
Economics is about using
what you got to get what you want the most. Georgians want clean
water and air, efficient and sustainable use of natural resources,
and economic development opportunities. Can Georgia's food and
fiber production industries contribute to our energy supplies
in a manner that is helpful to the environment while adding
value to Georgia's economy? This was the underlying question
the Center for Agribusiness and Economic Development of the
College of Agricultural and Environmental Sciences attempted
to illuminate in two recently released economic studies.
Powering Diesel Engines
off the "Fat of the Land"
Georgia agriculture currently
is among the leading states in animal production (poultry) and
vegetable oil production (peanuts and soybeans imported for
poultry). In addition, Georgia has a large population that uses
vegetable oils in its many restaurants and food service industries.
Unfortunately, Georgia also is on some of the national list
for air quality problems. The Atlanta metro area is not currently
in compliance with federal air standards and several other metro
areas are close to being placed on the non-compliance list.
The combination of abundant vegetable oils and animal fats in
Georgia and growing air quality concerns led the Center to conduct
a detailed study of the economics of producing cleaner burning
diesel fuels from cooking oils and animal fats.
The technology of converting
vegetable oils and animal fats into biodiesel is a well-established
process. The most commonly used process involves combining the
fat/oil with methanol and sodium or potassium hydroxide. This
process creates four main products - methyl ester (biodiesel),
glycerin, feed quality fat and methanol that is recycled back
through the system. The primary product, methyl ester, is better
know as biodiesel while the glycerin and fats can be sold as
well. The methyl ester process is very energy efficient in that
for each unit of energy required by the process approximately
3.2 units of energy are gained. Ethanol, which enjoys federal
tax advantages and mandated use in many states as a gasoline
engine fuel additive, has only a 1.25 returned energy ratio.
The predominant feedstock for ethanol is starch-based fuels
such as corn. Since the Midwest is the dominant corn producing
region in the world and several new ethanol plants have begun
production in the Midwest, it was determined that biodiesel
production would be more competitive under current technology
in Georgia than would ethanol.
Major feedstocks currently
available in Georgia include soybean oil, cottonseed oil, peanut
oil, spent restaurant fats and rendered poultry fats. It appears
that there is an adequate supply of oils and fats available
in or near Georgia to produce biodiesel as the total estimated
production in Georgia is close to 1 billion pounds annually,
of which approximately 334 million pounds were estimated to
be available for alternative use.
The Center secured the services
of Frazier, Barnes & Associates of Memphis, TN, a consulting
firm specializing in vegetable oil processing, to assess the
capital cost of various sized biodiesel production facilities.
Four different sized biodiesel production plants were evaluated
for the most economical size plant. It appears the most economical
sized facility is one that produces about 15 million gallons
of biodiesel per year. Such a plant would cost about $9.6 million
to construct.
The actual equipment and facility
costs of producing bioiesel were found to be a relatively small
proportion of the total costs of production. The feedstock cost
is the dominant factor in determining final production cost.
Total annual operating and fixed costs for a 15 million gallon
plant would be about $23 million. Actual estimated operating
cost and fixed cost are about 25 percent of total cost while
feedstock acquired at $0.15 per pound average cost would represent
75 percent of total cost. Clearly, the availability of low priced
feedstocks is imperative to providing the most competitive biodiesel
product.
Vegetable and animal fat prices
vary depending upon supply and demand for each of the products
and also upon the overall supply and demand situation for the
entire fat/oil complex due to substitutability between products
in some uses. In general, the vegetable oils have a higher unit
value than do the animal fats. The recent historical range of
prices for the leading potential feedstock sources is from $0.06
to $0.50 per pound. A 15 million gallon plant in Georgia would
use approximately one-third of the estimated available feedstock
supply produced in Georgia.
The cost of producing a gallon
of methyl ester depends upon the average cost of the feedstock.
If feedstock costs $0.10 per pound, production costs were estimated
to be about $1.11 per gallon. If feedstock costs rise to $0.25,
costs soar to $ 2.21 per gallon. At current average feedstock
prices of about $0.15, production costs would be near $1.48
per gallon (Graph 1). In late 2003 diesel fuel production prices
were about $.83 per gallon. Thus biodiesel is not competitive
with petroleum-based diesel at current prices. However, seldom
is biodiesel used in the pure form. Most commonly it is mixed
with petroleum diesel to form either a 2 or 20 percent blend.
Thus, the added cost to the blended price would be about one
cent at current diesel prices for a 2 percent blend and about
13 cents for a 20 percent blend.
