SORBENT COATED CARBON FIBERS AND THEIR MODULES FOR REDUCING CARBON DIOXIDE USING ELECTRICALLY DRIVEN TEMPERATURE SWING ADSORPTION SYSTEM
20250276279 ยท 2025-09-04
Inventors
- Ryan P. Lively (Atlanta, GA, US)
- Sayan Banerjee (Fremont, CA, US)
- Christopher W. Jones (Atlanta, GA)
- Won Hea Lee (Atlanta, GA, US)
- Matthew J. Realff (Atlanta, GA, US)
- Xin Zhang (Atlanta, GA, US)
Cpc classification
B01D53/0462
PERFORMING OPERATIONS; TRANSPORTING
B01J20/3204
PERFORMING OPERATIONS; TRANSPORTING
B01D2253/25
PERFORMING OPERATIONS; TRANSPORTING
B01D2259/40007
PERFORMING OPERATIONS; TRANSPORTING
B01J20/26
PERFORMING OPERATIONS; TRANSPORTING
International classification
B01J20/32
PERFORMING OPERATIONS; TRANSPORTING
Abstract
The present disclosure relates to relates to sorbent coated carbon fibers, modules containing the same, and their use in reducing carbon dioxide levels via direct air capture.
Claims
1. A carbon dioxide (CO.sub.2) capture material, the material comprising: a carbon-containing fiber; and a CO.sub.2 adsorptive material coating the carbon-containing fiber.
2. The CO.sub.2 adsorptive material of claim 1, wherein the carbon-containing fiber is a carbon fiber.
3. The CO.sub.2 adsorptive material of claim 2, wherein the carbon fiber is any one of a polymer-derived carbon fiber, an activated carbon fiber, a multi-walled carbon nanotube fiber, a single-walled carbon nanotube fiber, or a silicon carbide fiber.
4. The CO.sub.2 adsorptive material of claim 1, wherein the CO.sub.2 adsorptive material comprises a porous support and an adsorbent material.
5. The CO.sub.2 adsorptive material of claim 4, wherein the porous support is mesoporous.
6. The CO.sub.2 adsorptive material of claim 4, wherein the porous support is a porous silica, a porous alumina, a porous aluminosilicate, a metal-organic framework, a zeolite, a zeolitic imidazole framework, or a covalent organic framework.
7. The CO.sub.2 adsorptive material of claim 4, wherein the adsorbent material is an amine-based adsorbent.
8. The CO.sub.2 adsorptive material of claim 4, wherein the adsorbent material is any one of a poly(ethyleneimine), diethylenetriamine, an aminopropyl organosilane, tetraethylenepentamine, ethylenediamine, N,N-dimethylethylenediamine, a poly(allylamine), a diethylenetriamino organosilane, a polyaziridine, a methylaminopropyl organosilane, or an ethylenediamine organosilane.)
9. The CO.sub.2 adsorptive material of claim 4, wherein the CO.sub.2 adsorptive material comprises a polymeric material.
10. The CO.sub.2 adsorptive material of claim 9, wherein the polymeric material is any one of cellulose, cellulose acetate, a polyimide, a polyamide, a polyetherimide, a polyamide-imide, a polymer of intrinsic microporosity, a polysulfone, a polyethersulfone, or a polyvinylidene fluoride.
11. A carbon dioxide (CO.sub.2) capture module comprising a CO.sub.2 capture material according to claim 1.
12. The module of claim 11, wherein the module is a direct air capture (DAC) module.
13. The module of claim 11, wherein the module is a wind energy direct air capture (WEDAC) module.
14. The module of claim 13, wherein the module is configured to transition between an open configuration and a closed configuration, wherein in the open configuration, the CO.sub.2 adsorptive material is open to an external environment for adsorption of CO.sub.2 from air in the external environment onto the CO.sub.2 adsorbtive material, and in the closed configuration, the CO.sub.2 adsorptive material is isolated from the external environment for controlled desorption of the CO.sub.2 from the CO.sub.2 adsorptive material.
15. The module of claim 14, wherein the controlled desorption is vacuum-assisted and electrothermal.
16. A method removing CO.sub.2 from a mixture of gases comprising: transmitting the mixture of gases across a surface of a CO.sub.2 capture material according to claim 1, and removing CO.sub.2 from the mixture of gases by adsorption of the CO.sub.2 on the surface of the CO.sub.2 capture material.
17. A method removing CO.sub.2 from a mixture of gases comprising: transmitting the mixture of gases through a CO.sub.2 capture module according to claim 11. and removing CO.sub.2 from the mixture of gases by adsorption of the CO.sub.2 on the surface of the CO.sub.2 capture material.
18. The CO.sub.2 adsorptive material of claim 2, wherein the CO.sub.2 adsorptive material comprises a porous support and an adsorbent material.
19. The CO.sub.2 adsorptive material of claim 3, wherein the CO.sub.2 adsorptive material comprises a porous support and an adsorbent material.
20. The CO.sub.2 adsorptive material of claim 5, wherein the adsorbent material is an amine-based adsorbent.
Description
BRIEF DESCRIPTION OF THE DRAWINGS
[0028]
[0029]
[0030]
[0031]
[0032]
[0033]
[0034]
[0035]
[0036]
[0037]
[0038]
[0039]
[0040]
[0041]
[0042]
[0043]
[0044]
[0045]
[0046]
[0047]
[0048]
[0049]
[0050]
[0051]
[0052]
[0053]
[0054]
[0055]
[0056]
[0057]
[0058]
[0059]
[0060]
[0061]
DETAILED DESCRIPTION OF THE INVENTION
[0062] In this invention, carbon fibers were coated with mesoporous silica (SYLOID C-803) and cellulose acetate (CA) using a roll-to-roll coating system and then impregnated with poly(ethyleneimine) (PEI) within the coating layer. A fibrous configuration for the DAC modules was chosen for scalable CO.sub.2 sorbent fabrication. The electrothermal properties and CO.sub.2 adsorption capacity of the sorbent-coated carbon fibers were investigated. Fabricated modules with the sorbent-coated carbon fibers were then prepared for use in DAC-relevant experiments. The CO.sub.2 adsorption performance of the modules was measured in the ETSA system under various DAC-relevant conditions. The effects of vacuum, purge flow rate, and humidity on the ETSA performance of the DAC modules were demonstrated. The ability to achieve reasonable CO.sub.2 capacities in these systems as well as enable rapid thermal cycles via the usage of Joule heating has been demonstrated.
