Jan 12, 2012 | Diet
This white paper was written for
GHSP Inc. to support the PBS series:
Martha Amram
January 2012
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For an introduction to energy use in food, see our Overview & Tips
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Of the many items we consume each day, food is one of the largest,
at approximately 14 percent of annual U.S. energy consumption [1].
This short paper describes the calculations behind the personalized
energy-diet calculator prepared by WattzOn that helps users
understand the relative amounts of energy use to grow, process and
transport their food.
The goals of the energy-in-food calculator are:
· To provide information and create awareness about the role of
food in our daily energy use.
· To provide suggestions as to how an interested consumer can
reduce energy use by making alternate food choices.
· To provide information in a manner that engages consumers.
We have benefited from reviews of earlier drafts of this paper,
and from user experience with our web tools during the summer and
fall of 2011. This has shown us that food choices interact with a
host of other issues, including emotions about the nature of the
U.S. food industry, carbon calculations and perceptions about
personal diet and food choices. For example, Americans eat a lot
of sugar, and some reviewers have reacted to energy-in-food
calculations with judgments about this food choice.
Based on this early experience, we have focused the calculator and
this research note on the energy implications of food choices - a
single dimension of a multi-dimensional issue. There are many
elements of food and agriculture policy that affect climate change,
diet and health, but these are beyond the scope of this work. Here,
we maintain a narrow focus on personal energy use.
For most products and services, the item requiring the least amount
of energy to make is also the item with the smallest greenhouse gas
(GHG) emissions. This is not true for food. A diet heavy in beef
will have higher carbon content than a vegetarian diet, but the
energy required to make the two diets will not differ as much. An
important source of carbon emissions in diet is animal-based
foods. Animals themselves are producers of a significant amount of
emissions as they digest food. Food processing the livestock and
poultry does not require much more energy than processing in other
food groups. So while eating less meat clearly reduces the CO2e
(carbon dioxide equivalent) emissions, eating less meat does not
stand out as a key action to reducing energy use.
At the WattzOn website, users can enter data about their diet to
obtain estimates of energy use and CO2e emissions from the mix of
foods. Users adjust their food choices via a slider, moving the
icon right or left to increase or decrease the number of daily or
weekly servings of the food group.
The food groups shown are: beef, pork, poultry, fish, dairy,
grains, fruits and vegetables, and sweets. We provide the increased
detail on animal-based protein sources, because the relative energy
impact versus CO2e impact varies sharply by protein source.
Users can enter data for a household or for an individual and
display in either mode, as well. The results are shown in terms of
BTUs (thermal unit) per household per year. The results can also be
displayed in terms of pounds of CO2e.[2]
The diet tool calculations are based on U.S. economy-wide data on food consumption and food production. The basic concept is to match consumption and production by food type, thus obtaining the total energy used, to produce a total number of calories, which is then divided to obtain the energy required to produce a single calorie of that food type. With user information, via the sliders, the annual energy use from diet choices can be estimated.
The USDA reports the average number of calories per capita per
day by food type and the average number of servings per capita per
day by food type.[3] (The serving metric - cups, ounces, teaspoons
- is also provided.) These data are reported each year, and to
match the data on energy used in food production, calorie data from
2002 is used. There has been a slight downward trend in the number
of calories and servings in recent years, but little year-to-year
variation.
One of the important aspects of the USDA data is that it is "loss
adjusted," meaning that food production and calories are net of
waste. For example, if 150 calories of a food type are produced,
but only 100 calories are available for use by the consumer due to
waste, calculations that ignore waste will be significantly off.
Food data net of waste is not always available and makes studies
difficult to compare.
The Economic Research Service (ERS) of the USDA considers these
loss adjustments important, as the adjusted data more closely
reflect calories consumed and energy used. However, the ERS notes
that the adjustments are based on a few studies from the 1970s and
1980s, and that the food supply chain has changed significantly
since then.[4] Improved loss adjustments are an on-going project
at the USDA, and, meanwhile, a recent FAO study found that losses
in the North American food supply chain range from 6 percent of
product in milk to 45 percent or more in vegetables (FAO,
2010).
