource/1/jrsebh/v4/i3/p033111_s1?isAuthorized=no> (full
text here <http://www.dtic.mil/cgi-bin/GetTRDoc?AD=ADA539765>), and by the Palo
Alto Research Center <http://69.12.216.122/co2extraction.pdf> (PARC),who
each developed membrane processes to extract CO2from seawater.   The Navy’s
interest is military – shipboard production of synthetic jet fuel far from
supply lines – but I figure we can beat this sword into a ploughshare.

Rather than going after the CO2 directly with chemical scrubbers, they use
electrochemical processes to split seawater into an acid and base stream,
and the CO2 bubbles off from the acidified water.  The two streams are
recombined and returned to the ocean.  While these processes are novel,
they are very similar to a number of ion exchange processes, including
desalination, which are currently deployed at scale.

The Navy costed the production of jet fuel at sea.  But they neglected to
include the cost of energy for the carbon capture process.  I used the PARC
research to estimate it and include it in the Navy costings.  I arrived at
$1.78 per litre. I was also able to calculate the cost of just the carbon
capture part of the process at about $114 per tonne of CO2.

But if we don’t insist on running these processes on an expensive
ocean-going platform, the cost drops to $0.79 per litre for synfuel and $37
/tCO­2.  The costs are rough and there are a number of caveats, but this is
surprisingly low. To put it in context, the American Physical Society
recently reviewed carbon capture from air
<http://www.aps.org/policy/reports/assessments/upload/dac2011.pdf>, and
“optimistically” costed it at about $600/tonne.

The Navy costings are based on commercially available equipment whose
capital and operating costs are understood for all processes except the
membrane CO2 extraction. Analogous processes like desalination are
available for a cost baseline for membrane extraction.  The costing assumed
power from Navy nuclear reactors. (They also costed OTEC power – Ocean
Thermal Energy Conversion – but this is not a commercially available
technology.)

I describe the CO2 capture and fuel synthesis processes below, and show how
the costings were derived.  I also consider how the costs would change for
civilian nuclear electricity (Table 1).  In brief, accepting the Navy’s
assumptions leads to plausible prices for synfuel and carbon capture, but
the amount of new power generation required makes very large volume
production unlikely.

A spreadsheet with my cost calculations can be *downloaded here:* Synfuel
cost model
<https://bravenewclimate.files.wordpress.com/2013/01/synfuel-cost-model.xlsx>
*.*

*CCS – Carbon capture from seawater*

Concepts for carbon capture from air have been developed, but never
realized.  The basic idea is to pass air over alkaline scrubbers, such as
amine or carbonate solutions, extract the CO2, and recycle the scrubber
solution.  Because the concentration of CO2 in air is so low, a very large
surface area is required, and the process is energy intensive and overall
very expensive.

The American Physical Society prepared a technology assessment
<http://www.aps.org/policy/reports/assessments/upload/dac2011.pdf> on this
approach in 2011. The results weren’t promising.  A 1 Mt/yr CO2 extractor
comprised five 1 m x 1 m x 1 kilometre long air contactors, occupying about
1.5 km2.  The cost, so far as it could be determined for an undeveloped
technology, and making optimistic assumptions, was about $600 per tonne.
Another 2011 study estimated costs based on current experience with trace
gas removal systems at about $1000 per tonne
<http://www.pnas.org/content/108/51/20428.full.pdf+html>.
[image: Graphic – cover of the APS report, with link]
<http://www.aps.org/policy/reports/assessments/upload/dac2011.pdf>

Graphic – cover of the APS report, with link

But CO2 is very soluble in water, and its concentration in the ocean is
about 140 times higher than in air.  So we are using the whole of the ocean
surface as an air contactor right now – for better or worse!  The
extraction system is ‘built’, we just need to recover the CO2.

The PARC and Navy researchers both used the clever approach of acidifying
seawater with H+ ions generated by water electrolysis, forcing the CO2 to
bubble off.  The PARC system in the illustration used a stack of
semipermeable membranes sandwiched between two electrodes.  Inside the
stack, H+ is generated on one side of a membrane, and OH– on the other,
which creates alternating acid and alkaline compartments.  CO2 is recovered
as gas from the acid stream, which is then recombined with the alkaline
stream and returned to the ocean as CO2-depleted seawater.  The Navy
process chemistry is similar, but uses ion exchange resin beds instead of
the internal membrane stack.

