Highly microporous polymer-based carbons for CO2 and H2 adsorption

Jerzy Chomaa, Łukasz Osuchowskib, Michal Marszewskic and Mietek Jaroniec*c
aInstitute of Chemistry, Military University of Technology, 00-098 Warsaw, Poland
bMilitary Institute of Chemistry and Radiometry, 00-910 Warsaw, Poland
cDepartment of Chemistry and Biochemistry, Kent State University, Kent, Ohio 44242, United States. E-mail: jaroniec@kent.edu; Fax: +1 (330) 672-3816; Tel: +1 (330) 672-2032

Received 4th December 2013 , Accepted 12th March 2014

First published on 13th March 2014


Abstract

A series of microporous carbons has been obtained through carbonization and KOH activation of a commercially available styrene divinylbenzene resin with sulfonate functional groups, Amberjet 1200 H. The resulting carbons featured very high specific surface areas: from 725 m2 g−1 to 3870 m2 g−1, large total pore volumes: from 0.44 cm3 g−1 to 2.07 cm3 g−1, and exceptionally developed microporosity: from 0.2 cm3 g−1 to 1.16 cm3 g−1. The controlled activation process afforded high amounts of ultramicropores (micropores < 0.75 nm) reaching 0.32 cm3 g−1. Physisorption measurements showed very high uptakes of CO2 and H2 reaching 356 mg g−1 of CO2 (0 °C, 800 mmHg), 209 mg g−1 of CO2 (25 °C, 850 mmHg), and 39 mg g−1 of H2 (−196 °C, 850 mmHg).


Introduction

Gas adsorption on nanoporous materials plays an important role in solving energy-related issues such as CO2 capture and H2 storage. CO2 is a greenhouse gas that is excessively emitted to the atmosphere by burning fossil fuels, whereas H2 is considered as an environmentally-friendly fuel of the future.1 Thus, there is a great interest in the development of suitable nanoporous adsorbents for gas capture/storage that can be used for controlling the greenhouse effect and solving energy-related issues. Potential environmental benefits arising from this type of research may in a long run result in economic benefits and importantly, enhance the national energy security (independence from fossil fuel-based energy).2–5 Notably, nanoporous adsorbents may also be used in adsorption of different greenhouse (e.g., CO2, CH4) and environmentally-harmful gases (e.g., SO2, NOx).2

Numerous nanoporous materials such as carbons,6–8 ordered mesoporous silicas and amine-functionalized organosilicas,9–11 metal organic frameworks,12,13 porous polymers,14 and metal oxides15,16 were successfully employed as CO2 adsorbents. Recently, however, novel advanced materials such as microporous carbons,6,17–19 carbon–metal composites,20 biomass-derived carbons,17,21 carbon nanotubes,22 ordered mesoporous carbons,23 and N-doped carbons24 gained a significant interest. These carbon-based materials are favourably employed in CO2 adsorption, unsurprisingly, considering their availability and low cost as well as their good thermal, mechanical, and chemical stability. It appears that these carbon materials can be utilized not only in environmental remediation but in energy sector as well. One of such applications is H2 adsorption and storage. Hydrogen is considered a zero-emission fuel with the highest energy density per unit mass. Hydrogen storage can be achieved by adsorption, liquefaction, compression, or chemical bonding as metal hydrides.25 Adsorption of hydrogen on nanoporous carbon materials has significant advantages such as complete reversibility and fast kinetics of the process; carbon materials are also lightweight and, hence, the impact on the energy density is small. Importantly, carbon materials used in hydrogen storage have to provide extremely high surface area,26,27 which is often achieved by the presence of micropores with very small sizes that effectively increase material's H2 storage capability.28–30 Based on experimental data, Ströbel et al.31 predicted, using an extrapolation, that the specific surface area exceeding 4000 m2 g−1 is required to achieve 6 wt% of adsorbed hydrogen. Achievement of such high surface area is extremely challenging. Typically, the amount of adsorbed gas is associated with the specific surface area: the larger surface area is the larger adsorption is. However, recent studies showed that H2 adsorption can also be enhanced by the presence of ultramicropores (micropores < 0.75 nm).32

