エネルギー・環境を エネルギー・環境を エネルギー・環境を
エネルギー・環境を支える 支える 支える 支える 新規機能性活性炭 新規機能性活性炭 新規機能性活性炭 新規機能性活性炭
((
((Novel Functional Activated Carbons for the Applications to Energy and Environmental Devices)
尹尹尹 尹 聖昊聖昊聖昊聖昊 九州大学九州大学
九州大学九州大学 先導物質化学研究所先導物質化学研究所先導物質化学研究所先導物質化学研究所
[email protected]
第7講義 2012, Dec. 18
Contents:
1.
活性炭の構造、細孔分析及び応用2.
繊維状ナノ炭素の調製、構造及び応用活性炭を用いた水の浄化 活性炭を用いた水の浄化 活性炭を用いた水の浄化 活性炭を用いた水の浄化
Structure of PAN based carbon fiber Structure of PAN based carbon fiber Structure of PAN based carbon fiber Structure of PAN based carbon fiber
IAMS, Kyushu University Lc(002) Aromatic planar molecule
Stacking unit of planar molecules (Molecular assemble unit)
Micro-domain (Quasi-aligned molecular assemble unit)
Domain
Closely packed micro- domains in mesophase
pitch
Heat Treatment
Graphitic unit
Pleat unit Aligned micro-domains in the mesophase pitch fiber
fiber axis
Deformed micro-domain
Pitch fiber Graphitized fiber spinning
“Axial nano-scale microstructure in the graphitized fiber inherited from liquid crystal mesophase pitch”
Carbon, 34, 83-88 (1996) S. H. Yoon, Y. Korai, K.Yokogawa, S. Fukuyama, M. Yoshimura, I. Mochida
Control of structural units
Carbon materials from the structural points
Carbon is an Indispensable Material for Energy related Devices Best Structure for Best Performance
Best Selection Best Selection
Scientific Cycle
- Structural Understanding - Structure Preparation
- Working Mechanism Molecular Level Electrochemical Catalytic / Kinetics Molecular / Heat Transfer
Carbon
Best carbon?
7
How to prepare the activated carbons How to prepare the activated carbons How to prepare the activated carbons How to prepare the activated carbons
Selection of Precursor - Pore Framework / Density
- Properties of Pore Wall, Composition / Graphitic Extent - Reactivity at Activation
- Non-graphitizable precursors like polymer, biomass and isotropic coke for usual AC or ACF
- Graphitizable precursors like anisotropic cokes or mesophase pitch for EDLC electrode materials
Activation Procedures - CO
2, H
2O
- Alkali Hydroxides / Carbonates; More Research - Selective Catalytic Gasification ; Catalyst Control
Very Large Surface Area > 3000 m
2/g Adequate Pore And Wall
C C
C CO2 CO2
CO2 CO2
CO2 2CO
2CO 2CO
2CO
Activation Activation Activation Activation
C C C C
Carbon materials
Activation reagents
• Air, CO2, Steam
• KOH (NaOH), ZnCl2
Chemical activation
10
Conventional concept of activated carbons Conventional concept of activated carbons Conventional concept of activated carbons Conventional concept of activated carbons
STM images of ACFs
12
Structure of glassy carbon
13
Pore nucleation in activated carbon
14
Novel concept of activated carbon Novel concept of activated carbon Novel concept of activated carbon Novel concept of activated carbon
Surface Area, Pore : Depth & Volume Surface Structure
Surface Chemistry
Based and Edge Plane, Substituents Hetero Atoms in Hexagon
Carbon Structure of Wall
Micro, Nano, Macro Structure of Carbon Wall -Graphitization Extent
-Domain Structure
Density, Reactivity (Activated Surface) Precursor : Structure and Reactivity
15
Novel concept of activation Novel concept of activation Novel concept of activation Novel concept of activation
Structural factor should be considered for the better understanding of activated carbons and their applications.
Precursor of ACF has been composed of nano- structural primary units
Pores from intraparticles (Slit shaped? Micropores less than 2 nm)
Pores from interparticles (Channeled shaped having wider pore size distributions (0.2 ~ 50 nm)
Size and arrangement of BSU Etching and diffusion of oxidative agent against BSU
16
Novel understanding of activation mechanism
17
Novel recognition of the structure of ACs Novel recognition of the structure of ACs Novel recognition of the structure of ACs Novel recognition of the structure of ACs
Pore size distribution ( ( ( (NLDFT) ) ) )
20
Pore size distribution (Xe-NMR)
※N.Shiratori, et al., Langmuir 2009, 25(13), 7631-7637.