The economic and environmental
benefits to Georgia were also found to be significant. Of the
polluting emissions from diesel engines running regular diesel,
all but Nitrogen Oxides (which were unchanged) were found to
be reduced by 10 percent or more when compared to those using
a 20 percent biodiesel blend. So the likely environmental impacts
of replacing even 75 million gallons (total output of a 15 million
gallon biodiesel plant if blended at 20%) of Georgia's estimated
1.5 billion gallon diesel market could be significant. In addition,
the economic impact of one 15 million gallon/year Georgia biodiesel
plant would be an additional $34 million per year in output
in the Georgia economy, 132 more jobs, and an additional $4.5
million in Georgia tax revenues produced per year.
Lacking government mandates
or subsidies, a feedstock cost of 10 cents per pound or less
is needed for biodiesel to be cost competitive at current diesel
fuel prices. However, the difference in production cost is within
a range that could be managed by a Georgia policy that would
subsidize the production process and/or eliminate state taxes
on Georgia produced biodiesel utilizing Georgia produced feedstock.
The result could be good for Georgia's economy and environment.
Making Electricity From Poultry Poop?
According to the Energy Information
Administration, Georgia's electrical energy supply relies primarily
on fossil fuel and nuclear power. In 1999, 64% of electrical
power was generated by coal, 27% by nuclear, and 4% by natural
gas and petroleum fuels. Hydroelectric sources generated 2.3%
of Georgia's electrical supply. Other fuels, such as municipal
solid waste and agricultural biomass, generated the remaining
2.6% of electricity.
Research suggests the generating
potential from non-hydro renewables, particularly biomass, could
be much greater than current use trends. In addition, the potential
environmental and economic benefits may exceed traditional generation
methods. Accordingly, the possibility of using Georgia's biomass
resources as a potential fuel source has the interest of Georgia's
farmers, the electric power industry, environmentalists, as
well as the legislative community.
The main concern relies on whether biomass-fueled
power generation can be economically feasible, given current
generation technology. As a result, the Center for Agribusiness
and Economic Development, at the University of Georgia College
of Agriculture and Environmental Sciences, set out to determine
the feasibility of electrical power generation from Georgia's
farm produced biomass resources with partial funding by an appropriation
of the Georgia legislature. This study analyzes four generation
technologies in use today: direct-fire, co-fire, gasification,
and pyrolysis. To determine the economy of scale impact, each
technology was evaluated for three facilities that increased
in size, biomass input used, and electricity generated.
In order to evaluate the potential
for farm-produced biomass in electrical production, the supply
of biomass had to be evaluated by county. Biomass is not a dense
product and therefore cannot be transported across great distances.
So supplies within relatively small areas are important to the
feasibility of an electrical plant fueled by biomass. The supply,
likely cost, and fuel characteristics of 14 biomass farm produced
products were estimated. Most of the biomass products evaluated
were by-products of a primary enterprise (cotton stalks and
gin trash, peanut and pecan hulls, poultry litter, pine bark,
wood harvest residue and chips, corn stalks and excess grass
hay) while a few were crops that have been suggested for energy
production (switchgrass and kenaf). Of the 14 biomass products
evaluated, 2 were found to have a lower BTU cost than the lowest
cost fossil fuel, coal (pecan hulls and gin trash); an additional
3 were found to have lower BTU cost than the second lowest cost
fossil fuel, natural gas (pine bark, poultry litter, peanut
hulls; and finally an additional 4 were found to have lower
BTU cost than petroleum, the highest fossil fuel source (wood
chips, wood residue, grass hay, cotton stalks). The estimated
total farm produced biomass expressed in BTUs per county is
shown in Figure 1.
The next step in the study
was to evaluate different technologies for converting biomass
to electricity and the economies of size in each technology.
The four types of technology ranged from directly burning biomass
to a more experimental system called pyrolysis. A brief explanation
of the process studied and the three size operations of each
follow.
Direct Fire- Direct fire combustion
involves the burning of biomass with excess air, producing hot
flue gases, which then produce steam in the heat exchange section
of a boiler. The steam is then passed through a steam turbine
generator to produce electric power. The direct fire technology
was evaluated for 120, 200, and 400 wet tons per day (WTPD)
of biomass input. Total capital for equipment and buildings
t for the three size plants were $5.1, $7.2, and $11.6 million
respectively.
Co-fire- Co-firing refers
to the practice of introducing biomass as a supplementary energy
source in high efficiency boilers. The flue gases are then used
to produce steam and/or electric power as in a direct fire technology.
Co-fire is used when either the moisture content of the biomass
is high or when the supply of biomass is intermittent. In each
of the co-fire cases the biomass fuel supply deficit was supplemented
with enough natural gas, measured in thousand cubic feet (MCF),
to generate the same amount of power as in the direct fire cases.