Among various polymeric-type carbon precursors, styrene divinylbenzene ion-exchange resins with sulfonate functional groups are promising polymers for preparation of microporous carbons.33–35 Carbonization of these resins at temperatures between 500 and 900 °C in nitrogen atmosphere resulted in the decomposition of sulfonate groups and creation of microporosity. In particular, carbonization at 500 °C gave carbons with narrow pore size distribution in the micropore range with the average pore size between 0.38 nm and 0.45 nm.35

In this work, a series of microporous carbons was prepared by carbonization and activation of a commercially available styrene divinylbenzene resin with sulfonate functional groups, Amberjet 1200 H. The activation process conducted at 700 °C by using different amounts of KOH (1[thin space (1/6-em)]:[thin space (1/6-em)]1 to 6[thin space (1/6-em)]:[thin space (1/6-em)]1 KOH to carbon ratio) resulted in highly microporous and high surface area carbons. The resulting carbons exhibited high CO2 uptake at 0 °C and 25 °C, and H2 adsorption at −196 °C. The results presented in this work prove the dominant role of ultramicropores (pores below 0.75 nm) in CO2 adsorption, and the requirement of the extremely high specific surface area (∼4000 m2 g−1) for effective H2 adsorption.

Experimental

Preparation of polymer-based carbon

Monodisperse carbon spheres (C) were obtained from commercially available styrene divinylbenzene ion-exchange resin spheres (d = 0.5 mm), Amberjet 1200 H (Rohm and Haas, Philadelphia, PA, USA). Namely, 120 g of the resin spheres was dried at 100 °C for 3 hours and subsequently, immersed in 300 cm3 of 50% orthophosphoric acid (H3PO4, POCh, Poland). The swollen resin was evaporated in a rotary evaporator at 180 °C. The product was allowed to cool to room temperature and washed with 250 mL of water. Next, the resin was dried at 80 °C for 75 minutes. Finally, the resin was carbonized in static atmosphere in a furnace at 350 °C for 90 minutes using 20 °C min−1 heating ramp. The carbonized product was washed with 500 mL of distilled water and dried at 100 °C for 60 minutes.

Activation of carbon material

The activation process was carried out in nickel crucibles using 1 g of the carbon material and different amounts to KOH (POCh, Poland) to achieve the following KOH/carbon weight ratios: 1[thin space (1/6-em)]:[thin space (1/6-em)]1, 2[thin space (1/6-em)]:[thin space (1/6-em)]1, 3[thin space (1/6-em)]:[thin space (1/6-em)]1, 4[thin space (1/6-em)]:[thin space (1/6-em)]1, 5[thin space (1/6-em)]:[thin space (1/6-em)]1, and 6[thin space (1/6-em)]:[thin space (1/6-em)]1. The crucibles were placed in a furnace in nitrogen atmosphere and heated from room temperature up to 700 °C using 20 °C min−1 heating ramp and dwelled for 1 hour. The cooled product was immersed in 30 mL of 35 wt% of HCl and sonicated for 1 hour. Subsequently, the activated carbons were filtered and washed until natural pH, and dried at 100 °C for 24 hours. The resulting activated carbons were labelled according to the KOH/carbon ratios as: C-1, C-2, C-3, C-4, C-5, and C-6. The starting carbon material, obtained by carbonization of the resin, was denoted as C.

Measurements and calculations

Scanning electron micrographs were taken on a LEO 1530 scanning electron microscope manufactured by Zeiss (Germany) operated at 2 kV acceleration voltage.

All physisorption isotherms: N2 at −196 °C, CO2 at 0 °C and 25 °C, and H2 at −196 °C, were measured on an ASAP 2020 volumetric surface and porosity analyzer manufactured by Micromeritics (Norcross, GA, USA). Prior to measurements, each sample was outgassed at 200 °C for 2 hours.

