feasibility and environmental impacts of the...
TRANSCRIPT
Fuel Life Cycle
• Determine low lipid content cut-off where biodiesel production is unfavorable
• Perform techno-economic analysis on biodiesel from trap grease
• Analyze FER sensitivity to allocation methods for co-products
• Optimize distillation conditions to reduce sulfur content, producing ASTM
biodiesel
Proposed System to Integrate Biodiesel Production
Introduction
Megan E. Hums1, Colin J. Stacy1, Dr. Richard A. Cairncross1, Dr. Sabrina Spatari2
Drexel University, 1Chemical and Biological Engineering & 2Civil, Architectural, and Environmental Engineering 3141 Chestnut St. Philadelphia, Pennsylvania 19104: [email protected]
Conclusions
Feasibility and Environmental Impacts of the Production of Biodiesel from Grease Trap Waste
Biodiesel is a renewable fuel that can be produced from a variety of vegetable oils, animal fats, and waste greases. We utilize fats, oils, and greases (FOG) from commercial kitchen wastewater and convert it into biodiesel. Research at Drexel has demonstrated the technical feasibility of production of biodiesel from FOG; however, commercial feasibility is limited by the variability of its lipid content, which ranges between 2-30%, by volume. This poster presents a process for conversion of FOG to biodiesel.
• GTW-to-biodiesel is competitive with alternative biodiesels and low sulfur diesel
• Producing biodiesel under 10% lipid content is unfavorable due to process steam
requirement to separate lipids from grease
• Trap grease biodiesel FER is more favorable than soybean biodiesel >15% lipids
Acknowledgments Russell Reid * United States Department of Agriculture * Philadelphia Water Department
EPA P3 Design Award—SU-83352401 * GAAN RETAIN— Award No. P200A100117
EPA SBIR Grant—EP-D-14-09 * WERF Grant—U3R13
• Traditional biodiesels have high
negative impact due to
farming/harvesting of crops
• GTW does not include farming
step, but has a high impact due
to processing
• Impacts from GTW-to-biodiesel
process is dependent on lipid
content
Where, LHV= lower heating value, E=energy input, i=process step 1,2,3: 1=harvest/separation 2=conversion/purification 3=biodiesel transport
Future Work
TAG + Alcohol Biodiesel + Glycerol FFA + Alcohol Biodiesel + Water
Lipid content primarily affects steam requirement in separation step Below 10% lipids, process steam requirement increases steeply and FER decreases rapidly
Process steam requirements (Left ) From process analysis of each major process
step Here steam is produced by burning natural gas 𝐹𝐸𝑅 =
𝐿𝐻𝑉
𝐸𝑖𝑛𝑖=1
For >15%Lipids GTW Biodiesel has higher FER than Soybean Biodiesel For > 2% Lipids GTW Biodiesel has higher FER than Low Sulfur Diesel
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Fo
ss
il E
ne
rgy R
ati
o (
FE
R)
Lipid Content of Waste Grease (%)
Pro
ce
ss
Ste
am
En
erg
y R
eq
uir
em
en
t
(M
J-n
atu
ral g
as/M
J-b
iod
iese
l)
Separation of lipids from grease
Conversion of lipids to biodiesel
Purification of biodiesel
Methanol Recovery
Soybean Biodiesel
GTW Biodiesel
Petroleum Diesel
Fossil Energy Ratio (Right) FER = a ratio of fuel energy output divided by fossil energy input: High FER values desirable
Conventional Biodiesel Production:
• Refined vegetable oils (Soybeans)
• Contain primarily triglycerides (TAG)
• Expensive feedstock cost
• Cheap processing
Alternative Biodiesel Production:
• Waste fats, oils, and greases (FOG)
• Contain primarily free fatty acids (FFA)
• Low to no feedstock cost
• More complex processing
Challenges:
1. Waste grease produced in limited quantity and location-dependent
2. Lipid content in grease is highly variable; 2-30% total waste volume
3. Sulfur concentration inhibits production of ASTM grade biodiesel
Biodiesel from Waste Greases:
1. Utilizes a low-value liability to make a high-value product
2. Reduces the processing burden on waste management systems
3. Has the potential to fuel 1 million vehicles
Utilizing Waste Greases for Biodiesel Production
Waste greases challenge wastewater treatment processes and lead to clogging and
sewer overflows. Lipids can be extracted from waste greases for production of
biodiesel.
a) Grease Trap Waste (GTW) from commercial kitchen effluent
b) Sewage Scum (SS) from primary tanks at wastewater treatment plants.
Alcohol/Water Content Study
Bubble Column Reactor (BCR)*
Reactor developed at Drexel University for biodiesel production
Novel Biodiesel Technology
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FF
A c
on
ten
t (%
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Time (minutes)
Pure MeOH
90:10 MeOH:H2O
Pure EtOH
90:10 EtOH:H2O
Short-Path Distillation
Biodiesel is purified through distillation operating under a vacuum
(in collaboration with the USDA)
Crude FOG biodiesel is:
• Dirty
• High in sulfur content
• Difficult to separate
Short-path distillation purifies biodiesel:
• Under high vacuum: 1 mbar
• Low temperature:
• 115-190 °C @ 1 mbar
• 300-400 °C @ 1 mbar
• Reduces sulfur:
• Lipids: 300 PPM
• Crude: 201 PPM
• Residue: 776 PPM
• Biodiesel: 27 PPM
(ASTM grade = 15 PPM)
Life Cycle Assessment (LCA)
Method to evaluate energy usage and environmental impacts for a product
Operating Conditions:
• At 120 °C - Hotter than
boiling points of:
• Water (H2O)
• Methanol (MeOH)
• Atmospheric pressure
• MeOH rate 0.75 mL/min
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Un
rea
cte
d M
eth
an
ol R
ati
o
Tim
e t
o 9
5%
FF
A C
on
ve
rsio
n
(min
)
Normalized MeOH Feed Rate (1/min)
Time to 95% conversion (left axis)
Excess MeOH at 95% conversion (right axis)
BCR is Robust for:
• Waste Greases (FFA)
• Various Alcohols
• Elevated Water Content
Conversion/Excess MeOH Study
Biofuels are renewable due to the
recycling of biogenic Carbon Dioxide (CO2)
Achieves >95% FFA Conversion in less than 2 hours
Atmospheric boiling points:
• FAME: 344 °C
• FFA: 360 °C
• TAG: 884 °C
Harvest
Use as
Vegetable
Oil
Disposal
Distribute
CO2
Emissions
Acidic Oil
(FFA)
Crude
Biodiesel
(FAME)
MeOH &
H2O Vapor
(MeOH)
Vapor
FFA
+
MeOH
H2O
+
FAME
MeOH
H2O
Ris
ing
Bu
bb
les
Hot wall
Cold wall High
vacuum
Crude
Biodiesel
Biodiesel
Residue
Wipers
*Stacy, C. J.; Melick, C. A.; Cairncross, R. A., Esterification of free fatty acids to fatty acid alkyl esters in a bubble column reactor for use as biodiesel. Fuel Processing Technology 2014, 124, (0), 70-77.