The corresponding levels of fuel are 60, 100, and 200 WTPD of
biomass and 523, 872, and 1744 MCF of natural gas for Case 1,
2, and 3, respectively. Total building and equipment cost for
constructing the three units were estimated to be $4.6, $6.1,
and $9.8 million respectively.
|
Gasification- Gasification
for power production involves the chemical conversion
of biomass in an atmosphere of steam or air to produce
a medium or low calorific gas. This "biogas"
is then used as a fuel in a power generation plant that
includes a gas turbine generator for power production
and a waste heat boiler for steam production. The steam
can then be used to generate power. For this study the
only heat available for power generation is assumed to
be the heat content of the biogas. All other heat generated
by the gasification process is used to dry the feedstock.
The gasification technology was evaluated for 160, 267,
and 533 WTPD of biomass input. Total building and equipment
costs were $19.1, $28.6 for cases 1, 2 and 3, respectively.
Pyrolysis- Pyrolysis
is a process by which biomass is heated in the absence
of oxygen. For this study the feedstock is assumed to
be dried via heat generated by the pyrolysis process.
As a result the biomass decomposes to generate mostly
vapors, aerosols, and some charcoal. After cooling and
condensation, a transportable dark brown liquid oil is
formed which has approximately one half the heat content
of conventional fuel oil. Bio-oil, is approximately 20%
heavier than water and is both transportable and storable.
The bio-oil can be fed directly to a turbine and combusted.
Both power and steam can be generated from this process.
Energy from all bio-oil produced is saleable. Commercialization
of the pyrolysis process is in its initial stages, although
technology suppliers typically have small-scale pilot
plants and are working to build full size facilities.
The pyrolysis process assumes biomass inputs at 160, 320,
and 480 WTPD for case 1, 2, and 3, respectively. Capital
cost was estimated to be $13.9, $23.0, and $31.8 million
respectively.
|
 |
Each production technology was modeled to obtain
the estimated cost of producing electricity per Kilowatt hour
(KwH). The biomass feed stock cost represents the largest portion
of the production cost and thus was evaluated at three cost levels
of $10, $20, and $35 per ton of wet biomass. The results of the
cost analysis are summarized in Figure 2. The cost analysis also
includes a 1.8-cent per kWh federal tax incentive for electricity
produced from most biomass fuels including poultry litter. The
estimated production costs are compared to the average 1999 revenue
per kWh for all electricity sold (6.2 cents) and the marginal
cost of producing electricity by conventional means (2.9 to 3.2
cents -1998 Annual Energy Outlook). The marginal cost comparison
is the appropriate market price for an independent electric generator
as it is the price at which electricity could most likely be sold.
As can be seen, only the large-scale
gasification unit with the lowest biomass price comes close
to a competitive situation without further subsidy or incentive.
However, some states offer additional tax incentives for biomass
production. In addition, most states, including Georgia, allow
power companies to collect premium payments from consumers wishing
to consume "green" power. Such green power programs
allow those consumers who wish to support renewable fuels a
financial option. Unfortunately, biomass is not included in
the current green power programs in Georgia.
This study indicates that
large gasification units are currently on the verge of becoming
competitive and that Georgia has sufficient farm produced biomass
in several location to power such units. Each large-scale gasification
unit can produce about 167 million kWh per year, enough to power
more than 140,000 homes. In all, Georgia has enough farm-produced
biomass to supply 50 such generating plants. Farm produced biomass
could supply about 12% of the total electrical demand in Georgia
or 31% of the State's residential demand. Each biomass gasification
power plant was found to add about 10 million dollars to the
local economy either through direct sales or indirectly through
its impact on the local economy, 69 total jobs and over $700,000
in new tax receipts. While not calculated for this study, further
benefits are likely to be derived from replacing non-renewable
energy sources with renewable sources grown in Georgia. Furthermore,
the so called "green house emissions" of power produced
from biomass can be less than those produced from fossil fuels.
Economic development, a cleaner environment, and sustainable
natural resource use - that's killing three birds (and their
poop) with one stone! Or as an economist would say - using what
you got to get what you want the most!
|
|
Figure 2.
Electrical production cost
comparisons for biomass in alternative technologies and
sizes of operation with 1.8 cent federal credit. |
John C. McKissick
Professor and Director of Center for
Agribusiness and Economic Development
top
|
|

Section 10816 of the Farm
Security and Rural Investment Act of 2002 establishes the country
of origin labeling (COOL) requirement which retailers and suppliers
of farm products are mandated to comply with effective September
30, 2004. Interim guidelines for the COOL program have been
released in October last year which generated a lot of discussion
among government and industry representatives. Last month, the
U.S. Department of Agriculture (USDA) released a set of proposed
regulations for the implementation of COOL which shall be finalized
and approved before its implementation date next year.