Sorbent-Coated Carbon Fibers From Dip-Coating
[0063] Carbon fibers were initially coated by hand using a dip-coating technique (see Examples). The hand coated carbon fibers were observed to have a uniform white solid surface and exhibited good sorbent dope adhesion to the carbon fiber tow (
Electrical Properties and Joule Heating of the Sorbent-Coated Carbon Fibers
[0064] The effect of the length and the number of the carbon fibers on their electrical properties and Joule heating behavior was studied. All the carbon fibers, regardless of length and number of fibers in the module, were observed to follow Ohm's law (V=I.Math.R, where V is voltage, I is current, and R is resistance) at the low voltage, i.e., a linear relationship between electric current and potential was exhibited (
[0065] The temperature of the carbon fibers was observed to increase non-linearly with increasing electric potential (
[0066] Joule heating has also been explored for the sorbent-coated carbon fibers (
[0067] Furthermore, the temperature change of the fibers by Joule heating was monitored over time since rapid temperature control is an essential part of the ETSA process (
CO.SUB.2 .Adsorption Properties of the Coating Layer
[0068] CO.sub.2 adsorption behavior of the PEI-loaded CA/C803 outer layer peeled off the sorbent-coated carbon fibers. PEI impregnation was conducted for 12 hours at three different PEI concentrations: 5, 10, and 20 wt. % of PEI in methanol. This was done to identify advantaged PEI concentrations that resulted in reasonable CO.sub.2 uptakes under 400 ppm CO.sub.2 conditions.
[0069] PEI loadings on the sorbent layer increased with increasing PEI concentration, in which the coating layer prepared from 5, 10, and 20 wt % solution impregnation for 12 h exhibited 0.55, 1.04, and 1.59 g.sub.PEI/g.sub.coating, respectively (
[0070] Exploratory TGA experiments using pure CO.sub.2 at 30 C. were found to show typical non-Fickian CO.sub.2 uptakes regardless of the PEI impregnation conditions (
[0071] Cyclic adsorption/desorption experiments were conducted on the PEI-loaded sorbent layer under 100 sccm of 400 ppm CO.sub.2 to better understand the cyclic stability of these materials. Ten cycles were repeated with the adsorption at 30 C. for two hours and the desorption at 110 C. for an hour under flowing 400 ppm CO.sub.2 conditions (
Electrically-Driven Temperature Swing Adsorption of the Sorbent-Coated Carbon Fiber Modules for DAC
ETSA vs. TSA
[0072] Breakthrough experiments were conducted on DAC fiber modules to compare CO.sub.2 adsorption and desorption from TSA (
TABLE-US-00001 TABLE 1 Breakthrough Conditions and Results of the DAC Module Feed CO.sub.2 capacity CO.sub.2 level Flow rate q.sub.b q.sub.pe Adsorption (ppm) Balance gas (sccm) (mmol CO.sub.2/g.sub.fiber) Inert dry 400 N.sub.2 50 0.30 0.35 400 N.sub.2 100 0.30 0.39 400 N.sub.2 200 0.29 0.45 Dry 400 Air 100 0.28 0.40 Wet 400 Air 100 0.15 1.00 Pre-hydrated 400 Air 100 0.88 1.21 q.sub.b: breakthrough capacity, q.sub.pe: pseudo-equilibrium capacity
[0073] In the following ETSA cycle, the breakthrough curve of Adsorption 2 was the same as Adsorption 1, demonstrating that the adsorbed CO.sub.2 was completely regenerated during the first thermal desorption without any thermal degradations. The electrothermal desorption was conducted by applying 7 V and 1 A to the module. It showed a narrow CO.sub.2 concentration peak in a six-fold shorter time than the thermal desorption. We note that the area of the CO.sub.2 desorption curve from TSA was similar to that from ETSA, indicating the electrothermal desorption also completely removed the adsorbed CO.sub.2. It is estimated, based on these measurements, that 95% of CO.sub.2 was regenerated from 2.5 g of the sorbent-coated carbon fibers in 10 minutes by ETSA, while TSA with external heat applied by a heating tape needed 1 hour for the same fractional desorption (
[0074] Moreover, it was observed that the outer surface of the module was heated to only 50 C. during the electrothermal desorption (
Electrothermal Desorption of the Module Under Various DAC Conditions
[0075] ETSA cycles were conducted on the DAC modules with different feed and purge flow rates of 50, 100, and 200 sccm (
[0076] The ETSA processes were further investigated under simulated ambient conditions to explore the feasibility of the modules in more practical DAC environments. For that, simulated air (21% O.sub.2/79% N.sub.2) containing 400 ppm CO.sub.2 was used as the feed gas, replacing the nitrogen-balanced one, and the humidity was also controlled by flowing the inlet gas through a water bath before the module (
[0077] However, the presence of water vapor in the feed (99% RH) had a significant effect on the CO.sub.2 adsorption behavior. In the wet adsorption, where the CO.sub.2 and water vapor simultaneously flowed into a dry module, both water and CO.sub.2 showed breakthrough curves (
[0078] Lastly, the module was pre-hydrated with humid argon (99% RH) before the wet CO.sub.2/Air feed (
[0079] In this invention, sorbent-coated carbon fibers were prepared by roll-to-roll coating carbon fibers with CA/silica followed by PEI impregnation. The resulting fibers showed dual-layered structures in which carbon fibers at the core were uniformly covered with porous sorbent coating layers. The sorbent-coated carbon fibers exhibited rapid Joule heating behavior, driven by modest 7 V electric potentials, reaching CO.sub.2 desorption temperatures (80-120 C.) within a minute. The sorbent coating layer, when removed from the fiber, showed stable adsorption/desorption cyclic performance with constant CO.sub.2 uptake of 0.480.02 mmol/g under 400 ppm CO.sub.2. DAC modules were fabricated with the sorbent-coated carbon fibers and they showed CO.sub.2 breakthrough capacities of 0.30 and 0.88 mmol/g.sub.fiber in dry and pre-hydrated adsorption conditions, respectively. Approximately 95% of the adsorbed CO.sub.2 was obtained ruing regeneration in <10 min/g.sub.fiber by electrothermal desorption, which was six times faster than thermal desorption. The module surface temperature did not exceed 50 C. during Joule heating of the fibers to 110 C., indicating efficient heat management during the electrothermal desorption and potentially reducing cooling energy. The vacuum-electrothermal desorption exhibited a more intensive CO.sub.2 concentration peak and less increased module surface temperature compared to the electrothermal desorption. In addition, when CO.sub.2 was adsorbed in humid conditions, asymptotic CO.sub.2 desorption peaks with long tails were observed from the electrothermal desorption, likely due to the CO.sub.2 reacting with the adsorbed water. Overall, efficient ESA performance of the sorbent-coated carbon fiber modules was demonstrated by the breakthrough system under various DAC conditions400 ppm CO.sub.2 with different feed flow rates, balance gases, and humidity.