21
Effect of functional groups (Xe Effect of functional groups (Xe Effect of functional groups (Xe
Effect of functional groups (Xe- - - -NMR) NMR) NMR) NMR)
22
Adsorption of toluene by various ACs
Removal of SOx and NOx Using ACFs
VOCs
NVOCs: Dioxin, PCB CO
Sick-house gases SO 2
CO 2 NO 2
Ox
NO
SPM Toluene etc.
Benzene
Typical Hazard Gases in the Atmosphere
SO 2 SO 4 2-
ACF
2001
000 0 5 55 5 1 11 10000 1 11 15555 222 20000 222 25555
18:00 12:00 12:00 12:00 12:00 12:00 12:00 12:00 12:00 12:00 12:00 12:00 12:00 12:00 12:00 12:00 12:00 12:00
4/234/23 4/24 4/25 4/26 4/27 4/28 4/29 4/30 5/1 5/2 5/3 5/4 5/5 5/6 5/7 5/8 5/9
OG20A (0.100g)
セセセセッッッットトトトACF通
通通過通過過過後後後の後のののSO2濃濃濃濃度度度度 環環 環
環境境境境
SO
2 濃濃濃濃度度度度SOSOSOSO2222濃度(ppb)濃度(ppb)濃度(ppb)濃度(ppb)
2 22
2000000001111年年年 年 ((((1111777日7日日日間間間))))間
ACF (0.100g)
S O
2(p p b ) SO
2After ACF Ambient air
Lapse of time (day)
Data from Dr. Shimohara Of Fukuoka H & E Institute
ACF surface
SO
2(ad.) SO
3(ad.) H
2SO
4(ad.) SO
2O
2H
2O H
2O
aq. H
2SO
4SO
2SO
2+ad.→SO
2ad.
SO
2ad.+1/2O
2→SO
3ad.
SO
3ad.+H
2O→H
2SO
4ad.
H
2SO
4ad.+H
2O→aq.H
2SO
4×
DeSOx mechanism using ACF
Active Sites on Carbon Surface
Oxygen functional group Free valence Benzyne bonds on edge
Hetero-atoms in edge
Acidic nature: Oxidative Basic nature: Reductive
Oxygen activation Zigzag or Armchair
Hexagon stacking height
Hydrophilic/Hydrophobic Small surface energy
How to control ?
Breakthrough of SO 2 Removal
SO
21000ppm,O
25vol.% H
2O 10vol.%,N
2balance, Flow rate: 100ml/min, Temperature: 50℃
Optimum Post-Heat treatment with Reductive Oxygen Removal
Effect of Heat Treatment
Carbon C H N O Ash(%)
OG-15A 93.5 0.6 0.5 5.5 0.0
OG15A-H1100(0min) 97.0 0.4 0.5 2.2 0.0
OG-15A-H1100(1h) 96.8 0.2 0.3 2.7 0.1
(wt.%, dry)
Ar Ar Ar
Ar Ar Ar Ar Ar ,CO,CO
2Heat treatmen t
O O O
O O O O O H
H H
H H H H H O O O O H H H H H H H H
SO SO SO
SO
2222SO SO SO SO
2222H H H H
2222SO SO SO SO
4。4。4。4。aq Removal of Functional Groups
with Least Changes of Carbon Structure Surface Area and Hexagon Stacking
The Effect of Heat Treatment for SO 2 Removal
As-received
600 700 800 900 1000 1100 1200
20 40 60 80 100
SO2removal at stationary state (%)
Heat Treatment Temp. (
oC)
OG20A (2150m2/g)OG15A (1360m2/g) OG10A (1060m2/g) OG8A (840m2/g) OG7A (690m2/g) OG5A (480m2/g)
SO21000 ppm, O25 vol%, H2O 10%
W/F= 2.5 ☓☓☓☓10-3g.min.ml-1, Temperature 30 oC
DeSOx by ACF and CNF-ACF Composite
PDU for SOx Removal by ACF DeSOx condition: SO
21000ppm, O
25vol%,
H
2O 10vol%,
N
2balance
、、、、Total flow rate: 100 ml/min Reaction Temperature: 50 ℃
℃℃℃Time (h)
PO-CNF 1%
cat., 5min growing PO-CNF 5% cat., 5min growing H11000
DeSOx Properties of ACF and ACF-CNF
NO & NO 2 Oxidation over ACF
ACF surface
NO(ad.) O(ad.) NO
2(ad.) NO
3(ad.)