The USDA Proposed COOL Regulations
The COOL law covers a wide range of agricultural
operations that include perishable agricultural commodities
(fresh and frozen fruits and vegetables), muscle and ground
meat (beef, pork and lamb), seafood (fresh and frozen, farm-raised
or wild caught), and peanuts, which is largely grown in the
state. The law requires that these products be labeled at retail
to indicate their country of origin. The recently released regulations
stipulate the following specific requirements/provisions:
- " Labels for fish and shellfish must
distinguish between wild and farm-raised fish and shellfish;
- " Exclusion from the mandatory labeling
requirement of covered commodities if these were ingredients
in a processed food item (such as bacon, orange juice, mixed
nuts and fruit/vegetable party trays)
- " Exemption from this requirement of
food service establishments, such as restaurants, lunchrooms,
cafeterias, food stands, bars, lounges and similar enterprises.
Moreover, USDA's proposed
regulations clarify that a covered commodity can only bear a
"United States country of origin" declaration under
the following conditions applicable to certain farm commodities:
- Beef: covered commodity must be derived exclusively
from animals born, raised and slaughtered in the United States,
including animals that were born and raised in Alaska or Hawaii
and transported for a period not to exceed 60 days through
Canada to the United States and slaughtered in the United
States;
- Lamb and Pork: covered commodity must be
derived exclusively from an animal that was born, raised and
slaughtered in the United States;
- Farm-Raised Fish and Shellfish: Covered commodity
must be derived exclusively from fish or shellfish hatched,
raised, harvested and processed in the United States;
- Wild Fish and Shellfish: Covered commodity
must be derived from fish or shellfish harvested in the waters
of the United States or by a U. S. flagged vessel and processed
in the United States or aboard a U.S. flagged vessel.
- Perishable Agricultural Commodities and Peanuts:
Covered commodity must be derived exclusively from produce
or peanuts grown in the United States.
The USDA's proposed rule also
outlines requirements for labeling blended products as well
as products of mixed origin, including products produced in
both local and foreign markets. There are also record keeping
requirements for retailers and suppliers that have been established
by the recently released set of COOL regulations.
The Economics of the COOL Law
The original intent of this legislation is
for U.S. farmers to gain financial benefits from the mandatory
labels, which are envisioned to encourage consumers to choose
domestic over imported products. A rise in demand for local
farm products would lead to an increase in the prices of these
domestic commodities, which consequently would increase their
market share at the expense of imports (Kuchler, USDA-ERS).
Analysts, however, contend
that such could be a lofty expectation. Specifically, the Food
Marketing Institute (FMI) claims that the consumer surveys they
conducted during the last 20 years do not really establish country
of origin labeling as a factor in the consumers' grocery shopping
decisions. Instead, quality, value and convenience are the commonly
cited concerns of grocery shoppers surveyed. Recently, FMI commissioned
Wilson Research Strategies to conduct a survey on the COOL Law.
The results, which were released in mid-October, indicate that
53 percent are not confident that the law will increase sales
of domestic products.
The apprehension over the
less encouraging market effect of the COOL law is compounded
by USDA's estimates of projected costs associated with the implementation
of the mandatory labels. These expenses are associated with,
among others, modifying record keeping systems, segregating
products, printing labels, employee training, and performing
COOL audits. Each business facility of affected farm business
will incur estimated costs ranging from $180-$443 for producers,
$4,048 - $50,086 for intermediaries (such as handlers, importers,
processors, and wholesalers), and $49,581-$396-089 for retailers.
No Choice!
Despite the strong criticisms of this "severely
flawed law," the COOL law will take into effect by the
end of September next year. Affected farm businesses do not
really have a choice but to comply with the regulations. According
to the law, non-compliant businesses will be fined up to $10,000
if the labeling requirement has been willfully violated even
after a 30-day warning has been issued to the violators.
This labeling law that brings
about unexpected cost burdens, along with uncertain market and
financial gains, could threaten the survival of small growers
and ranchers as well undermine the competitiveness of U. S.
products in international markets. These unfortunate consequences,
as predicted by most economists, would likely prevail unless
the labeling law is either repealed or replaced with a new law
that would ensure that more realizable financial gains would
outweigh the inevitable costs of compliance.
Note: This compilation/summary
is based on press releases, economic studies and commentaries
from the websites of the Food Marketing Institute (http://www.fmi.org)
and the Economic Research Service of the U. S. Department of
Agriculture (http://www.ers.usda.gov).
Cesar L. Escalante
Assistant Extension Professor
top
|