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Formation of Fuel-Grade Ethanol B.
Kaspers, J. Koger, R. Gould[1],
A. Wossink[2],
R. Edens[2],
and T. van Kempen Summary The objective of this project is to investigate the
application of gasification technologies to the treatment of swine waste for
the ultimate production of fuel-grade ethanol.
This waste treatment system would reduce the negative environmental
impact of current manure management systems.
The research objectives are: 1) to develop and test a system for harvesting
swine manure in a form dry enough to be used as a gasification feedstock, 2) to
establish the feasibility and the gasification conditions for the swine
waste/amendments feedstock, 3) to characterize the end products of gasification
(ethanol and mineral ash) and their potential markets, and 4) to conduct a
rigorous economic analysis on the entire swine manure management model to
determine its feasibility along with the factors that promote or impede its
implementation. Introduction Ethanol production (primarily via fermentative methods) from
crops and other “renewable” biomass sources has received much attention
recently, but the current approach has problems. Mainly, crop-based feedstocks are subject to seasonal
fluctuations in supply, ultimately limiting ethanol generation. Such feedstocks necessitate either lengthy
storage of the perishable plant materials or stopping ethanol production
altogether during the off-season.
Another dilemma faced is that some of the feedstocks currently used in
ethanol production (e.g. corn stubble) have a greater value elsewhere (e.g.
fertilizer). More specifically, the
energy cost in harvesting these feedstocks (e.g. corn stubble) as well as their
lost value as soil amendments makes ethanol production costly to farmers
(Pimental, 1992). Animal manures avoid many of these problems because they are
a truly renewable feedstock. The quantity of swine manure produced in the U.S, estimated
at 5 billion kg dry matter per year, is sufficient to contribute substantially
to ethanol supplies. Assuming a
conversion efficiency of 40%, there is a theoretical ethanol yield of 500
million gallons per year. North
Carolina is the second largest hog-producing state within the U.S. with a swine
population large enough for gasification technology to be feasible. Thus, ethanol production of 80 million
gallons per year should theoretically be attainable. The most recent RFA
(Renewable Fuels Association) Ethanol Report (May 11, 2000) concludes that replacing
corn with less expensive feedstocks will result in substantial reductions in
ethanol production costs. Gasification of biomass has received much attention as a
means to convert waste materials to a variety of energy forms (i.e.
electricity, combustible gases, synfuels, various fuel alcohols, etc.). Gasification is a two-step, endothermic
process in which solid fuel is thermochemically converted into a low or medium
Btu gas. Pyrolysis (Step 1) of the
biomass is followed by either direct or indirect oxygen-deprived combustion
(Step 2) during the gasification process.
This process converts raw biomass into a combustible gas, retaining
60-70 % of the feedstock's original energy content. Thermochem’s steam reformer is the system we are investigating to
gasify our feedstock because this type of gasifier produces a hydrogen-rich,
medium-Btu fuel gas. This gasifier
design percolates superheated steam through an indirectly heated inert
fluidized bed of sand or a mineral material.
The organic feedstock injected into the bed undergoes a rapid sequence
of pyrolysis and vaporization reactions.
Higher hydrocarbons released among the pyrolysis products are steam
cracked and partially reformed to produce low molecular weight species. This process produces a gas with nearly
immeasurable environmental emissions of NOx, SOx, CO, and
particulates. The main reason this particular gasifier design is favored is
because of its hydrogen to carbon ratio (2:1) is ideal for ethanol synthesis. A
recent cost and performance analysis of biomass (i.e. wood) gasification
systems for combined power generation indicated that such a steam system
(Battelle Columbus Laboratory) had the lowest capital cost and product
electricity cost (Craig and Mann, 1997).
There is an intensive effort, especially in North Carolina,
to develop a better waste management strategy.
The ultimate goal of this project is to eliminate the land application
of lagoon effluent. The elimination of this waste via gasification would
abolish the need for land application of waste. The primary obstacle to overcome in this project is
converting the swine manure into a suitable feedstock for gasification. Factors such as moisture content, density,
and transportation requirements must be investigated. The most common waste systems currently employed, the lagoon (1%
Dry Matter (DM)) and slurry basin (10% DM), do not produce a waste stream which
makes for a suitable feedstock for gasification and thus alternative waste
management systems must be developed.
When the appropriate feedstocks are selected, the gasifier will be
engineered to maximize product gas yields. Results and Discussion Initially, fresh fecal samples were collected from our swine
research facility (Jan. 2000) to corroborate literature findings that claim
swine feces is typically 20-30% dry matter.
The mean DM for the fresh fecal samples obtained from grower/finisher
pigs fell within the reported range at 28.6%.