NO O
2NO
2Heating
NO NO
2NO NO3
Identified reaction
aq.HNO
3Strong Inhibition of H
2O
The oxidation of NO 2 always produces NO
And NO 3
-through the disproportionation.
The Mechanism of NO Reductive Removal
ACF surface
NO(ad.) O(ad.) NO
2(ad.) + NH
3(ad.)
NO O
2NH
3N
2+H
2O
The mechanism of NO removal consists of adsorption and oxidation of NO into NO
2which is reduced with NH
3NOx Reduction at Room Temperature
• NOx oxidation
• Urea Activation
• NOx in Environment
• Roles of ACF : More variety of ACF
ACF
(NH
2)
2CO
NOx + O
2N
2+ H
2O
NO
2NO
2NO
2NO
2NO
20 00
0 1111 2222 3333 4444 5555 6666 7777 8888 9999 11101000 11111111 1111 2222 11113333 1111 4444 11115555 1111 6666 1111 7777 11118888 1111 9999 22220000 2222 1111 22222222 22223333 2222 4444 2222 5555 000
0 5 55 5 1 11 10000 1 11 15555 2 22 20000
(p p m ) NO exhaust (10ppm)
NO
2exhaust Lapse of time (hr)
Half amount of adsorbed NO
2is exhausted as NO.
Glass tube
ACF (0.100g) 20ppm
10ppm
Breakthrough time
Adsorption of NO 2 in ACF
Flow rate: 300ml / min
Including of O
2(21%)
NO NO
ACF (0.100g) NO
NO
NO NO
NO NO
Scavenging activities against NO
(p p m )
20ppm
Lapse of time (hr) 0000
5555 10 10 10 10 15 15 15 15 20 20 20 20
0000 1111 2222 3333 4444 5555 6666 7777 8888 9999 10101010 11111111 12121212 13131313 141414 15141515 1615161616 17171717 18181818 19191919 20202020 212121 22212222 2322232323 24242424 25252525
NO exhaust
NO
2exhaust
Breakthrough time
Contact time: 0.3 sec
0.5 h r
Including of O
2(21%)
Flow rate: 300ml / min
NO NO
NO NO NO
NO NO
22NO NO
NO 8mm
0.100g 3cm in length
0.600g 18cm in length 0.300g 9cm in length
0.900g 27cm in length 2.7 sec Cont. time 0.3sec
0.9 sec
1.8 sec NO
NO
NO NO NO NO
22NO
NO NO NO NO
22NO
NO NO NO NO
22NO
The characteristics of NOx purification
NOx is fixed as HNO
3Characterization of ACF purification
ACF
Natural ventilation
Room temperature, ozonizer is no need, no light irradiation, compact design
NO 2 NO 2 SPM
SO 2 Hazardous
NH 3 Odor NO
NO
Forced ventilation
chemicals
ACF
Three-dimensional wind vectors
Natural ventilation system (Fixed type) ACF fence
Natural wind
39 40
Novel applications of ACs Novel applications of ACs Novel applications of ACs Novel applications of ACs
1.HCHO(Removal of sick-house gases) 2.Super capacitor
3.Medicine
4.Capacitive De-ionization (CDI)
5.Heat Pump (adsorptive heat pump)
41
1.HCHO & Toluene (Sickhouse gases)
42
Removal of HCHO using ACs Removal of HCHO using ACs Removal of HCHO using ACs Removal of HCHO using ACs
43
Micro Micro Micro
Micro ATR ATR ATR- ATR - - -FTIR analysis of ACs FTIR analysis of ACs FTIR analysis of ACs FTIR analysis of ACs
44 Relative amount of pyridinic nitrogen functional groups for PAN based ACFs by micro-ATR FTIR analysis
Sample Internal Standard Pyridinic N
aInternal Standard /Pyridinic N
FE100 279 134 0.48
FE200 276 108 0.39
FE300 332 70 0.21
FE400 330 64 0.19
aWavenumber related with pyridinic nitrogen: 1610 ~ 1600 cm-1
Mi Mi Mi
Micro cro cro- cro - - -ATR ATR ATR ATR FTIR FTIR FTIR FTIR
45
Effect of humidity Effect of humidity Effect of humidity Effect of humidity
JOURNAL OF APPLIED POLYMER SCIENCE 106 (4):
2151-2157 NOV 15 2007
46 FE100 FE200 FE300 OG5A OG7A OG15A
Breakthrough Time (h)
0 1 2 3 4 5 6 7
Dry Wet
47
Novel concept of pore Novel concept of pore Novel concept of pore
Novel concept of pore( ( (shallow pore ( shallow pore shallow pore) shallow pore ) ) )
48
PAN PAN
PAN PAN based activated carbon nanofiber based activated carbon nanofiber based activated carbon nanofiber based activated carbon nanofiber
49
Removal of HCHO using PAN Removal of HCHO using PAN Removal of HCHO using PAN
Removal of HCHO using PAN- - -ACNF - ACNF ACNF ACNF
50
Shallow pore Shallow pore Shallow pore Shallow pore( ( ( (? ?? ?) ) ) )
Carbon, 48, 4248-4255 (2010).
