Biogas upgrading – Review of commercial technologies - SGC
Biogas upgrading – Review of commercial technologies - SGC
Biogas upgrading – Review of commercial technologies - SGC
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<strong>SGC</strong> Rapport 2013:270<br />
Only the amine scrubber system has a heat requirement. The heat is required for<br />
reversing the chemical reaction and liberating the CO2. The amount <strong>of</strong> heat depends<br />
to some extent on the inlet methane concentration, but since system heat<br />
loss is constant this effect is to some extent buffered. A typical value for the heat<br />
demand is 0.55 kWh/Nm 3 , which is required in heating the stripper. The heat is<br />
added at 150-120°C and 80% <strong>of</strong> the heat may be reused in low-temperature<br />
(65°C) applications such as substrate pre-heating or AD heating. Catalytic or<br />
thermal oxidation <strong>of</strong> methane in the <strong>of</strong>f-gas from both physical scrubbers, membrane<br />
and PSA can also be used to heat the AD or the substrate as well as the<br />
excess heat from the compressors.<br />
The chemical consumption <strong>of</strong> the water scrubber and amine scrubber is mainly<br />
anti-foaming agents and, in the amine scrubber case, make-up <strong>of</strong> amine. The requirement<br />
is small, with the highest reported by the amine scrubber system<br />
(0.00003 kg/Nm 3 ) with the water scrubber being in the same vicinity. Hydrogen<br />
sulphide removal requires activated charcoal, both for PSA, genosorb, membranes<br />
and amines; there is also an option in the case <strong>of</strong> water scrubbers to use sulphur<br />
removal on the <strong>of</strong>f-gas to meet environmental permits. All <strong>of</strong> the <strong>technologies</strong> have<br />
approximately the same need for lubricant oil for the compressors.<br />
3.3 Methane slip<br />
The methane slip is quite high in the PSA case with 1.8-2% reported as mean and<br />
median values. Higher values are most probably due to temporary technical problems.<br />
The water scrubber has a slip <strong>of</strong> about 1% in modern plants. Values much<br />
higher than this are not probable in a well-functioning plant. Both these <strong>technologies</strong><br />
require tail-end solutions to decrease the methane slip to meet stricter regulations.<br />
This may be done by thermal or catalytic oxidation <strong>of</strong> the methane slip. The<br />
amine scrubber system has a much lower amine slip with 0.1% guaranteed. Organic<br />
physical scrubbers have a higher slip than the other <strong>technologies</strong>, but the<br />
methane is oxidized to supply heat to the process to enable the desorption and<br />
thus it is utilized internally. Membranes also seem to enable operation with a very<br />
low methane slip, about 0.5%, with design (iii) in Figure 15. In some membrane<br />
applications on the market, liquefaction <strong>of</strong> the carbon dioxide in the waste gas is<br />
used to recover 100% <strong>of</strong> the methane in the waste gas by cryogenic separation.<br />
3.4 Investment costs<br />
The investment cost <strong>of</strong> the various <strong>technologies</strong> has been reported earlier in the<br />
text, but in summary the different <strong>upgrading</strong> methods does not differ much; especially<br />
not at higher throughputs. The specific investment costs are shown together<br />
in Figure 31.<br />
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