[0080] Table 2 lists exemplary, but non-limiting, components that may be used to prepare the fibers and modules described herein.
TABLE-US-00002 TABLE 2 Electrically Conductive Layer Core CO.sub.2 Adsorptive Coat Component Carbon Fiber Polymer Porous Adsorbent Additive (Support for Adsorbent) General Any commercial Any soluble Any A mine-based adsorbent Material or synthesized polymers mesoporous carbonaceous material fiber (CF) (pore diameters of 2-50 nm) Non- Polyacrylonitrile Cellulose Silica Poly(ethyleneimine) Limiting (PAN) CF (commercial, (PEI) Examples C803, SBA - 15, MCM - 41, fumed) Activated CF Cellulose Alumina (- Diethylenetriamine acetate (CA) alumina) (DETA) Multi-walled Polyimide (PI) Silica A minopropyl Carbon Mesocellular organosilanes (APS) nanotube fiber Foam (MCF) Single-Walled Polyamide (PA) Metal- Tetraethylenepentamine Carbon Organic (TEPA) nanotube fiber Frameworks (MOF) Silicon carbide Polysulfone Zeolite Ethylenediamine (EN) fiber (PSf) Polyethersulfone Zeolitic N,N- (PES) Imidazole dimethylethylenediamine Frameworks (MMEN) (ZIF) Polyvinylidene Covalent Poly(allylamine) (PAA) fluoride (PVDF) Organic Frameworks (COF) diethylenetriamino organosilanes (DT) aziridine in situ polymerization (AZ) methylaminopropyl organosilanes (MAP) ethylenediamine organosilanes (ED)
EXAMPLES
Materials
[0081] A roll of carbon fiber tow (UT-CF-3K, 4.4 lb) was obtained from ACP Composite Inc. (Livermore, CA, USA) for Joule heating media. Cellulose acetate (MW 50,000 Da, Sigma-Aldrich Inc.), mesoporous silica (SYLOID C-803, Grace Davison Inc.), and poly(vinylpyrrolidone) (MW 40,000 Da, Sigma-Aldrich Inc.) were thoroughly dried at 110 C. for at least 12 hours in vacuum oven before the coating dope preparation. Branched poly(ethylenimine) (PEI, MW 800) was purchased from Sigma-Aldrich for CO.sub.2 adsorbent impregnated on the silica coating layer. N-Methyl-2-pyrrolidone (NMP, Reagent Plus, 99%) was obtained from Sigma-Aldrich, and methanol (ACS Reagent, 99.8%) and n-hexane (ACS Reagent, >98.5%) were purchased from VWR.
Preparation of Sorbent-Coated Carbon Fibers
[0082] The sorbent-coated carbon fibers were fabricated by dip-coating the neat carbon fibers into a silica-containing polymer dope. The coating dope was prepared following previous formulations used to spin sorbent fiber.sup.33,34 but with a different optimized composition for dip-coating methods (Table 3). A prime dope and a silica dispersion mixture were made separately and mixed together to obtain the coating dope. For the prime dope preparation, 5.22 g of cellulose acetate (CA) was dissolved into 75.8 g of N-methylpyrrolidone (NMP) and 31.2 g of deionized (DI) water, and the mixture was kept on a roller under an IR lamp until a homogeneous solution was formed. For the silica dispersion mixture, 19 g of C803 mesoporous silica was added into 202.2 g of NMP and 83.5 g of DI water, and the mixture was mechanically stirred for three hours. The dispersion was further homogenized with a probe sonifier (Branson 250) for an additional hour. The 74.9 g of the prime dope was added to the silica dispersion mixture, followed by 13.9 g of CA and 6.4 g of poly(vinylpyrrolidone) (PVP). The system was vigorously stirred for another three hours and kept on the roller with heat overnight. The obtained dope for carbon fiber dip-coating was a viscous and foggy white dispersion.
TABLE-US-00003 TABLE 3 Dope Composition for Carbon Fiber Dip-Coating Composition (wt. %) CA PVP C 803 NMP DI 4.3 1.6 4.7 63.2 26.1
[0083] Hand dip-coating was conducted on the carbon fibers for preliminary examination of the coating dope properties (e.g., adhesion, thickness, drying rate). Approximately 10 cm of carbon fibers were completely immersed in the coating dope and pulled out slowly with tweezers, and excessive solution at the fiber surface was gently removed. The wet carbon strands were soaked into a DI water bath to induce phase inversion of the silica-loaded dope. The sorbent-coated carbon fiber was stored in fresh DI water for three days to complete the phase inversion, followed by continuous solvent exchange with methanol and n-hexane for three hours each, then air drying.