Specific surface area, SBET, was calculated using Brunauer–Emmett–Teller (BET) method based on low-temperature nitrogen adsorption isotherm in a relative pressure range of 0.05–0.2, assuming a cross-section area of nitrogen molecule equal to 0.162 nm2.36 Total pore volume, Vt, was calculated by converting the volume of nitrogen adsorbed at relative pressure p/po = 0.99 to the volume of liquid nitrogen.37 Pore size distribution function (PSD) was calculated from low-temperature nitrogen adsorption isotherm using DFT method implemented in the ASAP 2020 instrument software. Ultramicropore volume, VDFTmi1, was calculated from the corresponding PSD in a pore size range 0–0.75 nm. Micropore volume, VDFTmi2, was obtained for pores below 2 nm. Total pore volume, VDFTt, and specific surface area, SDFTt, were calculated using DFT algorithm for pores within range 0.4–50 nm. Ultramicropore volume, Vmi1αs, and micropore volume, Vmi2αs, were calculated using comparative αs-plot method,37 for αs values in range 0.25–0.5 and 0.9–1.3, respectively (were αs is a reduced adsorption defined as the ratio of adsorption at particular relative pressure to the adsorption at p/po = 0.4). The reference material used in the comparative studies was Cabot BP280 carbon black reference material.38 External surface, Sextαs, was calculated in αs range of 3–8. Mesopore volume, Vmeαs, was calculated by subtraction of Vmi2αs from Vt. Additionally, PSD was calculated using Kruk–Jaroniec–Sayari (KJS) method,39 which is based on Barrett–Joyner–Halenda (BJH) algorithm,40 and uses the corrected Kelvin equation and the experimentally obtained statistical film thickness for nitrogen on the Cabot BP280 material. Micropore width, wKJSmi2, and mesopore width, wKJSme, were calculated as maxima of the PSD curve in the corresponding pore size ranges. Microporosity was calculated as the ratio of Vmi2αs to Vt and expressed in %.

Results and discussion

Morphology

Scanning electron microscopy (SEM) was used to investigate morphology of the styrene divinylbenzene resin, and the resulting carbon material and activated carbons. Fig. 1 shows SEM micrographs of a single resin sphere, a single carbon sphere, a collection of the carbon spheres, and grains of the activated carbon C-4. As can be seen in this figure the resin material – used as a carbon precursor – has spherical morphology with extremely uniform diameters of ca. 500 μm.
image file: c3ra47278g-f1.tif
Fig. 1 Scanning electron micrographs of the styrene divinylbenzene resin (A), the carbon material (B) and (C), and the activated carbon C-4 (D).

The carbon material, obtained through carbonization of the resin, retained the spherical morphology; however, the spheres are noticeably cracked with diameters ca. 450 μm. It is possible that the cracking is related to the volume change, which occurred when the swollen resin impregnated with orthophosphoric acid underwent the thermal treatment at 350 °C. Finally, the subsequent activation process, conducted at 700 °C with KOH, destroyed the spherical morphology and the resulting activated carbon was in the form of irregularly shaped grains of different sizes. Activation conditions were used as in our previous work, which shows that 700 °C is sufficient temperature for effective KOH activation.41

Porosity

The aim of our work was to obtain carbon materials with high specific surface area, well-developed porosity, and with possibly large amount of ultramicropores. Fig. 2 shows low-temperature nitrogen adsorption–desorption isotherms of all carbon materials. All isotherms can be classified as type IV with H4 hysteresis loop according to the IUPAC classification.42 Table 1 lists all of the structural parameters calculated based on the nitrogen adsorption data.
image file: c3ra47278g-f2.tif
Fig. 2 Low-temperature nitrogen adsorption–desorption isotherms measured on all carbon materials.
Table 1 Structural parameters for all carbon materialsa
Carbon SBET (m2 g−1) Vt (cm3 g−1) VDFTmi1 (cm3 g−1) VDFTmi2 (cm3 g−1) VDFTt (cm3 g−1) SDFTt (m2 g−1) Microporosity (%)
a C – carbon, C–X – X denotes the KOH/carbon weight ratio; SBET – BET specific surface area; Vt – total (single-point) pore volume obtained from the amount adsorbed at p/po ≈ 0.99; VDFTmi1 – volume of ultramicropores (pores < 0.75 nm) obtained on the basis of DFT PSD; VDFTmi2 – volume of micropores (pores < 2 nm) obtained on the basis of DFT PSD; VDFTt – total pore volume estimated by the DFT method; SDFTt – total specific surface area obtained by the DFT method; microporosity – percentage of volume of micropores (Vαsmi2) in the total pore volume (Vt).
C 218 0.12 0.01 0.07 0.10 101 67
C-1 725 0.44 0.08 0.20 0.34 489 68
C-2 1510 0.83 0.20 0.55 0.66 1480 77
C-3 3180 1.70 0.27 0.97 1.25 2120 75
C-4 3870 2.07 0.32 1.16 1.60 2600 77
C-5 3630 1.95 0.25 0.99 1.53 2240 75
C-6 2900 1.54 0.18 0.75 1.25 1760 77


