Life cycle energy use and GHG emissions of microalgal
Transcript of Life cycle energy use and GHG emissions of microalgal
Life cycle energy use and GHG emissions of
microalgal biodiesel in China
Zhang Tingting, Xie Xiaomin, Huang Zhen Research Center for Combustion &
Environmental Technology
SJTU
The 7th Annual CE-CERT-SJTU Student Symposium
Outline
Backgrounds 1
Methodology 2
Results and discussions 3
Conclusions and prospects 4
Backgrounds
1.1 Challenges to global transportation energy
Energy security
Global warming
Atmosphere pollution
Energy security
2009 fuel shares of
total final consumption
2009 shares of
oil consumption by sector
Data source: from IEA
Total final consumption worldwide is dominated by oil. 61.7% of oil is used
for transport in 2009.
Energy security
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Oil
pro
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2010 world oil proved reserves and R/P ration
Oil proved reserves R/P ration
1-US; 2-China; 3-North America; 4-S. & Cent. America; 5-Europe
&Eurasia;6-Middle East; 7- Africa; 8-Asia Pacific;9-Total World
Data source: from BP
Energy security
118.4
43.7
28.8 33.3
24.1
12.7 10.1 7 2.7 2.5
7.2 1.3 2.7
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Millio
n t
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2010 Crude oil imports and compositon in China
Data source: from BP
55% of crude oil in China are mainly imported from Middle East and
West Africa. It might cause oil security issue, as the situation in these
regions are complicated.
Global warming
Data source: from IPCC
Global warming
Data source: from IPCC
Global warming
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China US Canada India Italy Japan
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CO
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O2/c
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O2/U
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CO2-GDP CO2-POP
2010 CO2 emissions for different countries
With the development of modern society, China is becoming the
largest CO2 emission country, except for CO2-POP.
Data source: from BP(the left one,2010) & IEA(the right one,2009)
Atmosphere pollution
Population
explosion
Increasing energy
consumption
Fossil fuel use Automotive
emission
Air pollution
Acid rain Photochemical smog Poor visibility
Atmosphere pollution
According Aaron van Donkelaar et al.’s research, the concentration of
PM2.5 in Eastern China is extremly high.
Data source: A. van Donkelaar et al.
Backgrounds
1.2 Solution —— Biomass energy
First generation biofuel
Second generation biofuel
Third generation biofuel
First generation biofuel
The first generation biofuels are derived from food crops (e.g. corn,
soybean) that are rich of sugar, starch, and lipids to generate bioethanol
and biodiesel. It may cause food security issues.
Second generation biofuel
The second generation biofuels are derived from agricultural and forestry,
waste, switchgrass, jatropha seeds, palm oil et al. to generate bioethanol
and biodiesel. Although they avoid the land competition with grain, the
collection and disposal of the biological waste are difficult.
Third generation biofuel
Microalgae is known extensively as the newly emerging biofuel feedstock,
which would be used to produce biodiesel, bio-oil, cogenaration with biogas,
et al.
Why microalgae ?
Advantages:
High area productivity;
Minimizes competition with conventional agriculture;
Utilizes a wide variety of water sources;
Recycles stationary emissions of CO2;
Compatible with integrate production of fuels and co-
products within biorefineries.
Contrast of several kinds of raw materials used for producing
biodiesel to meet the fuel need of transportation in China
Crops Annual
output
(ton/acre)
Oil content
(%)
Annual oil
output
(ton/acre)
Land
requirements
(104 acre)
Land
requirements
to cultivated
land (%)
Soybean 1.449 16 0.2320 27605.21 225.45
Corn 5.28 9 0.4752 13468.01 110.00
Castor 1.005 58-75 0.5829-0.7538 8490.88-
10979.59
69.34-89.67
Rapeseed 1.837 37.5-46.3 0.6889-0.8505 7524.71-
9290.51
61.45-75.86
Jatropha 4.8 50 2.4 2666.67 21.78
Oil sally beans 12 25 3 2133.33 17.42
Palm 7.4 50 3.7 1729.73 14.12
Microalgae 166.3 30 49.89 128.28 1.05
microalgae 166.3 70 116.36 54.98 0.45
Data source: from Tong Mu, Zhou Zhigang.
Development of microalgal biodiesel
Time Researchers Project key points
1950s Meiser , Oswald & Golueke Utilization of carbohydrate of algal cells to
produce methane via anaerobic digestion.
1978-1996 U.S. DOE’s NREL Aquatic Species Program pushed by the oil
embargo and energy price surges ($25 million).
1968-1990 U.S. DOE Marine Biomass Program: produce fuels to
substitute natural gas with macroalgae.
1990-2000 MITI Japan The Earth Update Technology Research Plan:
photobioreactor.
2006-now GreenFuel、Livefuels 、Shell、Chevron、PetroSun、AlgaeLink、Diversified、Solazyme et al.