In addition to food waste in the supply chain, there is
considerable food waste at home. The FAO study found 25 percent
food waste in the home. Parfitt et al. (2010) cite the original
studies used for these conclusions, which show in-home food waste
of 12-25 percent. For our calculations, we consider food calories
available "at the front door". Wasted food still required energy
to produce, and, thus, no explicit data adjustment is needed.
There is, however, an opportunity to save energy by reducing
in-home waste.
Two key data sources are used that provide the energy consumed
and the CO2e emitted in the production of food. The first is the
Environmental Input-Output and Lifecycle Cost Analysis (EIO-LCA)
database, developed and maintained by the Green Design Institute at
Carnegie Mellon University (CMU), which tracks energy use and CO2e
emissions by industry.[5] The second is a recent study by the
USDA, Energy Use in the U.S. Food System. Both data sets are based
on the input-output tables of the U.S. economy, produced by the
Bureau of Economic Analysis (BEA).[6]
Input-output tables provide a comprehensive view of the economy,
tracking all inputs across all industries that are needed for the
production of final goods. The BEA maintains a 480-sector table,
the most detailed analysis of its type in the world. There are 28
food sub-industries in the table. The latest BEA input-output
table is based on 2002 data. The CMU and USDA studies are based on
the BEA work, and, thus, also present data from 2002.
The EIO-LCA model is the result of more than 15 years of research
at Carnegie Mellon University, and is a leading tool for lifecycle
environmental impact analysis.[7] Of particular importance for
food calculations is that the EIO-LCA model tracks energy use and
CO2e emissions for the entire supply chain. For example, the
estimates of the energy used to produce one pound of beef available
at a local grocery store will include, among other inputs, the
energy used to grow and transport the grain to feed the cattle, all
energy for packaging and processing, energy for the materials to
build new processing plants in the meat industry, and energy to
transport the refrigerated meat to the store. This list is not
exhaustive, but merely illustrative of how the EIO-LCA model, based
on economy-wide input-output tables, captures the full lifecycle
energy use and CO2e emissions. As this is the standard breadth of
the EIO-LCA model, the results are comparable for each food
input.
A few data details and wrinkles: The EIO-LCA data report a single
sub-industry, "animal products," instead of its sub-groups of beef,
pork and other meats. The USDA study provides this detail for
energy use. The USDA study overlaps with the EIO-LCA data on other
food industries, and the overlapping data are much the same. The
CO2e data for the beef and pork are from another USDA study (USDA,
2011d). The EIO-LCA energy and CO2e data are reported in terms of
dollars of industry output. Industry output per food sub-industry
is from the U.S. Census for 2002.[8]
The USDA provides calories and servings data by food group, with
detail about items within a group. For example, under the
vegetables group (48 calories per day, on average), data are
available for the daily calories consumed for lettuce, tomatoes and
more.
A key piece of analysis in building the diet calculator is the
matching of these food groups to food industries. This process is
extremely important, as it ensures conformance between the data
sets. In a few cases, a food item was moved from one food type to
another, for better conformance with food industry data. For
example, ice cream is in the dairy food group for diets, but in the
sweets food industry for these calculations. Using the
sub-industry detail, it was moved to the dairy industry group to
create a better match between food production and food
consumption.
When constructing the diet calculator, we faced a tension between
ease-of-use and informative detail. As the food group detail was
adjusted to balance these factors, we also discovered that some
sub-foods/sub-industries have less reliable results, due to small
consumption or production. For example, the average American eats
16 calories of fish per day, less than one serving. Given this
relatively small amount, it is no surprise that the energy used to
produce a calorie is relatively high. And, as the 16 calories are
the total consumption from specific types of fish, each with an
even smaller number of calories, minute changes in the number of
calories consumed by fish type will have a large effect on the
calculated energy use per calorie consumed. To avoid this problem,
the food sub-industry groups are aggregated, when possible. Fish
is treated as a separate source of protein, despite the potential
for measurement errors, because of the strong consumer interest in
this food.
The final food groups in the calculator are:
· Beef
· Pork
· Chicken
· Fish
· Grains
· Dairy
· Fruits & Vegetables
· Sweets
Not shown in the list are "added fats and oils", which is 24
percent of the calories consumed by the average American. This is
a difficult food group to deal with, as most us would not know
where those nearly 600 calories go. To best capture the full
energy profile of the food industry, while not confusing users, we
distributed the calories consumed from added fats and oils to other
food groups by proportionately scaling up the number of servings,
keeping the total calories consumed constant. Separately, energy
used and CO2e emissions from added fats and oils were distributed
to other food groups in the same manner.