Impregnation of Poly(Ethyleneimine) in the Sorbent-Coated Carbon Fibers
[0084] PEI impregnation in the sorbent-coated carbon fibers was conducted following the post-spinning PEI infusion methods described by Labreche et al. (Post-spinning infusion of poly (ethyleneimine) into polymer/silica hollow fiber sorbents for carbon dioxide capture. Chemical engineering journal 221, 166-175, 2013). First, the sorbent-coated carbon fibers were soaked in methanol to fill the pores at the coating layers. Then the pre-saturated fibers were transferred to PEI/MeOH solution and kept for 12 hours to complete PEI impregnation. The PEI concentration was varied between 5-20 wt. %, and the total amount of PEI in the solution was set to be more than ten times over the total weight of C803 in the fibers to minimize concentration change during the PEI loading. After the impregnation, the PEI-loaded fibers were washed with hexane to remove the unloaded PEI, followed by 1-hour air drying and 2-hour vacuum drying at 100 C.
Joule Heating of the Sorbent-Coated Carbon Fibers
[0085] Direct current (DC) voltage was applied by a DC power supply (30 V 10A) to the carbon fibers or the sorbent-coated carbon fibers to measure the electric resistance and Joule heating temperature. The carbon fibers were cut into specific lengths, and both ends were connected to the power supply with alligator clips. The surface temperature was measured by a calibrated thermal imager (ACEGMET, IP65). The electric potential was strictly controlled to not allow the fiber surface temperature to exceed 300 C. The Joule heating temperature under constant DC voltage was measured after the fiber held its peak point for more than 30 seconds. Additionally, the effect of the configuration of the carbon fibers on Joule heating behavior was investigated with different fiber lengths and number of fibers.
Characterization
[0086] A field-emission scanning electron microscopy (FE-SEM, Hitachi 8010) was used to observe the morphologies of sorbent-coated carbon fibers. The fiber samples were cut in liquid nitrogen for cross-sectional SEM images. All the samples were coated with gold particles for 30 seconds using a Hummer 6 sputter coater.
[0087] Thermogravimetry analysis (TGA) was utilized to investigate CO.sub.2 uptake and cyclic adsorption/desorption stability of the PEI-loaded coating layers. Specifically, TGA Q-500 (TA Instruments, DE, USA) was used for adsorption capacities under pure CO.sub.2 at 30 C. The sorbent layer sample was mechanically delaminated from the sorbent-coated carbon fibers by hand and subsequently activated at 110 C. for 2 hours under a flowing nitrogen atmosphere at a 10 C./min heating rate. Then, the sample was equilibrated to 30 C. with a 20 C./min cooling rate. The sample gas flow was changed to 50 sccm of pure CO.sub.2 for 2 hours while the mass changes of the samples were monitored.
[0088] TGA Q-550 (TA Instruments) with a CO.sub.2/H.sub.2O analyzer (LI-850, Li-Cor, NE, USA) was used for gas uptake and cyclic adsorption/desorption under 400 ppm CO.sub.2. For the 400 ppm CO.sub.2 adsorption uptake experiments, the sorbent layer was activated at 110 C. under a nitrogen atmosphere until the CO.sub.2 level in the Li-Cor detector went below 10 ppm, followed by flowing 400 ppm CO.sub.2 in N.sub.2 for 24 hours at 30 C. For cyclic stability, ten cycles of adsorption/desorption were conducted under the 400 ppm CO.sub.2 condition, where adsorption and desorption temperatures were 30 C. and 110 C., respectively. The CO.sub.2 level at steady state, however, was 50 ppm lower than the feed concentration (400 ppm). We speculate this difference was from both or either the CO.sub.2 detection error and/or CO.sub.2 concentration error of the gas cylinder. However, as a 400 ppm CO.sub.2 cylinder was used for both the sample and balance purge during adsorption, the sample was under the same gas composition of the cylinder we used.
Fabrication of DAC Modules
[0089] The DAC modules for carbon capture applications were made of a sorbent-coated carbon fiber bundle. After PEI impregnation, the fibers were cut into 11 inch segments, and one inch of the sorbent coating layers were peeled off from both ends of the fiber to expose conductive carbon. Then, 3-6 strands of the fibers were collected, and the carbon ends of the bundle were tied with copper wires (
Roll-to-Roll Coating of the Carbon Fibers
[0090] Carbon fiber dip-coating has been scaled using a roll-to-roll coating system 1000 as illustrated in
where the weight faction of the sorbent layer (w.sub.s) was calculated from the mass of the sorbent-coated carbon fiber (m.sub.sc) and the carbon fiber (m.sub.c).
Dynamic Gas Adsorption and Desorption
[0091] Dynamic gas adsorption/desorption tests were conducted using a lab-made breakthrough apparatus (
Adsorption
[0092] Before the initial breakthrough measurements, the module was activated at 110 C. flowing 100 sccm of dry argon to desorb the pre-adsorbed gases until N.sub.2, O.sub.2, H.sub.2O, and CO.sub.2 signals became stable at the minimum. Then, the heat was turned off, and the system was cooled to room temperature using an auxiliary fan blowing on the exterior of the module. In this study, three different adsorption modes were operated subject to humidity controls: (i) dry adsorption, (ii) wet adsorption, and (iii) pre-hydrated adsorption. For the dry adsorption, the nitrogen or air containing 400 ppm CO.sub.2 directly flowed into the shell side of the module maintaining dry (0% RH) system. On the other hand, for the wet adsorption, the feed gas passed through the saturator prior to the module, providing 99% RH flow. In the pre-hydrated adsorption, the module was pre-saturated with water by flowing humid argon, followed by the adsorption stage with wet 400 ppm CO.sub.2. When applying humid flows into the module, the feed gas flowed through the water bath at least 10 minutes after humidity reached 99% to pre-saturate the feed flow and the water bath and then connected to the module.
