2. Air pollution compliance costs often cited as an
obstacle in construction or operation of
biorefineries.
Costs of compliance with air pollution regulation
are added to the Geospatial Bioenergy Systems
Model (GBSM).
Parker, N., Tittmann, P., Hart, Q., Nelson, R.,
Skog, K., Schmidt, A., Gray, E., et al. (2010).
Development of a biorefinery optimized biofuel
supply curve for the Western United States.
Biomass and Bioenergy, 34(11),
3.
4. Existing work has focused on
technoeconomic assessments, resource
assessments and spatial modeling.
Spatially explicit models developing steadily
Concern over sustainability, need for further
study
High computational burdens
How to integrate environmental concerns
with cost-based modeling?
5. Previous GBSM Work
Engineering/Economic
Models of Biorefineries
Spatially Explicit
Resource Assessment
Supply Chain
Optimization Model
GIS-based
Transportation
Cost Model
Air Pollution Cost Data
Nonattainment Zone
Maps
7. Biochemical Lignocellulosic Ethanol
NREL 2011 Process Design (Humbird et al, 2011)
Fischer-Tropsch Diesel
Swanson et al. (2010)
FAME Biodiesel
Haas et al. (2006)
Corn Ethanol
Parker et al. (2010) based on ANTARES 2009
model.
8.
9. Dominant regulation is Clean Air Act, which sets
standards for maximum allowed air pollution levels
and requires state/local compliance.
Areas exceeding maximum are in “non-attainment”
Main pollutants of interest:
PM2.5 – Combustion byproduct, responsible for cancer,
heart disease, lung disease
Nitrogen Oxides (NOx) – Ground-level Ozone precursor
11. PM Control
Dry
Electrostatic
Precipitator
NOx Control
Selective
Catalytic
Reduction
Includes 60%
Indirect costs.
All values in 000’s of 2002 US Dollars.
12. Air pollution control costs added to fixed and
capacity dependent costs (ai and bi
respectively), if the facility is sited in a
relevant nonattainment area.
13.
14. Corn ethanol limited to 15 Billion gal/yr (RFS2
Max)
Switchgrass is planted on 50% of both
cropland idle and cropland pasture acres
Forest from federal lands is not allowed
Fuel demand constraint requires each
terminal receive its fair share of each biofuel.
Blend wall raised to 15%
15.
16.
17.
18.
19. Small reduction in production
volume & system profit.
Bio-refineries in non-attainment
areas reduce capacity slightly, those
outside increase slightly.
In one instance (Phoenix, AZ) a new
bio-refinery opens outside of a
nonattainment area, where none was
under baseline conditions.
20. Air pollution control costs appear to have a
relatively small effect on net biofuel system
production, price and spatial distribution.
0.3% Reduction in total volume produced at $3.10
ethanol selling price.
MSW is the most affected feedstock.
Monetizeable environmental considerations
can be incorporated into profit-maximizing
optimization modeling
21. AHB-PNW Study of biofuel production from
hybrid poplar in OR, WA, ID, CA
Add agent choice at feedstock producer and
biorefinery operation level
BCAM feedstock modeling
Generate nationwide spatial air pollutant
emissions inventory
29. 50% of paper currently landfilled can be separated
for fuel production
75% of wood currently landfilled can be separated
for fuel production
75% of yard wastes currently landfilled can be
separated
50% of food wastes currently landfilled can be
transitioned to a source separated collection
method
75% of the remainder of of the organic fraction of
MSW (including plastic, etc) can be used for fuel
production
Only biogenic fraction is reported in the results
30. Only consider non-irrigated switchgrass
Yields from ORNL study
We use upland yields
The study predicts the 95 percentile of
switchgrass yields based on field trials.
Land base assigned based on NASS statistics
Cropland (Idle) – 25% or 50%
Cropland (Pasture) – 25% or 50%
Pastureland – 0% or 5%