In addition, 9 percent of the food industry's energy use is from
seasonings, sauces and miscellaneous items - again, a food group
that is difficult to deal with. The calories, energy use and CO2e
were distributed to the other food and industry groups.
The adjustments for seasonings and fats preserve ease-of-use while
keeping constant energy consumed, and CO2e emissions at the
aggregate level. This is a reasonable approach, as the food items
(sauces, seasonings and added fats) are consumed in conjunction
with the other food groups.
Table 1 shows the results of these calculations. Descriptions of
typical serving sizes are from the Cleveland Clinic.[9] The
composition of the average American diet is shown for 2,600 total
calories per day. As mentioned earlier, these are calories before
any food preparation waste in the home. Actual consumption will be
less.
Note on Table 1 that the average American diet has a large number
of calories from grains and sweets, and few calories from fruits
and vegetables. As one shifts from the average American diet to
healthier alternatives, the caloric composition shifts
significantly, as do energy use and CO2e emissions.
Table 1 shows relatively high BTU per calorie produced for fish,
and also high CO2e emissions for this source of protein. As
mentioned earlier, this food group was broken out separately
because of consumer interest, but we do not have high confidence in
the data for fish.

Table 2 shows the same data in a different format, one that
highlights the relative energy intensity of various food groups.
Because of concerns about the quality of the data for fish, the
table was prepared both with and without the fish food group. The
results for CO2e are no doubt familiar to many readers. Beef is
the largest emissions producer, by far. In contrast, the column of
results for energy use in food production shows much less variation
across food groups. In particular, beef is not an intense user of
energy, but, in fact, is at or below average. This leads to an
interesting result: eat less beef to reduce emissions; eat less
fruits and vegetables to reduce energy use.
Table 2 highlights how examining food policy through a single
attribute - energy use or CO2e emissions - may miss other important
goals, such as healthy eating. Food policy has multiple
objectives, and personal preference determines the balance point.
Minimizing energy use might not be the most important goal for many
people.

Table 3 below provides an overall perspective and presents results
that can be compared to those of other researchers. The table
shows the calories, energy use, and emissions associated with the
average American diet. Note that the average American diet is a
research product of the USDA, and is not likely to be the diet of
anyone you know. It is based on food production, adjusted for
losses. It is also adjusted for imports and exports. The USDA's
average American diet is commonly used to show typical consumption
and its validity has been extensively researched.[10]
Table 3 shows that consumption of proteins and grains are the
largest energy uses in our diet. (The sum of the protein rows, from
beef to fish, is 29 percent of daily BTUs on average.) The
consumption of these food groups is also the largest emissions of
CO2e. Americans eat very few fruits and vegetables, only 12
percent of calories, and increasing consumption of this food group
will not save energy or carbon. Fresh vegetables, in particular,
have a relatively high-energy intensity, due to the handling and
refrigeration of these perishable crops.

The total CO2e emissions from the food calculations are line with other carbon calculators, such as Jones and Kammen (2011), who estimate from EIO-LCA data that food emissions are 7.7 CO2e metric tons per year. (Our estimate is 9.8 CO2e metric tons per year, with the differences arising from the treatment of food away from home, miscellaneous food, the composition of the average diet, and so on.) Similarly, a data summary from the University of Michigan shows that the average American emits 8 metric tons of CO2e per year from food choices.[11] The same source also estimates that 48 percent of emissions arise from beef and dairy consumption, and our estimate is that 49 percent of emissions are from these sources.
The energy results from the food calculations are line with Eschel and Martin (2006) and the USDA, with about 15 percent of total energy use arising from food consumption for the average consumer.
It is important to note that congruence amongst estimates of
carbon emissions and energy use for food is desirable, but may be a
limited opportunity; results are highly dependent on methodology.
Researchers have approached this complicated area quite
differently. Here are some of the factors to consider when
evaluating studies, as often one is comparing "apples to
oranges":
Defining the boundaries of the analysis. For
example, the World Watch Institute includes many sources of land
clearing in CO2e calculations. The CMU data uses older EPA data,
and includes less of this item.