Fully launched the biofuel production from
microalgae.
2000-now
in China
Research institution: Tsinghua University, East China University of Science
and Technology, CAS, SJTU, Xiamen University, et al.
Enterprise: ENN, SINOPEC, Gloden Race Group Co., Ltd. et al.
Time Incidents
1969 LCA was derived from the resource consumption and
environmental analysis of beverage bottle at Coco-
Cola Company.
1990s Methodology of LCA was gradually consummate in the
promotion of SETAC.
1996 LCA was brought into ISO (ISO14000).
1997 ISO14040, 14041, 14042 and 14043 were issued.
Business software SimaPro 7, GaBi 4 et al.
Freeware GREET, GHGenius、TRACI、EIO-LCA、Tsinghua-
CA3EM
1.3 LCA of biofuels
LCA (Life cycle assessment) is a “cradle-to-grave” analysis for accessing
the resource use and environmental impacts and tradeoffs of industrial
systems and processes.
Application of LCA of biofuels
Corn
Wheat
Cassava
Switchgrass
Soybean
Rapeseeds
Jatropha seeds
Bioethanol
Biodiesel
Methanol
Biogas
Vehicle use
WTT TTW
1.4 Research questions
Microalgal biodiesel
Energy consumption
???
Environmental impacts
???
Water
use
???
2 Research methodology
Culture
Harvesting
Extraction
Conversion
Biodiesel
Water & nutrients
recycle
Aftertreatment
Remnants Fish feed
Glycerin
Anaerobic
digestion
Biogas
Electricity generation
Export to the grid
Life cycle boundary
Life cycle boundary of microalgal biodiesel
Inventory analysis
Parameters units ORP 1 ORP 2
Length m 150 190
Width m 10 20
Depth m 0.3 0.3
Hydraulic mean depth m 0.28 0.28
Pond volume m3 994 2651
Mean liquid velocity m/s 0.3 0.3
Residence time day 10 13
Flue gas m3/day 1445 1926
Outlet flow rate m3/day 100 200
Culture ----- Open raceway ponds (ORP)
Algae species: Chlorella vulgris;
Growth rate: 0.017kg/(m2•day);
Concentration: 0.5 kg/m3(dry biomass);
TAG content: 14%;
CO2 concentration: 2.5%
Sunshine
Nutrients
CO2
Water
Algae
Inventory analysis
Dewatering
Microbial flocculation
Centrifugation
Solar energy
Oil extraction --- organic co-solvents
n-hexane;
Extraction efficiency: 90%
Co-products: extracted biomass
Oil conversion --- chemical transesterification
Methanol ;
Catalyst;
Ratio of methanol to oil: 56:1;
Extraction efficiency: 89%;
Co-products: glycerin
WTP (STP) energy consumption and GHGs among different BD blends
CD J-BD100 M-BD100-60
-40
-20
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20
40
CD J-BD20 M-BD2010
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CD J-BD100 M-BD1000
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WT
P (
ST
P)
en
erg
y
co
nsu
mp
tio
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MJ/
MJ
Total energy
Fossil fuel
Petroleum
GH
Gs:
gC
O2-e
q/M
J
CD J-BD20 M-BD200.0
0.2
0.4
0.6
0.8
1.0
WT
P (
ST
P)
en
erg
y
co
nsu
mp
tio
n:
MJ/
MJ
Total energy
Fossil fuel
Petroleum
GH
Gs:
gC
O2-e
q/M
J
3 Results and discussions
Characteristics of M-BD
-The highest total energy consumption
- The highest fossil fuel consumption
- Energy efficiency: 17.4%
- The lowest petroleum consumption
- The lowest GHG emissions
BD20 blends VS BD100
- Lower energy consumption
- Higher GHG emissions
WTP details for BD from jatropha and microalgae
Energy intensity stages for M-BD
- Algae growing
- Oil extraction
J-BD M-BD
0.0
0.5
1.0
1.5
2.0
2.5
3.0
Fo
ssil
en
erg
y
co
nsu
mp
tio
n:
MJ/
MJ
J-BD M-BD-0.15-0.10-0.050.000.050.100.150.200.25
Petr
ole
um
co
nsu
mp
tio
n:
MJ/
MJ
Actual value
J-BD M-BD
-300
-200
-100
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GH
G e
mis
sio
ns:
gC
O2-e
q/M
J
CO2 credits
BD T&D
Transesterification
Oil extraction
Feedstock transportation
Feedstock growing
Energy intensity stages for J-BD
- Jatropha growing
- Oil extraction
- Seeds transportation
CO2 credits (M-BD VS J-BD)
- Larger due to carbon fixation
ability.