[0093] Breakthrough capacity (q.sub.b, mmol/g) and pseudo-equilibrium capacity (q.sub.pe, mmol/g) was calculated from the integrated areas of the breakthrough curves until the normalized CO.sub.2 concentration (C/C.sub.0) reaches 0.05 and 0.95, respectively, following Equations 2A and 2B.
where V.sub.m (cm.sup.3(STP)mol.sup.1) and M(g) indicate the molar volume and sample weight, and t.sub.b (min) and t.sub.0.95 (min) are adsorption time for breakthrough and pseudo-equilibrium, respectively.
Desorption
[0094] Once the breakthrough curves reached adsorption equilibrium, three different desorption conditions were evaluated: (i) externally-driven thermal desorption, (ii) electrothermal desorption, and (iii) vacuum-electrothermal desorption, which correspond to TSA, ETSA, and VETSA system, respectively.
Externally-Driven Thermal Desorption
[0095] The module was covered by heating tape and aluminum foil to minimize heat losses (
Electrothermal Desorption
[0096] The copper wires from the module were connected to the DC power supply (
Vacuum-Electrothermal Desorption
[0097] The module was isolated from the feed gas by closing the ball valves at the inlet and outlet, and the needle valve between the module and the vacuum pump opened. The pump pulled the vacuum for 10 s and disconnected from the module (
Wind Energy DAC (WEDAC) Modules
[0098] In this example, the DAC modules described above were scaled up 20to capture the CO.sub.2 from ambient air in a WEDAC process. 120 sorbent-coated carbon fibers (each 30 cm in length) were vertically aligned inside a removable vacuum casing. The fibers were individually separated from the center support structure. The modules had 6 g of sorbent-coated carbon fibers. The vacuum case was made of two rubber covers and a 630 cm clear acrylic tube. The rubber covers enveloped the acrylic tube, sealing the inner space of the cylinder.
[0099] All fibers were observed to exhibit approximately uniform Joule heating behavior, reaching the desorption temperature at 5 V in 3 min.
[0100] A WEDAC experimental setup was implemented for ETSA operation. In an open and windless space (a laboratory), the module stood vertically at a specific distance from the fan. The bottom of the adsorption body was connected to an electric power supply. The top of the vacuum case was continuously linked to a micropump (DC 12 V 12 W, micro diaphragm pump air compressor, max. 75 kPa, 12 LPM) and gas sampling bag. The WEDAC process consists of adsorption/desorption cycles. For the ambient air CO.sub.2 adsorption, the module in the open configuration, and the fan blew air across the laboratory towards the fibers at a controlled wind speed and blowing time. After a period of time, the WEDAC module was converted to the closed configuration by enclosing the fibers within the vacuum case, residual air was pumped out, and then an electric potential was applied on the module with the vacuum for desorption. The vacuum level was 0.3 bar. Then, 5 V of electric potential was applied to the module for the electrothermal desorption. Once the gas sampling bag stopped being inflated, the power was turned off and module was cooled. Then, the gas bag was replaced, the pump was turned off, and the module was returned to the open configuration for a subsequent adsorption step. The CO.sub.2 purity in the gas sampling bag was measured by a CO.sub.2 analyzer (Model 906, Quantek Instrument, MA, USA).
[0101] For adsorption, fan-generated wind was blown through the module at a wind speed of 3 m/s, where the wind speed ratio at the front and back of the module was observed to be 0.21 (i.e., the average air velocity within the module is at least 21% of the windward side air velocity). These modules were electrothermally regenerated with a weak vacuum pump (i.e., no flowing inert gases). These prototype modules were able to generate a 81.5 mol % concentrated CO.sub.2 product without dilution from the ambient air (<400 ppm CO.sub.2) in 10 min of Joule heating under a 0.3 bar vacuum in the laboratory.
[0102]
Techno-Economic Analysis of a Pilot-Scale WEDAC System
[0103] A passive wind-driven cylindrical contactor with a diameter of 6 cm and a height of 1 m was studied. The contactor was uniformly filled with PEI-coated carbon fibers. This system could be set in a moderately windy location (wind speed is assumed to be 3 m/s) for adsorption. Joule heating from external power supply with the aid of vacuum was implemented during desorption process. An insulation coat was implemented during desorption to reduce the convective heat loss to the surroundings by convection from the surface of the cylinder. After desorption, the system was cooled down in natural wind where it is assumed the insulation can be withdrawn but the system is still sealed by a thin impermeable fabric. A full cycle includes adsorption, desorption, and cooling processes. The detailed parameters used in this TEA analysis are listed in Table 4.