Inclusion of all food groups. For example,
miscellaneous food, seasonings, and flavorings are nearly 9 percent
of food industry energy, but are often omitted from food-emissions
calculators. Also, beverages are not included in diet or food
industry data sources, though they consume energy and provide
calories. For example, soft drinks and alcoholic drinks are an
additional 13 percent of energy use, above estimates from food
alone (based on EIO-LCA data).
Fuel conversions. The EIO-LCA uses a 31 percent
fuel efficiency for electricity generated from coal plants. Other
analyses do not distinguish between generation sources and keep all
at 100 percent efficiency, and thus have much lower energy use and
emissions.
Waste in the food supply chain. Some studies
account for this and some do not.
What is the objective function? For example,
monoculture has bad effects that are not related to energy or CO2e.
Additionally, there are fertilizer runoff problems. These are
issues that change the relative value of food groups and an
informed consumer might want to consider them. Again, it is not
clear that minimizing energy use is the single-decision criterion
for consumption or policy-making.
Our current diet. Many studies do not start with
the average American diet, and then vary food choices from this
reference point. For example, eating healthy per the Choose My
Plate diet recommended by the USDA will almost certainly reduce
emissions - if less meat is eaten -- but, surprisingly, may
sometimes increase energy use, depending on the specific fruits and
vegetables and non-meat protein that replaces meat. The relative
impact of diet choices must be measured against where we are, not
where we wish we were.
The EIO-LCA data have been analyzed by others, and their research
suggests additional recommendations. Weber and Mathews (2008)
examine the transport component of energy use in the food system.
They find that 83 percent of energy used comes from production, and
that only 4 percent of energy is used to transport food from the
producer to stores or restaurants. On average, food travels about
1,000 miles during the production process, but the authors conclude
that the average consumer can save more energy or emissions by
shifting away from beef or poultry one day a week than by buying
local.
Typically, the food supply chain is assumed to end at the store or
restaurant. The consumer then drives to those locations to purchase
food. Weber and Mathews extend their analysis from simply
transportation in the food supply chain, to the miles driven to
purchase food. They note that reducing annual driving by 1,000
miles per year saves about the same amount of energy as does buying
local. Reducing driving by 1,100 miles per year saves the same
amount of energy as does shifting from animal to vegetable protein
sources one day a week. Of course, the specifics of any tradeoff
will depend on the particular vehicle and its mileage, but the
authors point out that it might be easier to make changes via
diet.
While the overall energy intensity of the U.S. economy has been
declining, the food industry has been going in the opposite
direction. Energy use per capital has been raising energy use in
the food industry, largely from a shift to processed foods (USDA,
2010). The change reflects the decline in cooking at home; energy
use from cooking, captured in utility bills, has dropped and energy
use in the food supply chain has increased. Total energy may not
have increased; energy consumption might just be a transfer from
one sector to another. It is difficult to draw the conclusion of
"buy fewer packaged foods and cook more at home to save
energy."
Finally, although the data are not recent or as complete as one
would like, it does appear that there is considerable opportunity
to reduce energy and emissions in food consumption by wasting
less. The FAO study and the USDA estimates suggest considerable
waste in the food supply chain, but importantly for these
calculations, there is also considerable waste in the home. A
recent report by the USDA suggests that consumers waste a
significant of calories purchased, with the exact amount varying by
food group (USDA, 2011c). So, reducing wasted food at home can
make a significant savings in energy and emissions.
· Eat less. One-third of adults are obese in the
United States, consuming more calories than needed.[12] Eating is a
very emotional issue, and we doubt that adults will eat less to
save energy, but the math of food intake is clear.
· Buy less and waste less. Estimates are that
12-25 percent of food purchased is wasted in the home. More careful
food purchasing can be a large source of energy savings.
· Eat fewer grain products. More than 35 percent
of the energy in the average American diet comes from the grains
food group. Further, many grain products have added fats and oils,
and/or added sugar, which are another 20 percent of energy in the
diet. In sum, 55 percent of energy and 60 percent of calories are
from grains, sugars, and fats. Because of its large share of the
current American diet, this can be a place to reduce.
In addition, analyses by others using the same data suggest
that:
· Buying local has only a small impact on energy and emissions,
because most food energy is from production, not
transportation.