The activated carbons studied exhibited extremely high values of the specific surface area SBET (up to 3870 m2 g−1), total pore volume Vt up to 2.07 cm3 g−1, micropore volume VDFTmi2 up to 1.16 cm3 g−1, and ultramicropore volume VDFTmi1 up to 0.32 cm3 g−1. Notably, all these parameters change as a function of the KOH/carbon ratio: initially, the values increase from C-1 to C-4 and decrease thereafter for C-5 and C-6 samples.

Interestingly, in all cases the values of the total pore volume VDFTt, calculated using DFT method, were considerably smaller as compared with the total pore volumes Vt, calculated using volume of nitrogen adsorbed at p/po ≈ 0.99. The same is apparent when comparing the values of the specific surface area SDFTt, calculated using DFT method, with SBET, obtained by the BET method. This behaviour is known because the BET method overestimates the specific surface area of microporous carbons.43

The aforementioned quantities, specific surface area and total pore volume, reach their maximum values for the C-4 material; the same apply to the other structural parameters listed in Table 1. Unsurprisingly, the values of the structural parameters obtained for the carbon material C are considerably lower as compared to those evaluated for the activated carbons. Fig. 3 shows pore size distribution functions (PSDs), calculated using DFT method, for all carbon materials. All activated carbons show trimodal PSDs with three maxima appearing in the following ranges: 0–1 nm, 1–2 nm, and 2–3 nm. The carbon material C, on the other hand, does not have any porosity in the range of smallest pores: 0–1 nm. Based on this observation, one can conclude that KOH activation was shown to be a successful way for introducing ultramicroporosity (pores below 0.75 nm) in carbons, which was found to be the key factor controlling CO2 uptake at ambient conditions.19,44


image file: c3ra47278g-f3.tif
Fig. 3 Incremental pore size distribution functions for all carbon materials (calculated by the DFT method).

In addition, the KOH activation increased the amount of larger micropores (1–2 nm) in addition to those already present in non-activated carbon. Interestingly, the fraction of microporosity in the total porosity is ca. 75% on average for all of the activated carbons. The amount of introduced ultramicroporosity, and larger micropores (supermicropores), follows the same trend as all other structural parameters and reach their maxima for the C-4 material.

In addition, the structural parameters have been calculated using the αs-plot method.37 Fig. 4 shows αs plots for the selected activated carbons: C-1, C-3, and C-4. The solid straight lines, calculated in the αs range 0.25–0.5, were used to estimate volumes of ultramicropores Vmi1αs; whereas, the dotted straight lines, calculated in the αs range 0.9–1.3, were used to estimate volumes of micropores Vmi2αs. Table S1 (ESI) lists all structural parameters calculated using the αs-plot method. Based on the obtained values, one can conclude that KOH activation resulted in the development of both, ultramicropores and large micropores (supermicropores). Similarly, the highest values of the structural parameters were recorded for the activated carbon C-4: ultramicropore volume Vmi1αs = 0.31 cm3 g−1, micropore volume Vmi2αs = 1.59 cm3 g−1, and mesopore volume Vmeαs = 0.54 cm3 g−1.


image file: c3ra47278g-f4.tif
Fig. 4 αs plots for the selected activated carbons: C-1, C-3, and C-4. The solid straight lines calculated in the αs range 0.25–0.5 (Vmi1αs), the dotted straight lines calculated in the αs range 0.9–1.3 (Vmi2αs).

Low-temperature nitrogen adsorption isotherms were used to calculate PSD functions using Kruk–Jaroniec–Sayari (KJS) method.39 Fig. S1 (ESI) shows the calculated PSDs for all activated carbons studied. The PSD curves show two distinct maxima: one present in the micropore range wKJSmi2 ca. 0.8 nm and the other at the border range of micropores and mesopores. The values of these maxima for each material are listed in Table S1 (ESI). Notably, the PSD peaks in the micropore range are narrower than the peaks present in the mesopore range. The obtained PSD curves illustrate the effect of the KOH activation on the evolution of microporosity in the activated carbons studied.