These DM values were not significantly (p= .26) different between the
various sized (50-200 lbs.) grower-finisher pigs. The mean energy value of the samples was found to be 4361
cal/g. However, the energy values
displayed a decreasing trend as body size increased (p= .16). This trend can be explained by the increase
in digestion time that occurs with an increase in the animal’s body
weight. In comparison to other
potential feedstocks for gasification (Table 1), swine waste has a high enough
energy value to make gasification feasible.
|
Material
|
Energy content (cal/g) |
Corn cob |
4928 |
|
Birch
wood |
4613 |
|
Swine
waste |
4361 |
|
Corn
straw |
4253 |
|
Wheat
straw |
4247 |
|
Rice
straw |
3903 |
A thorough investigation of existing swine waste management
systems within the U.S. suggests a low probability for obtaining feces with a
desired DM content for steam reformation (60-80%) from currently employed
systems (most commonly the lagoon and the slurry basin). Some alternative housing systems like hoop
structures (found primarily in the Midwest) and dry waste systems (Hog high-rise
in Ohio) have been examined. Samples
were obtained from three hoop facilities in Indiana because they utilize a deep
bedding system which could yield a dry waste.
Analysis of these samples determined that this waste stream was
unsuitable as a possible feedstock for steam reformation with a mean dry matter
content of only 41%. Analysis of samples for DM and energy content from the
high-rise in Ohio will be conducted in the future.
European swine research facilities have shown that a
conveyor belt collection system seems favorable for obtaining a drier waste
stream. Thus, we designed a small-scale
(single pen) belt unit with plans to construct a large-scale (100 pigs) model
in the summer of 2000. These units
should provide us with a suitable feedstock for steam reformation without
having to employ additional drying mechanisms.
Initially, we set up a housing structure to simulate a belt
system, in order to measure ammonia emissions.
The system consisted of grower/finisher pigs housed within a pen on
tenderfoot flooring with PVC sheets slanted six inches below it, allowing the
urine to drain away from the manure. This structure was housed within one of
our enclosed chambers where ammonia levels were monitored using an FTIR
(Fourier Transform-Infrared) spectrophotometer. There was no increase in ammonia emission over the three days the
animals were housed there, in contrast to the usually observed increase in
ammonia emissions. This finding
suggests that an innovative manure collection system like the conveyor belt
will dry the manure as well as reduce odors within the swine housing facility,
making it a more environmentally friendly system.
Next, we built a small-scale model, consisting of one pen
with tenderfoot flooring and a plastic belt running below it. Our first pilot trial was with
grower/finisher pigs averaging 31 kg.
Although this system required improvements, a DM of 60% was achieved,
indicating the system could produce a feedstock for gasification. This trial also examined DM as a reflection
of times between collections off the belt.
Dry matter seemed to be the highest when the belt was moved one foot
each day over a three-day period.
Further investigation into the collection periods will be examined in
subsequent pilot trials after which a larger scale unit will be built.
Implications
Our research thus far has shown that swine manure can be a suitable feedstock for gasification. The belt system (an alternative waste management system) has the potential to dry the swine waste to more than 60% DM. Investigation into possible amendments of North Carolina's cash crop wastes (i.e. peanut shells, wood shavings, wheat straw, etc.) remains a possibility for producing an even drier feedstock. Alterations to the steam reformer will be performed to optimize product gas composition for ethanol production and to allow for flexibility in feedstocks (with or without amendments, varying dry matter contents, etc.). Also, the ash product produced in the steam reformer will be examined for use as a mineral source in animal feeds or as a fertilizer. The final conclusion regarding the feasability of gasifying swine waste will be dependent upon the economic analysis of the entire housing and gasification system. A decision support system (DSS) will be developed that stimulates and optimizes the whole chain from animal production to manure spreading or processing. The system will assess the logistics, economics, and environmental effects for each of the elements of the chain. An economic/environmental sensitivity analysis of gasification as a manure processing technology will be performed by changing the options (such as subsidies on ethanol), constraints (particularly the regulatory context), and model assumptions step by step. The results will be compared to an environmentally sustainable system based on current technologies, waste disposal by land application at agronomic rates that avoid eutrophic consequences.
Literature Cited
Craig, K.R. and
Mann, M.K. “Cost and Performance Analysis of Three Integrated Biomass
Gasification Combined Cycle Power Systems”. DOE BioPower Program Technical
Reports, Aug. 1997.
Pimental,
D. 1992. Energy inputs in production agriculture. Energy in World
Agriculture. ed. R.C. Fluck. Amsterdam; Elsevier. Pgs. 13-29.