The process has not been scaled up, but the technology and challenges are
similar to reverse osmosis desalination, so there seems to be no in
principle reason why it couldn’t be.  The lifetime of membranes operated in
seawater is also unknown, but again, membrane desalination of seawater
shows the problem can be overcome, using techniques like polarity reversal
to remove scale formation.
[image: Figure 1. The membrane separation system developed by PARC.
Seawater (SW) is pumped through alternating bipolar and anion exchange
membranes (BPM, AEM), and an electrolyte solution (ES) is pumped past the
electrodes, separated from the seawater streams by a cation exchange
membrane (CEM). H+ and OH- form on opposite sides of the BPM, creating
acidic and basic compartments.]
<https://bravenewclimate.files.wordpress.com/2013/01/sw_fig1.png>

Figure 1. The membrane separation system developed by PARC. Seawater (SW)
is pumped through alternating bipolar and anion exchange membranes (BPM,
AEM), and an electrolyte solution (ES) is pumped past the electrodes,
separated from the seawater streams by a cation exchange membrane (CEM). H+
and OH- form on opposite sides of the BPM, creating acidic and basic
compartments.

This process doesn’t require material inputs of acids or bases – they are
generated internally by electricity, and it is non-polluting – only the
original seawater is discharged, minus the CO2.  The process consumes 242
kJ per mole of CO2.

Applying the capital, operating expense, and cost of energy assumptions
made by the Navy researchers gives a carbon capture cost of about $114 per
tonne CO2, using Navy nuclear electricity at 7.0 c/kWh.  If sequestered –
perhaps by injection into spent offshore oil or gas fields, as this is a
marine process – this would be offset by any carbon price that might apply,
currently $23/tonne in Australia, for a net $91 per tonne (exclusive of
sequestration costs).

The Navy estimated the capital cost of the carbon capture process at $16m
for a 715 tCO2 per day plant.  Unfortunately no justification is offered
for this cost, so I am unable to check it, and it seems quite low.  I have
used this cost as given, but it may underestimate the CO2capture cost.

As a purely speculative exercise, what would it take to draw atmospheric
carbon down to 350 ppm with just this technology?  If we follow the
American Physical Society in their technical assessment of direct air
capture and set a target of reducing atmospheric CO2 to 350 ppm by
capturing 400 Gt over a hundred years, we would need to collect 4 Gt/yr,
from the perspective of an already decarbonised society.  We would require
the power of about 700 AP-1000 nuclear reactors.  At the Chinese cost of
$1.3b apiece and an 80 year lifetime this would cost a bit over $1 trillion
dollars.  That sounds like a lot of money. But its only about the cost
of America’s
2003 Iraq War <http://en.wikipedia.org/wiki/Financial_cost_of_the_Iraq_War>
spread
over the century, so I guess it’s a question of priorities.

*CCS – Carbon capture and synfuel*

The feedstock for fuel synthesis is hydrogen, and a source of carbon.
Commercial synfuel operations have all used fossil carbon, such as natural
gas, or coal in coal-to-liquids processes.  They address availability of
liquid hydrocarbons, but are terrible emitters, using fossil carbon both as
a material input and to provide the energy to run the process. CO2 extracted
from seawater is an ideal carbon source – it embodies negative emissions
and is very pure, free of sulphur and other impurities.

In the Navy concept <http://www.dtic.mil/cgi-bin/GetTRDoc?AD=ADA539765>,
carbon dioxide is converted to carbon monoxide by reaction with hydrogen.
The carbon monoxide is further condensed with hydrogen in the Fischer-Tropsch
process <http://en.wikipedia.org/wiki/Fischer-Tropsch_process>, to produce
hydrocarbon.  The overall reaction is, nominally,

11 CO2 + 34 H2 à C11H24 + 22 H2O

Fischer-Tropsch produces a range of pure alkanes, with no aromatics or
sulphur, although heavier hydrocarbons may require cracking.  Alternative
fuels such as methanol or dimethyl ether could also be produced from
the CO2 and
H2 feedstock, and would require no further processing.  So the end product
is much closer to a final fuel formulation than, say, crude oil.