TABLE-US-00004 Parameter Symbol Value Unit Contactor installation cost C.sub.c 60 $/kg.sub.contactor Heat capacity of CO2 C.sub.p, g 849 J /(kg .Math. C.) Heat capacity of contactor C.sub.p, s 1100 J /(kg .Math. C.) solid Sorbent dope's cost C.sub.s 2 $/kg Vacuum pump purchase cost C.sub.v 125 $ Wind power cost C.sub.wind 0.03 $/kWh Contactor diameter D.sub.c 6 cm Fiber diameter D.sub.f 1 mm Contactor porosity .sub.c 0.909 Joule heating input during E.sub.joule 7.2 (ETSA)/75.7 GJ tCO.sub.2.sup.1 desorption (External heating Bare module factor fbm 3.05 CO2 adsorption heat H.sub.ads 65.6 kJ/mol Contactor height H.sub.c 1 m Contactor material's lifetime L.sub.c 10 yr Sorbent lifetime L.sub.s 0.5 yr Vacuum pump's lifetime L.sub.v 10 yr Contactor mass M.sub.c 0.35 kg Number of contactors N 15 (ETSA)/3 (External sharing a vacuum pump heating) Cycles per year N.sub.cycle/yr 8375 (ETSA)/5677 (External heating) Vacuum pump efficiency 50 % Ambient pressure P 1 atm Vacuum degree during P.sub.0 0.05 atm desorption CO2 annual productivity Pr.sub.a 0.2 (ETSA)/0.08 tCO.sub.2/(kg .Math. yr) (External heating) Swing capacity q.sub.w 0.54 (ETSA)/0.32 mol/kg.sub.contactor (External heating) Adiabatic compression factor 1.3 of CO2 Desorption time per cycle t.sub.des/cycle 10 (ETSA)/600 (External sec heating) Temperature difference T 110 (ETSA)/100 C. between desorption and (External heating) adsorption Desorption temperature T.sub.des 140 (ETSA)/130 C. (External heating) Wind speed U.sub.0 3 m/s Weight ratio of pure fibers W.sub.c 0.5 over coated fibers Weight ratio of pure fibers W.sub.s 0.5 over coated fibers
[0104] The overall cost of the DAC system includes capital costs, fixed operating and maintenance costs, and variable operating and maintenance costs. The capital costs included contactor capital cost, vacuum pump capital cost, and indirect capital costs. Fixed operating and maintenance costs were assumed to be 5% of the total capital cost. Variable operating and maintenance costs include sorbent operating cost, Joule heating operating cost and vacuum pump operating cost, which is mostly the cost of electricity for the latter two components. The contactor capital cost is given by Equation (3):
where C.sub.c ($) represents the installation cost of the contactor, including material cost and infrastructure cost related to contactor base, shell, and carbon fibers, and was estimated to be 60 $/kg.sub.contactor; w.sub.c represents the weight ratio of the carbon fibers over the coated fibers, and was estimated to be 0.5; L.sub.c (yr) represented the lifetime of the contactor materials, and was estimated to be 10 years; and Pr.sub.a (tCO.sub.2/(kg.Math.yr)) was the annual productivity of DAC system, and was estimated based on the simulated cycle behaviors using a 2 d computational fluid dynamic (CFD) model and a 2 d process model under given operating conditions.
[0105] Vacuum pump capital cost is given by Equation (4):
where fbm represented the bare module factor of the vacuum pump; C.sub.v ($) represents the purchasing cost of vacuum pump, which was determined by the system size, vacuum degree and maximum flow rate; N represents the number of contactors sharing the vacuum pump, considering the ratio of adsorption and cooling periods over desorption period was larger than four at most operating conditions, N was set to be 5; L.sub.v (yr) represents the lifetime of the vacuum pump, and was estimated to be 10 years; and M.sub.c (kg) represents the mass of the contactor, which was estimated 0.909.
[0106] Indirect capital cost is related to the annual production of a plant and the energy input per ton CO.sub.2. Assuming our DAC system could capture 1 million ton CO.sub.2 per year, the indirect cost was estimated to be 30 $/tCO.sub.2.
[0107] Sorbent operating cost is given by Equation (5):
where C.sub.s ($/kg) represents the sorbent dope material cost, and was estimated to be 2 $/kg.sub.contactor; w.sub.s represents the mass ratio of the sorbent over the coated fibers, and L.sub.s (yr) represents the lifetime of the sorbent, and was estimated to be 0.5 years.
[0108] Vacuum pump operating cost is given by Equations (6A-D) assuming adiabatic compression:
where P (atm) represents the ambient pressure, 1 atm; P.sub.0 (atm) represents the vacuum degree during desorption, which was 0.05 atm; V (m.sup.3) represents the volume of the extracted CO.sub.2 at 1 atm; V.sub.0 (m.sup.3) represents the volume of the extracted CO.sub.2 at P.sub.0, and was calculated based on the transient desorption rate of CO.sub.2 (Equations 7C and D); represents the adiabatic compression factor of CO.sub.2 , and was estimated to be 1.3; represents the pump efficiency, and was assumed to be 50%; N.sub.cycle/yr represents the operating cycles per year; t.sub.des/cycle (hr) represented the desorption time per cycle; C.sub.wind ($/Wh) represents the cost of wind power, which was assumed to be 0.03 $/kWh; T.sub.des ( C.) represents the average temperature of the fibers during desorption; R represents the gas constant; and q.sub.w (mol/kg) represents the swing capacity per cycle.
[0109] Joule heating operating cost is given by Equation (7A):
where E.sub.Joule (GJ tCO.sub.2.sup.1) represents the Joule heating input during desorption for capturing one ton of CO.sub.2. Joule heating input energy was converted to four parts, including CO.sub.2 desorption heat (Equation 7B), CO.sub.2 sensible heat (Equation 7C), contactor sensible heat (Equation 7D) and forced convective heat loss from the surface of the device during desorption (the remaining heat):
where H.sub.ads (kJ/mol) represented the adsorption heat of CO.sub.2 onto PEI loaded carbon fibers, 65.6 kJ/mol; M.sub.w,CO2 (kg/mol) represented the molar mass of CO.sub.2; C.sub.p,g (J/(kg.Math. C.)) represented the heat capacity of CO.sub.2, 849 J/(kg.Math. C.); T ( C) represents the temperature difference between desorption and adsorption processes; and C.sub.p,s (J/(kg.Math. C.)) represents the heat capacity of the contactor, 1100 J/(kg.Math. C.).