CO2 adsorption

CO2 adsorption on the activated carbons was measured at 0 °C and 25 °C up to 800 and 850 mmHg, respectively. Fig. 5 and 6 show the measured CO2 isotherms for all carbon materials for the respective temperatures. Complementarily, Fig. S2 and S3 show the same isotherms expressed as mmol of adsorbed CO2 per unit mass of adsorbent (mmol g−1) for the respective temperatures.
image file: c3ra47278g-f5.tif
Fig. 5 CO2 adsorption isotherms measured at 0 °C for all carbon materials.

image file: c3ra47278g-f6.tif
Fig. 6 CO2 adsorption isotherms measured at 25 °C for all carbon materials.

Initially, CO2 uptake increases in order from the C-1 material to C-4 material, which correlates with the amount of the KOH used during activation. The maximum uptake is observed for the C-4 material and thereafter adsorption declines for the materials C-5 and C-6. Conspicuously, the highest CO2 adsorption was observed for the material that has the highest values of the structural parameters: SBET, Vt, VDFTmi1, VDFTmi2, VDFTt, SDFTt among all the activated carbons studied. The recorded values were: 356 mg of CO2 (0 °C, 800 mmHg) and 209 mg of CO2 (25 °C, 850 mmHg). Table 2 shows a comparison of CO2 and H2 adsorption data for various materials.

Fig. 7 shows the CO2 uptake at 0 °C and 25 °C as a function of specific surface area SDFTt for all carbon materials. The solid lines represent a simple linear regression over the values at two temperatures with the correlation coefficients: R2 = 0.918 for 0 °C, and R2 = 0.879 for 25 °C. Although, the CO2 uptake clearly increases with the specific surface area, the correlation is not strong enough to claim that the surface area is the parameter determining CO2 adsorption.


image file: c3ra47278g-f7.tif
Fig. 7 CO2 uptake at 0 °C and 800 mmHg, and at 25 °C and 850 mmHg as a function of the specific surface area SDFTt for all carbon materials.
Table 2 Comparison of CO2 and H2 adsorption on various materials
Materials CO2 at 1 bar and 0 °C (mg g−1) CO2 at 1 bar and 25 °C (mg g−1) H2 at 1 bar and −196 °C (mg g−1)
This publication 73–343 42–189 5.3–37.5
Activated carbons 123–37846 66–21146 3–2648
222–38047 131–20747
Carbide-derived carbons 110–16849 Up to 2748
Zeolite-templated carbons 213–30450 140–19350 15.6–22.751
Various metal oxides 21–5252
Zeolites 33–20546
120–23152
MOFs 0.16–26453 0.57–37353 11.7–25.454


Fig. 8 shows the CO2 uptake at 0 °C and 800 mmHg, and at 25 °C and 850 mmHg as a function of the ultramicropore volume VDFTmi1 for all carbon materials. Similarly, the solid lines are linear regressions over two sets of points; however, the correlation coefficients are noticeably better in this case: R2 = 0.986 at 0 °C and R2 = 0.970 at 25 °C. These results suggest that the volume of ultramicropores has a pronounced effect on the CO2 uptake at pressures up to 850 mmHg; the latter is almost linearly correlated with the volume of ultramicropores. Similar results were recently reported by Sevilla et al. in their work on microporous and N-doped carbon microspheres.45


image file: c3ra47278g-f8.tif
Fig. 8 CO2 uptake at 0 °C and 800 mmHg, and at 25 °C and 850 mmHg as a function of ultramicropore volume VDFTmi1 for all carbon materials.

The above conclusion is additionally supported by Fig. S4–S6 included in ESI. Fig. S4 shows the CO2 uptake at 0 °C and 800 mmHg, and at 25 °C and 850 mmHg as a function of the specific surface area SBET for all carbon materials; Fig. S5 shows the same variable as a function of the ultramicropore volume Vmi1αs and Fig. S6 as a function of the micropore volume Vmi2αs. In those cases, the specific surface area SBET was calculated using BET method and the latter two values, Vmi1αs and Vmi2αs, were calculated using comparative αs-plot method.