3 Results and discussions
BD production
process Fossil fuel split (%) Petroleum split (%) GHGs split (%)
Jatropha seeds Microalgae Jatropha seeds Microalgae Jatropha seeds Microalgae
1 Feedstock phase 45.41 69.85 115.15 132.53 50.50 78.80
1.1 Process energy 1.55 22.31 10.69 41.82 1.95 38.79
1.2 Fertilizer 35.69 47.54 36.91 90.71 38.11 40.01 1.2.1 N 17.91 45.07 3.57 61.74 14.15 36.66 1.2.2 P 7.04 1.54 9.51 14.32 8.69 1.96 1.2.3 K 1.54 0.22 4.36 4.34 2.22 0.33
1.3 Pesticide 0.04 0 0.16 0 0.05 0 1.4 Herbicide 0 0 0 0 0 0 1.5 Feedstock
transportation 8.13 0 67.39 0 10.39 0
2 Fuel phase 54.59 30.15 -15.15 -32.53 49.50 21.20
2.1 Oil extraction -13.84 5.99 -107.73 -257.33 3.68 4.55
2.2
Transesterification 66.74 23.56 78.54 190.71 43.65 15.87
2.23T&D 1.69 0.60 14.04 34.09 2.17 0.79
Stage contribution of biodiesel production process for jatropha and microalgae
3 Results and discussions
Fossil fuel for M-BD are mainly used for algae growing. Petroleum are mainly
used for fertilizer production and process like dewatering. GHG emissions are
mainly concentrated on process energy and fertilizer production.
CD M-BD100 J-BD100 M-BD20 J-BD200123456789
Fo
ssil
en
erg
y
co
nsu
mp
tio
n:
MJ/
km
Vehicle operation
Fuel
Feedstock
Actual value
CD M-BD100 J-BD100 M-BD20 J-BD20
0.0
0.5
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1.5
2.0
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3.0
3.5
Petr
ole
um
co
nsu
mp
tio
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MJ/
MJ
CD M-BD100 J-BD100 M-BD20 J-BD20
-300-200-100
0100200300
GH
G e
mis
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ns:
gC
O2-e
q/M
J
WTW results for different fuel blends
3 Results and discussions
WTW characteristics for M-BD100
- The highest fossil fuel consumption
but lowest petroleum consumption.
- the lowest GHG emissions.
- Microalgae culture stage
account for 73.8% of total
fossil fuel.
BD20 blends may be a
better choice in the near
future.
3 Results and discussions
WTW results for fossil fuel contribution
The forms of fossil fuel are different in each fuel pathway.
- Petroleum is the main power source for diesel vehicle.
- Coal and NG are the main source for M-BD due to larger electricity use
and auxiliary materials consumption like methanol, fertilizer.
0%
10%
20%
30%
40%
50%
60%
70%
80%
90%
100%
Baseline (CD) M-BD100 J-BD100
Fo
ss
il fu
el c
on
trib
uti
on
: %
Coal Natural Gas Petroleum
3 Results and discussions
0.000
0.500
1.000
1.500
2.000
2.500
3.000
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4.000
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5.000
Baseline (GV) Baseline (CV) PHEV30 EV M-BD20
WT
W f
os
sil
fu
el
co
ns
um
pti
on
: M
J/k
m
Feedstock Fuel Vehicle Operation
WTW fossil fuel consumptions for M-BD20:
- High fossil fuel consumption at current technology level in China.
Strategies:
- Enhance production efficiency
- Improve the structure of electricity grid
- Apply the genetic modification of algae
WTW fossil fuel consumption results for different vehicles
3 Results and discussions
-100.00
-50.00
0.00
50.00
100.00
150.00
200.00
250.00
300.00
350.00
Baseline (GV)
Baseline (CV)
PHEV30 EV M-BD20
WT
W G
HG
em
iss
ion
s: g
CO
2-e
q/k
m
Feedstock Fuel Vehicle Operation
WTW GHG emissions for M-BD20:
- Could reduce the GHG emissions due to carbon fixation
via photosynthesis.
WTW GHG emission results for different vehicles
4 Conclusions and Prospects
WTP results of M-BD showed the highest fossil fuel consumption
but good performance on petroleum consumption and GHG emissions .
WTP fossil fuel is 10 times higher than that of conventional diesel;
WTP petroleum consumption is 77.7% lower than that of CD;
WTP GHG emissions is 185.5% lower than that of CD.
WTW results of M-BD showed the same trends with WTP.
BD100 do not consume any fossil energy and petroleum during
vehicle operation stage.
Microalgae culture stage account for 73.79% of the life cycle fossil
fuel consumption.
Suggestions and Prospects
Life cycle model of M-BD should focus on integration of other
technologies to reduce the process fossil fuel use.
Wastewater treatment
Biogas production from anaerobic digestion of residual algae
Nutrients recycle
……
Life cycle results are sensitive by many parameters.
Production efficiency
Lipid content
Energy structure
Electricity grid mix
……
The co-products allocation should be further investigated.
Thank you!