A source of hydrogen is required, and the energy required to produce the
hydrogen is the single most expensive component in the whole process.  The
Navy used performance data for large scale 2 MW commercial water
electrolysis units that cost $2m each and can produce 485 m3 per hour of
hydrogen.
[image: Figure 2. Hydrogen Technologies 2 MW water electrolysis unit.]
<https://bravenewclimate.files.wordpress.com/2013/01/sw_fig2.png>

Figure 2. Hydrogen Technologies 2 MW water electrolysis unit.

Suppose the whole process were powered by Navy nuclear electricity.  The
USS Nimitz has two reactors that together produce 200 MWe.  Using 37 MWe
for CO2 capture and 163 MWe for hydrogen generation from 78 electrolyser
units, they could produce 24 million litres of fuel per year, for about
$1.78 per litre (Table 1).

For context, a small oil refinery produces about 550 million litres per year
<http://www.dtic.mil/cgi-bin/GetTRDoc?AD=ADA539765>, while Sasol’s South
African coal liquefaction plant, the largest commercial Fischer-Tropsch
plant, produces 8.8 billion litres per year
<http://en.wikipedia.org/wiki/Synfuel>.  To produce the same fuel output as
the Sasol plant the Navy process would require about 73 GW.  So while the
cost per litre may look plausible, the infrastructure required is huge.

*Land based operation and other improvements*

Not everyone has the Navy’s interest in manufacturing at sea.  What if the
process were operated from a land based site?  The largest capital
component in the Navy costing is the floating platform, which adds a huge
$650m to a 200 MWe power plant.  If the platform cost were taken out, the
fuel cost drops to a bargain basement $0.79 per litre, and the carbon
capture cost drops to $37 per tonne!

A nuclear site doesn’t come for free, even on land, so these are lower
limits to the possible costs.  Maybe we should look at current civilian
LCOE nuclear electricity costs.  Nicholson *et al*. reviewed available data
in their 2010 *Energy* paper
<http://www.ecolo.org/documents/documents_in_english/Carbon-pricing-Nicholson-2010.pdf>
and
reported electricity costs for established nuclear power.

Table 1 shows synfuel and carbon capture costs for median and low end
electricity costs for established nuclear power, and for the low end of
current Chinese nuclear builds.  The cheapest Chinese cost gives synfuel at
just $0.82 per litre, and carbon capture at just $39 per tonne.

The other major cost component is hydrogen production by electrolysis,
which is very energy intensive.  There are more efficient ways to do this,
such as using high temperature solid oxide electrolysis cells, or the
sulphur-iodine thermolysis cycle.  These processes operate above 800 °C.  High
temperature gas reactors
<http://en.wikipedia.org/wiki/Very_high_temperature_reactor> could provide
this heat, and an efficient HTGR-SI hydrogen production system would
further reduce the synfuel cost (though not the carbon capture cost).

<https://bravenewclimate.files.wordpress.com/2013/01/sw_table1.png>1. 2012
Annual Energy Outlook
<http://www.eia.gov/forecasts/aeo/electricity_generation.cfm>, US EIA.
2. Australian
Energy Technology Assessment
<http://bree.gov.au/documents/publications/aeta/Australian_Energy_Technology_Assessment.pdf>,
Aust. Govt. Bureau of Resource Economics and Energy 2012.  3. Willauer,
Hardy & Williams
<http://jrse.aip.org/resource/1/jrsebh/v4/i3/p033111_s1?isAuthorized=no>,
Naval Research Laboratory 2012, with minor changes.  4. Nicholson, Biegler
& Brook <http://www.sciencedirect.com/science/article/pii/S036054421000602X>
, *Energy* 2010.

*CCS – Carbon capture at source*

Carbon dioxide can be captured more readily from the flue gases of either
coal or natural gas power plants.  The IPCC estimates carbon capture costs
from these sources as US$15-75 per tonne CO2
<http://www.ipcc.ch/pdf/special-reports/srccs/srccs_summaryforpolicymakers.pdf>.
If we are committed to burning more coal, we might at least use it a second
time before releasing it to the atmosphere.  A coal plant supplying CO2to a
Fischer Tropsch plant collocated with a high temperature gas reactor
producing hydrogen would produce carbon neutral liquid fuel.

The overall carbon accounting for the electricity and synfuel would be
roughly the same as for sequestration, if the synfuel substituted for oil.
It would also avoid the difficult problem of finding a permanent
sequestration solution for the CO2.  Its not negative emissions, but it is
at least emission free.