H2 adsorption

H2 adsorption was measured at −196 °C and pressure up to 850 mmHg. Fig. 9 shows H2 adsorption isotherms measured at −196 °C for all carbon materials. Similarly to CO2 adsorption, H2 uptake at 850 mmHg pressure increases in order from C-1 to C-4, along with the amount of the KOH used during activation, and declines thereafter for the C-5 and C-6 materials. The H2 uptake at 850 mmHg pressure was found to be highest for the C-4 material as well. The latter material adsorbed 39 mg g−1 of H2 at −196 °C and pressure of 850 mmHg. Fig. 10 shows H2 uptake at −196 °C and 850 mmHg as a function of the specific surface area SDFTt for all carbon materials. The solid line represents a simple linear regression with the correlation coefficient: R2 = 0.995.
image file: c3ra47278g-f9.tif
Fig. 9 H2 adsorption isotherms measured at −196 °C for all carbon materials.

image file: c3ra47278g-f10.tif
Fig. 10 H2 uptake at −196 °C and 850 mmHg as a function of the specific surface area SDFTt for all carbon materials.

The strong correlation between H2 uptake and specific surface area proves that H2 adsorption on activated carbons is mainly governed by their specific surface area. The conclusion is further supported by Fig. 11, which shows the same variable but plotted as a function of the ultramicropore volume, VDFTmi1. The solid line represents a simple linear regression with the correlation coefficient: R2 = 0.979, which is high but noticeably lower than that for the linear dependence of H2 uptake on the specific surface area (Fig. 10). Based on these observations, hydrogen is possibly adsorbed through film formation rather than by micropore filling mechanism. The strong correlation between H2 uptake and ultramicropore or micropore volumes can be explained as indirect relation to high surface area of these pores (which is the main contribution to the overall surface area of the materials).


image file: c3ra47278g-f11.tif
Fig. 11 H2 uptake at −196 °C and 850 mmHg as a function of the ultramicropore volume VDFTmi1 for all carbon materials.

Additional plots showing the H2 uptake as a function of the structural parameters calculated by using BET and αs-plot methods are included in ESI. Fig. S7 shows H2 uptake at −196 °C and 850 mmHg as a function of the specific surface area SBET for all carbon materials. Fig. S8 and S9 show the same variable but plotted as a function of the ultramicropore volume, Vmi1αs, and micropore volume, Vmi2αs, respectively. The correlation coefficients for these regressions are: 0.943, 0.936, and 0.950, respectively.

Conclusions

A series of microporous carbons has been obtained through carbonization and KOH activation of a commercially available styrene divinylbenzene resin with sulfonate functional groups, Amberjet 1200 H. The resulting carbons showed large amounts of ultramicropores (micropores < 0.75 nm) and high specific surface area. The well-developed microporous structure resulted in high CO2 and H2 uptakes. The best activated carbons adsorbed: 356 mg g−1 of CO2 (0 °C, 800 mmHg) and 209 mg g−1 of CO2 (25 °C, 850 mmHg); and 39 mg g−1 of H2 (−196 °C and 850 mmHg). KOH activation resulted in the development of highly microporous structure as compared to the corresponding non-activated carbon, see the following data: the specific surface area changed from 218 m2 g−1 to 3870 m2 g−1, total pore volume from 0.12 cm3 g−1 to 2.07 cm3 g−1, micropore volume from 0.07 cm3 g−1 to 1.16 cm3 g−1, and ultramicropore volume from 0.01 cm3 g−1 to 0.32 cm3 g−1. The extremely good adsorption properties of the resulting microporous carbons toward CO2 and H2 render them applicable in the environmental and energy-related applications such as CO2 capture and hydrogen storage.

Acknowledgements

JC and LO acknowledge the National Science Centre (Poland) for support of this research under grant 2013/09/B/ST5/00076.