[0110] A techno-economic analysis of a pilot-scale WEDAC system was conducted by considering a comparison between direct and indirect ETSA (direct ETSA refers to heating the carbon fiber cores, while indirect ETSA refers to heating the contactor surface, both with electric energy) with either wind power (0.03 $ kWh.sup.1) or US grid power (0.06 $ kWh.sup.1). The overall cost includes capital costs (capex) of the contactor; vacuum pump and indirect cost; fixed operating and maintenance cost (fixed O&M ex); and variable operating costs (opex) of the sorbent, vacuum pump, and Joule heating. In general, Joule heating opex was the major contributor of the overall cost, followed by vacuum pump capex. The overall cost was projected to be approximately 160 $ tCO.sub.2.sup.1 with direct ETSA driven by renewable electricity (we assumed wind energy in our analysis as co-location of the DAC module and a wind turbine is likely advantageous). The energy consumption of the ETSA process is dominated by the Joule heating energy input during desorption, which is expected to be approximately 7.2 GJ tCO.sub.2.sup.1 for a full-scale process, given a cycle capacity of 0.54 mol CO.sub.2/kg contactor (1.08 mol CO.sub.2/kg sorbent). Our analysis of the Joule heating energy usage (
Experimental Conclusions
[0111] Herein, we demonstrate the feasibility and scalability of ETSA for the DAC system with data from a lab-made DAC system. We explored the application of ETSA to DAC by creating ETSA fiber materials and DAC modules. We have included testing data on an ETSA WEDAC module that is designed to operate in the presence of wind instead of with fans. We also include a techno-economic analysis on this concept to highlight a potential path forward to low-cost DAC. The sorbent-coated carbon fibers were prepared by roll-to-roll coating carbon fibers with CA/silica followed by PEI impregnation. The resulting fibers showed dual-layered structures in which carbon fibers at the core were uniformly covered with porous sorbent coating layers. The sorbent-coated carbon fibers exhibited rapid Joule heating behavior, driven by modest 7 V electric potentials, reaching CO.sub.2 desorption temperatures (80-120 C.) within a minute. The sorbent coating layer, when removed from the fiber, showed stable adsorption/desorption cyclic performance with constant CO.sub.2 uptake of 0.480.02 mmol/g under 400 ppm CO.sub.2.
[0112] DAC modules were fabricated with the sorbent-coated carbon fibers, and they showed CO.sub.2 breakthrough capacities of about 0.30 and about 0.88 mmol/g.sub.fiber in dry and pre-hydrated adsorption conditions, respectively. Approximately 95% of the adsorbed CO.sub.2 was obtained during regeneration in <10 min by electrothermal desorption, which was six times faster than external, indirect thermal desorption. The module surface temperature did not exceed 50 C. during Joule heating of the fibers to about 110 C., indicating efficient heat management during the electrothermal desorption and thus potentially reducing cooling times. The vacuum-electrothermal desorption exhibited a more intensive CO.sub.2 concentration peak and less increased module surface temperature compared with the flowing gas electrothermal desorption. In addition, when CO.sub.2 was adsorbed in humid conditions, asymptotic CO.sub.2 desorption peaks with long tails were observed from the electrothermal desorption, likely due to the CO.sub.2 reacting with the adsorbed water. Overall, efficient ETSA performance of the sorbent-coated carbon fiber modules was demonstrated by the breakthrough system under various DAC conditions 400 ppm CO.sub.2 with different feed flow rates, balance gases, and humidity.
[0113] We created DAC modules with a 20 scale-up factor compared with our laboratory devices. These scaled-up DAC modules contain 120 sorbent-coated carbon fibers and can operate without fans in windy environments. The modules adsorbed CO.sub.2 from the ambient air and regenerated concentrated CO.sub.2 by vacuum-assisted electrothermal desorption at productivities and purities (80%-85 mol % CO.sub.2) that are consistent with what we expect based on our fundamental measurements of the coated carbon fiber performance. Importantly, the sorbent-coated carbon fibers were made of all industrial products, including carbon fibers, sorbents, polymers, and silicas, highlighting the potential for shorter commercialization times relative to more exotic materials. Future implementations of such DAC materials can also incorporate thermoelectric materials into the fiber, thus enabling the conversion of adsorption enthalpy to reduce the net power required by this DAC concept.
[0114] We have conducted TEA on a pilot-scale passive ETSA WEDAC system. The energy consumption of Joule heating during desorption is 7.2 GJ tCO.sub.2.sup.1. The energy efficiency of this Joule heating approach is potentially promising with only 7% of the total heating being lost convectively to the ambient. The overall cost is expected to be about 160 $ tCO.sub.2.sup.1 in optimal conditions. This ETSA DAC system possesses advantages such as lower capital costs, higher annual productivity from faster desorption process, and lower energy losses, which together contribute to a lower cost.