Complete removal of HCHO using MnOx/ACNF
Catalysis Today, in press (2012).
52
53 54
2.Super capacitor
55
Study of super capacitor using NMR Study of super capacitor using NMR Study of super capacitor using NMR Study of super capacitor using NMR
56
57 58
59 60
19 19
19 19 F MAS Solid F MAS Solid F MAS Solid F MAS Solid- - -State NMR Spectra - State NMR Spectra State NMR Spectra State NMR Spectra
61
2 22
2 H MAS Solid H MAS Solid H MAS Solid H MAS Solid- - - -State NMR Spectra State NMR Spectra State NMR Spectra State NMR Spectra
62
T T
T T 1 11 1 Values Measured from Values Measured from Values Measured from Values Measured from 2 22 2 H MAS Solid H MAS Solid- H MAS Solid H MAS Solid - - -State NMR State NMR State NMR State NMR Spectra
Spectra Spectra Spectra
63
Surface modified PCNFs
2006, 22(22), 9086.Langmuir64
Capacitances of PCNF series
2006, 22(22), 9086.LangmuirCharacteristics of activated carbons for the selective adsorption behaviors for Indole
and Amylase
AC- medicine Research background
66
Renal function decrease for removal poisons from body Artificial dialysis
Artificial dialysis Artificial dialysis Artificial dialysis
big burden to patient
To prolong the introduction of dialysis, AC medicine was developed Chronic Kidney Desease
AC internal medicine AC internal medicine AC internal medicine AC internal medicine
・ To remove the entro-poisons like indole through the excretion with activated carbon.
・ Very hard to take a dose (6g/day)
研究目標 67
How to decrease the dosage amount
Factors for selective adsorption Factors for selective adsorption Factors for selective adsorption Factors for selective adsorption
・Surface area and pore size
・Shape
・Surface property
Model adsorption materials Model adsorption materials Model adsorption materials Model adsorption materials
・To be removed
Indole (MW: 117.15)
⇒ a kind of poisons
・Not to be removed
Amylase (MW: about 46000)
⇒Digestive enzyme
Samples
68
Relatively similar shapes of pores but different surface area and pore size distribution
OG series (Osaka Gas)
αsanalysis OG5A OG7A OG10A OG15A OG20AH2-OG
5A H2-OG
7A H2-OG
10A H2-OG
15A H2-OG
20A SAC OAC Scmep SACmip
SA (m2/g) Amicro 646 982 1283 1688 1928 728 1247 1305 1548 1802 1254 1585 570 1409
Ameso 0 0 0 0 0 0 0 0 0 0 56 0 108 143
Aexternal 0.3 0.3 0.1 0.3 0.3 0.4 0.1 0.3 0.3 0.5 6.6 1.4 0.2 0.4
Pore size (nm)
W micro 0.65 0.68 0.74 0.90 1.11 0.65 0.70 0.75 0.91 1.11 0.69 0.96 0.64 0.74
d meso 0 0 0 0 0 0 0 0 0 0 12.0 0 5.85 3.24
Oxygen contents
(%) 14.3 19.0 22.2 12.8 12.1 6.0 5.2 4.5 2.5 2.6 15.1 4.7 6.0 4.4
Ball type activated carbons
Ball type activated carbons with diameters of 100~300μm H
2-OG series
Hydrogenation of OG series to remove the oxygen functional groups(600℃, 1h)
・Surface area and pore
・ Surface property
Effect of functional groups for binary solutions
69
Removal ratio of Indole (%)
OG5A OG7A OG10A OG15A OG20A
Small functional groups
49.9 70.1 69.3 70.9 72.1
Large functional groups
43.1 63.3 63.8 69.9 68.6
Removal ratio of amylase (%)
OG5A OG7A OG10A OG15A OG20A
Small functional groups
16.5 26.7 26.6 26.3 24.7