Notes and references

  1. C. Robertson and R. Mokaya, Microporous Mesoporous Mater., 2013, 179, 151 CrossRef CAS.
  2. R. E. Morris and P. S. Wheatley, Angew. Chem., Int. Ed., 2008, 47, 4966 CrossRef CAS PubMed.
  3. M. Jorda-Beneyto, F. Suarez-Garcia, D. Lozano-Castello, D. Cazorla-Amoros and A. Linares-Solano, Carbon, 2007, 45, 293 CrossRef CAS.
  4. A. W. C. van der Berg and C. O. Arean, Chem. Commun., 2009, 668 Search PubMed.
  5. Q. Wang, J. Luo, Z. Zhong and A. Borgna, Energy Environ. Sci., 2011, 4, 42 CAS.
  6. N. P. Wickramaratne and M. Jaroniec, ACS Appl. Mater. Interfaces, 2013, 5, 1849 CAS.
  7. J. Silvestre-Alberto, A. Wahby, A. Sepulveda-Escribano, M. Martinez-Escandell, K. Kaneko and F. Rodriguez-Reinoso, Chem. Commun., 2011, 47, 6840 RSC.
  8. A. Boonpoke, S. Chiarakorn, N. Laosiripojana, S. Towprayoon and A. Chidthaisong, Korean J. Chem. Eng., 2012, 29, 89 CrossRef CAS.
  9. J. Ren, L. Wu and B. G. Li, Ind. Eng. Chem. Res., 2012, 51, 7901 CrossRef CAS.
  10. T. L. Chew, A. L. Ahmad and S. Bhatia, Adv. Colloid Interface Sci., 2010, 153, 43 CrossRef CAS PubMed.
  11. A. Zukal, J. Jagiello, J. Mayerova and J. Cejka, Phys. Chem. Chem. Phys., 2011, 13, 15468 RSC.
  12. K. Sumida, D. L. Rogow, J. A. Mason, T. M. McDonald, E. D. Bloch, Z. R. Herm, T. H. Bae and J. R. Long, Chem. Rev., 2012, 112, 724 CrossRef CAS PubMed.
  13. J. Liu, P. K. Thellapally, B. P. McGrail, D. R. Brown and J. Liu, Chem. Soc. Rev., 2012, 41, 2308 RSC.
  14. M. G. Rabbani and H. M. El-Kaderi, Chem. Mater., 2012, 24, 1511 CrossRef CAS.
  15. Q. Wang, H. H. Tay, Z. Zhong, J. Luo and A. Borgna, Energy Environ. Sci., 2012, 5, 7526 CAS.
  16. M. Broda and C. R. Müller, Adv. Mater., 2012, 24, 3059 CrossRef CAS PubMed.
  17. M. G. Plaza, C. Peveida, B. Arias, M. D. Casal, C. F. Martin, J. Fermoso, F. Rubiera and J. J. Pis, J. Environ. Eng., 2009, 135, 426 CrossRef CAS.
  18. G. P. Hao, W. Li, D. Qian and A. H. Lu, Adv. Mater., 2010, 22, 853 CrossRef CAS PubMed.
  19. N. P. Wickramaratne and M. Jaroniec, J. Mater. Chem. A, 2013, 1, 112 CAS.
  20. C. H. Yu, C. H. Huang and C. S. Tan, Aerosol Air Qual. Res., 2012, 12, 745 CAS.
  21. J. Wang, A. Heerwig, M. R. Lohe, M. Oschatz, L. Borchardt and S. Kaskel, Mater. Chem., 2012, 22, 13911 RSC.
  22. S. Sircar, T. C. Golden and M. B. Rao, Carbon, 1996, 34, 1 CrossRef CAS.
  23. D. Saha and S. Deng, J. Colloid Interface Sci., 2010, 345, 402 CrossRef CAS PubMed.
  24. X. Wei, C. Liu, Z. Zhou, L. Zhang, J. Zhou, S. Zhou, Z. Yan, H. Gao, G. Wang and S. Z. Qiao, Energy Environ. Sci., 2012, 5, 7323 Search PubMed.
  25. H. Wang, Q. Gao and J. Hu, J. Am. Chem. Soc., 2009, 131, 7016 CrossRef CAS PubMed.
  26. M. Hirscher and B. Panella, J. Alloys Compd., 2005, 404–406, 399 CrossRef CAS.
  27. Q. Hu, Y. Lu and G. P. Meisner, J. Phys. Chem. C, 2008, 112, 1516 CAS.
  28. Z. Yang, Y. Xia and R. Mokaya, J. Am. Chem. Soc., 2007, 129, 1673 CrossRef CAS PubMed.
  29. A. Pacuła and R. Mokaya, J. Phys. Chem. C, 2008, 112, 2764 Search PubMed.