The Following References may be Pertinent to the Present Application
[0115] 1. Sanz-prez, E. S., et al. (2016). Direct capture of CO.sub.2 from ambient air. Chemical reviews 116, 11840-11876. [0116] 2. Breyer, C., et al. (2019). Direct air capture of CO.sub.2: a key technology for ambitious climate change mitigation. Joule 3, 2053-2057. [0117] 3. Rim, G., et al. (2022). Sub-Ambient Temperature Direct Air Capture of CO.sub.2 using Amine-Impregnated MIL-101 (Cr) Enables Ambient Temperature CO.sub.2 Recovery. JACS Au 2, 380-393. [0118] 4. Sujan, A. R., et al. (2019). Direct CO.sub.2 capture from air using poly (ethylenimine)-loaded polymer/silica fiber sorbents. ACS Sustainable Chemistry & Engineering 7, 5264-5273. [0119] 5. Song, M., et al. (2022). Cold-Temperature Capture of Carbon Dioxide with Water Coproduction from Air Using Commercial Zeolites. Industrial & Engineering Chemistry Research. [0120] 6. Haertel, C. J. J., et al. (2021). The promise of scalable direct air capture. Chem 7, 2831-2834. [0121] 7. Shi, X., et al. (2020). Moisture-driven CO.sub.2 sorbents. Joule 4, 1823-1837. [0122] 8. Grande, C. A., et al. (2009). CO.sub.2 capture from NGCC power stations using electric swing adsorption (ESA). Energy & fuels 23, 2797-2803. [0123] 9. Wilcox, J. (2020). An electro-swing approach. Nature Energy 5, 121-122. [0124] 10. Zhao, Q., et al. (2019). CO.sub.2 capture using a novel hybrid monolith (H-ZSM5/activated carbon) as adsorbent by combined vacuum and electric swing adsorption (VESA). Chemical Engineering Journal 358, 707-717. [0125] 11. Regufe, M. J. o., et al. (2020). Development of hybrid materials with activated carbon and zeolite 13 for CO.sub.2 capture from flue gases by electric swing adsorption. Industrial & Engineering Chemistry Research 59, 12197-12211. [0126] 12. Zhao, Y., et al. (2022). Rapid joule-heating activation boosted capacitive performance of carbon fibers. Composites Communications 34. 10.1016/j.coco.2022.101263. [0127] 13. Lu, M., et al. (2021). Continuous stabilization of polyacrylonitrile (PAN)-carbon nanotube (CNT) fibers by Joule heating. Chemical Engineering Science 236. 10.1016/j.ces.2021.116495. [0128] 14. Lu, M., et al. (2020). Structure, properties, and applications of polyacrylonitrile/carbon nanotube (CNT) fibers at low CNT loading. Polymer Engineering & Science 60, 2143-2151. [0129] 15. Chien, A.-T., et al. (2014). Electrical conductivity and Joule heating of polyacrylonitrile/carbon nanotube composite fibers. Polymer 55, 6896-6905. [0130] 16. Athanasopoulos, N., et al. (2011). Numerical investigation and experimental verification of the Joule heating effect of polyacrylonitrile-based carbon fiber tows under high vacuum conditions. Journal of Composite Materials 46, 2153-2165. 10.1177/0021998311430159. [0131] 17. An, H., et al. (2011). CO.sub.2 capture by electrothermal swing adsorption with activated carbon fibre materials. International Journal of Greenhouse Gas Control 5, 16-25. [0132] 18. Moon, S.-H., and Shim, J.-W. (2006). A novel process for CO.sub.2/CH.sub.4 gas separation on activated carbon fiberselectric swing adsorption. Journal of colloid and interface science 298, 523-528. [0133] 19. Sullivan, P. D., et al. (2004). Activated carbon fiber cloth electrothermal swing adsorption system. Environmental science & technology 38, 4865-4877. [0134] 20. Keller, L., et al. (2019). Electrical swing adsorption on functionalized hollow fibers. Chemical Engineering Journal 371, 107-117. [0135] 21. Zhao, Q., et al. (2017). Impact of operating parameters on CO.sub.2 capture using carbon monolith by Electrical Swing Adsorption technology (ESA). Chemical Engineering Journal 327, 441-453. [0136] 22. Verougstraete, B., et al. (2022). Electrical swing adsorption on 3D-printed activated carbon monoliths for CO.sub.2 capture from biogas. Separation and Purification Technology 299, 121660. [0137] 23. Ribeiro, R., et al. (2013). Activated carbon honeycomb monolithZeolite 13 hybrid system to capture CO.sub.2 from flue gases employing Electric Swing Adsorption. Chemical Engineering Science 104, 304-318. [0138] 24. Quan, W., et al. (2022). Scalable Formation of Diamine-Appended Metal-Organic Framework Hollow Fiber Sorbents for Postcombustion CO.sub.2 Capture. JACS Au. [0139] 25. Lee, Y. H., et al. (2021). Controlled Synthesis of MetalOrganic Frameworks in Scalable Open-Porous Contactor for Maximizing Carbon Capture Efficiency. JACS Au 1, 1198-1207. [0140] 26. Diederichsen, K. M., et al. (2022). Nondimensional Analysis of a Hollow Fiber Membrane Contactor for Direct Air Capture. Industrial & Engineering Chemistry Research 61, 11964-11976. [0141] 27. Wilfong, W. C., et al. (2022). Directly Spun Epoxy-Crosslinked Polyethylenimine Fiber Sorbents for Direct Air Capture and Postcombustion Capture of CO.sub.2. Energy Technology, 2200356. [0142] 28. Labreche, Y., et al. (2013). Post-spinning infusion of poly (ethyleneimine) into polymer/silica hollow fiber sorbents for carbon dioxide capture. Chemical engineering journal 221, 166-175. [0143] 29. Sholl, D. S., et al. (2022). Exemplar Mixtures for Studying Complex Mixture Effects in Practical Chemical Separations. JACS Au 2, 322-327. [0144] 30. Fan, Y., et al. (2014). Evaluation of CO.sub.2 adsorption dynamics of polymer/silica supported poly(ethylenimine) hollow fiber sorbents in rapid temperature swing adsorption. International Journal of Greenhouse Gas Control 21, 61-71. [0145] 31. Wijesiri, R. P., et al. (2019). Desorption process for capturing CO.sub.2 from air with supported amine sorbent. Industrial & Engineering Chemistry Research 58, 15606-15618. [0146] 32. Didas, S. A., et al. (2014). Effect of amine surface coverage on the co-adsorption of CO.sub.2 and water: spectral deconvolution of adsorbed species. The journal of physical chemistry letters 5, 4194-4200. [0147] 33. Labreche, Y., et al. (2014). Poly (amide-imide)/silica supported PEI hollow fiber sorbents for postcombustion CO.sub.2 capture by RTSA. ACS Applied Materials & Interfaces 6, 19336-19346. [0148] 34. Labreche, Y., et al. (2013). Post-spinning infusion of poly (ethyleneimine) into polymer/silica hollow fiber sorbents for carbon dioxide capture. Chemical engineering journal 221, 166-175.
The description of the present embodiments of the invention has been presented for purposes of illustration but is not intended to be exhaustive or to limit the invention to the form disclosed. Many modifications and variations will be apparent to those of ordinary skill in the art. As such, while the present invention has been disclosed in connection with an embodiment thereof, it should be understood that other embodiments may fall within the spirit and scope of the invention. All patents and publications cited herein are incorporated by reference in their entirety.