*Is carbon capture from the ocean worth a carbon credit?*

Does it matter whether CO2 is captured from the ocean or from the
atmosphere?  I’ve assumed not, so long as CO2 is removed from the
biosphere.  Atmospheric CO2 causes global warming, oceanic CO2 causes ocean
acidification.  Both have serious consequences.

But if ocean uptake of CO2 were very slow, burning synfuel derived from
oceanic carbon would be just as bad for the climate as burning fossil
fuels.  If the climate were more sensitive than ocean pH to anthropogenic CO
2, we might prefer to leave the carbon in the oceans.  Would seawater
carbon capture benefit ocean acidity, or climate, or neither?

Table 2 shows the distribution of carbon between air, land and sea over a
recent twenty year period.  Roughly half of our CO2 emissions end up in the
atmosphere, a third in the ocean, and a sixth on land.  There is
substantial equilibration between ocean and air on a timeframe short enough
to be relevant to climate.  There is a complicated tradeoff between marine
and climate impacts of CO2 emissions, but it appears carbon capture from
either reservoir would be beneficial.

<https://bravenewclimate.files.wordpress.com/2013/01/sw_table2.png>From
Table 3.4, *The oceanic sink for carbon dioxide
<http://www.pmel.noaa.gov/pubs/outstand/sabi2854/uptake.shtml>*, Sabine &
Feely 2007

*Conclusion*

We’re not going to be manufacturing the world’s diesel from seawater
anytime soon.  There is a limit to the rate at which we can roll out zero
emission power capacity, nuclear or otherwise, and for a long time the most
environmentally effective application will be to displace coal power, and
gas.  But if we take seriously the need to decarbonise our energy systems,
this will have to happen, most likely by mass production of modular nuclear
reactors.  It would take many decades to build that capability.  But by
then, in a warming world suffering from ocean acidification and hydrocarbon
depletion, zero emission synfuel at $1 per litre, and carbon capture at $40
per tonne would look like a bargain.

Maybe its time to stop talking about carbon capture and storage, and start
talking about carbon capture and synfuel.

*Appendix: Production costs*

The Navy researchers provided a rough costing of an ocean-going nuclear
powered carbon capture and Fischer-Tropsch synthesis plant, and came up
with a fuel cost of production of $1.52 per litre.  They did however
neglect to include the cost of energy for the carbon capture process.  I
constructed a revised cost model that includes the energy for carbon
capture, which I took to be the same as measured by the PARC researchers
for their process (242 kJ mol-1).

The energy and cost of seawater pumping was also not accounted for. I
estimated this as follows.  In a previous paper
<http://www.dtic.mil/cgi-bin/GetTRDoc?AD=ADA544002> on their carbon capture
system the Navy researchers describe their ion exchange unit, and give its
specifications as

Max Flow: 35 cm3s-1

Max Pressure: 350 kPa

So I write *P = QR* where *R* is the hydraulic resistance.  If the max flow
occurs at the max pressure, *R* = 350 kPa/35 cm3s-1 = 1010 Pa s m-3.  The
experimental flow rate was 2.5 cm3s-1.  So I can write power = *PQ* = *Q*2
*R* = 0.0625 W for 2.5 cm3s-1, or 2.5 MW for 100 m3s-1.

This is approximately 1% of total process power, so its a minor component,
and I don’t include it in the cost.

I allowed the carbon capture and Fischer Tropsch plant costs to scale with
production capacity.  Otherwise I have followed the Navy costs and
assumptions, including a cost of capital of 8% pa and annual operation and
maintenance expenses of 5%.  The main line items are given in Table 3.  For
more details, refer to the Navy paper and the spreadsheet.

Some of the Navy capital costs are unsourced and I am unable to verify
them.  These include the cost of the CO2capture and Fischer Tropsch plants,
given as $16m and $140m respectively, per 82 000 gallons per day fuel
output.  I take these values on faith.

The final cost I arrive at is $1.51 per litre, the same as the original
researchers – the increase in assumed power is roughly the power required
to run the carbon capture, so the changes mostly cancel out.  This
spreadsheet was then used to model the alternative scenarios in Table 1.

<https://bravenewclimate.files.wordpress.com/2013/01/sw_table3.png>

———————————–

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