  30. W. C. Xu, K. Takahashi, Y. Matsuo, Y. Hattori, M. Kumagi, S. Ishiyama, K. Kaneko and S. Iijima, Int. J. Hydrogen Energy, 2007, 32, 2504 CrossRef CAS.
  31. R. Ströbel, J. Garche, P. T. Mosley, L. Jörissen and G. Wolf, J. Power Sources, 2006, 159, 781 CrossRef.
  32. J. R. Morris, C. I. Contescu, M. F. Chisholm, V. R. Cooper, J. Guo, L. He, Y. Ihm, E. Mamontov, Y. B. Melnichenko, R. J. Olsen, S. J. Pennycook, M. B. Stone, H. Zhang and N. C. Gallego, J. Mater. Chem. A, 2013, 1, 9341 CAS.
  33. S. J. Park and W. Y. Jung, J. Colloid Interface Sci., 2002, 250, 196 CrossRef CAS PubMed.
  34. S. J. Park and W. Y. Jung, Carbon, 2002, 40, 2021 CrossRef CAS.
  35. H. Nakagawa, K. Watanabe, Y. Harada and K. Miura, Carbon, 1999, 37, 1455 CrossRef CAS.
  36. S. Brunauer, P. H. Emmett and E. Teller, J. Am. Chem. Soc., 1938, 60, 309 CrossRef CAS.
  37. M. Jaroniec and K. Kaneko, Langmuir, 1997, 13, 6589 CrossRef CAS.
  38. M. Kruk, M. Jaroniec and K. P. Gadkaree, J. Colloid Interface Sci., 1997, 192, 250 CrossRef CAS PubMed.
  39. M. Kruk, M. Jaroniec and A. Sayari, Langmuir, 1997, 13, 6267 CrossRef CAS.
  40. E. P. Barrett, L. G. Joyner and P. P. Halenda, J. Am. Chem. Soc., 1951, 73, 373 CrossRef CAS.
  41. J. Górka, A. Zawislak, J. Choma and M. Jaroniec, Carbon, 2008, 46, 1159 CrossRef.
  42. K. S. W. Sing, D. H. Everett, R. A. W. Haul, L. Moscou, R. A. Pierotti, J. Rouquerol and T. Siemieniewska, Pure Appl. Chem., 1985, 57, 603 CrossRef CAS.
  43. M. Kruk, M. Jaroniec and K. P. Gadkaree, Langmuir, 1999, 15, 1442 CrossRef CAS.
  44. Y. Liu and J. Wilcox, Environ. Sci. Technol., 2012, 46, 1940 CrossRef CAS PubMed.
  45. M. Sevilla, J. B. Parra and A. B. Fuertes, ACS Appl. Mater. Interfaces, 2013, 5, 6360 CAS.
  46. Z. Chen, S. Deng, H. Wei, B. Wang, J. Huang and G. Yu, Front. Environ. Sci. Eng., 2013, 7, 326 CrossRef CAS.
  47. A. Wahby, J. M. Ramos-Fernandez, M. Martinez-Escandell, A. Sepulveda-Escribano, J. Silvestre-Albero and F. Rodriguez-Reinoso, ChemSusChem, 2010, 3, 974 CrossRef CAS PubMed.
  48. M. Sevilla and R. Mokaya, Energy Environ. Sci., 2014 10.1039/c3ee43525c , advanced article.
  49. M. E. Casco, M. Martinez-Escandell, J. Silvestre-Albero and F. Rodriguez-Reinoso, Carbon, 2014, 67, 230 CrossRef CAS.
  50. Y. Xia, R. Mokaya, G. S. Walker and Y. Zhu, Adv. Energy Mater., 2011, 1, 678 CrossRef CAS.
  51. J. Cai, L. Li, X. Lv, C. Yang and X. Zhao, ACS Appl. Mater. Interfaces, 2014, 6, 167 CAS.
  52. C. Chen and W.-S. Ahn, Chem. Eng. J., 2011, 166, 646 CrossRef CAS.
  53. S. Keskin, T. M. van Heest and D. S. Sholl, ChemSusChem, 2010, 3, 879 CrossRef CAS PubMed.
  54. J. L. C. Rowsell and O. M. Yaghi, J. Am. Chem. Soc., 2006, 128, 1304 CrossRef CAS PubMed.

Footnote

Electronic supplementary information (ESI) available: Additional table and nine plots included. See DOI: 10.1039/c3ra47278g

This journal is © The Royal Society of Chemistry 2014
Click here to see how this site uses Cookies. View our privacy policy here.