Large functional groups
10.5 17.4 17.8 20.4 17.4
0 1 2 3 4 5
OG5A OG7A OG10A OG15A OG20A AdsorptionselectivityAdsorptionselectivityAdsorptionselectivityAdsorptionselectivity ofofofofIndoleIndoleIndoleIndole
H2OGシリーズ
OGシリーズOG (Large functional groups) H2-OG (Small functional groups)
70
Capacitive De-ionization (CDI)
• Diffusion of ions inside of pores
- Rapid electrochemical adsorption and desorption
Principle of electrical desalination
(electrode) -Na+
- - - -
Na+
Na+ Na+ Na
+
+ + + + + Cl-
Cl-
Cl- Cl-
Cl- (separator) Sea water
Distilled water
CHARGE
- - - Na+
Na+ +
+
+ Cl-
Cl- NaCl
(electrode) (electrode) (electrode)
(separator)
Concentrated water
DISCHARGE
Experimental setup
73
Maxsorb series OG series
Nitric ion removal behaviors Nitric ion removal behaviors Nitric ion removal behaviors Nitric ion removal behaviors
Total
硝酸性窒素イオンにおける脱塩特性は Max
MaxMax
Max---III-IIIIIIIIIが最大特性が最大特性が最大特性が最大特性を示した。
三井鉱産のコークスがOGシリーズより良かった。
MaxsorbMaxsorbMaxsorbMaxsorb >>>> MitsuiMitsuiMitsuiMitsui cokescokescokes >cokes>>> OGOGOGOG seriesseriesseriesseries
0 120 240 360 480 600
0 40 80 120 160
Ionic conductivity (mS m-1)
Time (min) max-II max-III
Electrolyte : NO3-N (20 mg L-1), Flow rate : 5 g min-1
0 120 240 360 480 600
0 40 80 120 160
Electrolyte : NO3-N (20 mg L-1), Flow rate : 5 g min-1 Ionic conductivity (mS m-1)
Time (min) max-II max-III OG-10A OG-20A Mitsui cokes (350 m2 g-1)
0 120 240 360 480 600
0 40 80 120 160
Ionic conductivity (mS m-1)
Time (min) OG-5A OG-7A OG-10A OG-15A OG-20A
Electrolyte : NO3-N (20 mg L-1), Flow rate : 5 g min-1
Up to 1 Up to 1 Up to 1 Up to 1.0V .0V .0V .0V
90.5
82.3
68.4
51.3
28.1
20.1
1 5 10 20 30 40
Desalination rate (%)
(flow rate : 10㎖/min)
Cl - ions in the city water
Effect of flow rate
Points
• How to increase lifetime
• How to increase adsorption selectivity and amount of ions
⇒
Optimization of pore and its distribution How to increase molecular diffusivity Preparation of high electric conductive AC
Application of activated carbons to Heatpump
for energy-free operation
77
Thermal Powered Cooling System
Principle of Heat Pump
Adsorption
Desorption
78
吸着式ヒートポンプの性能と材料特性
Static analysis of adsorptive HP
How to increase power
• Increasing effective adsorption How to increase COP
• Making temperature change smaller
79
吸着式ヒートポンプの性能と材料特性
Performance test results
Silica gel- water Activated carbon - ethanol
Points
• How to increase adsorption amount of molecules such as water, methanol and ethanol
⇒
Optimization of pore and its distribution
How to increase molecular diffusivity
Preparation of high thermal conductive AC
81
Carbons from now
Era of nano-carbons are almost finished. Only special applications are promising!
Era of GOOD Raw material to GOOD Product are almost finished. China and other developing countries will take over whole markets!
Era of BAD Raw material to GOOD Product are coming. Developed countries only have chances on such materials
Novel carbon, if it can be found, still has a chance to change the paradigm.
But what is that?
Nano-carbons (Concept, methodology)
Conventional carbons (Waste Materials)
Fusion