· Driving to the store to purchase food uses more energy per year
than does transporting food to the store.
· There are large waste losses in the food supply chain, and
reduction of this waste throughout the industry can lower the
energy content of food significantly.
· Energy use in the food industry has risen as Americans cook less.
We continue to shift our purchases to prepared foods. An example is
washed and bagged lettuce.
BEA (2011), Benchmark Input-Output Tables for 2002. www.bea.gov/industry/io_benchmark.htm.
Eschel and Martin (2006), "Diet, Energy and Global Warming,"
Earth Interactions, 2006, http://pge.uchicago.edu/workshop/documents/martin1.pdf.
FAO (2010), Global Food Losses and Food Waste, downloaded from: www.fao.org/fileadmin/user_upload/ags/publications/GFL_web.pdf.
Hendrickson et al. (2006), "Environmental Life Cycle Assessment of Goods and Services, An Input-Output Approach". Resources for the Future, 262 pages.
Jones and Kammen (2011), "Quantifying Carbon Footprint Reduction Opportunities for U.S. Households and Communities," Environmental Science & Technology, downloaded from: http://pubs.acs.org/doi/abs/10.1021/es102221h.
Parfitt et al. (2010), "Food Waste within Food Supply Chains: Quantification and Potential for Change to 2050," Philosophical Transactions of the Royal Society, B, downloaded from: http://rstb.royalsocietypublishing.org/content/365/1554/3065.abstract
Weber and Mathews (2008), "Food-Miles and Relative Impact of Food Choices in the U.S.," Environmental Science and Technology. Downloaded from: psufoodscience.typepad.com/psu_food_science/files/es702969f.pdf.
USDA (2010), "Energy Use in the U.S. Food System," Economic Research Service, downloaded from: www.ers.usda.gov/Publications/err94/err94.pdf.
USDA (2011a). See "Average Daily per Capita Calories from the U.S. Food Availability, Adjusted for Spoilage and Other Waste," www.ers.usda.gov/data/foodconsumption/spreadsheets/foodloss/Calories.xls.
USDA (2011b), "Loss-Adjusted Availability, by Servings." www.ers.usda.gov/Data/FoodConsumption/FoodGuideSpreadsheets.htm#servings.
USDA (2011c), "Consumer-Level Food Loss Estimates and Their Use in the ERS Loss-Adjusted Food Availability Data," Economic Research Service, downloaded from: www.ers.usda.gov/Publications/TB1927/.
USDA (2011d), "U.S. Agriculture and Forestry Greenhouse Gas Inventory: 1990-2008; Chapter 2: Livestock and Grazed Land Emissions"; www.usda.gov/oce/climate_change/AFGG_Inventory/2_LivestockandGrazing.pdf.
World Watch Institute (2011), Livestock and Climate Change;
www.worldwatch.org/files/pdf/Livestock%20and%20Climate%20Change.pdf.
NOTES
[1] 14 percent (USDA, 2010)
[2] For consumer interest, other metrics may be displayed on the web tool, but as each can be translated into units of energy or CO2e, the discussion here will focus only on these two.
[3] See USDA (2011a) and (2011b).
[4] This discussion is available at www.ers.usda.gov/data/foodconsumption/FoodGuideDoc.htm.
[5] The EIO-LCA model is available in an interactive form from Carnegie Mellon University, at www.eiolca.net/cgi-bin/dft/use.pl. The producer price version of the model was used. Data on the energy use and CO2e emissions by food sub-industry were obtained, per $100 million in economic activity. The total 2002 economic activity by food sub-industry was obtained from the EIO-LCA model documentation, www.eiolca.net/docs/full-document-2002-042310.pdf. Energy use was then normalized to millions of BTUs per capita, using 2002 population estimates of 287.8 million residents (U.S. Census, http://www.census.gov/popest/data/historical/2000s/vintage_2002/index.html).
[6] The data are available at eiolca.net, USDA (2010) and BEA (2011), respectively.
[7] For an introduction to the model, see www.eiolca.net.
[8]. The industry sales data was downloaded from: http://factfinder.census.gov/servlet/IBQTable?_bm=y&-geo_id=&-ds_name=EC0231I1&-_lang=en.
[9] http://my.clevelandclinic.org/heart/prevention/weight/servingsize.aspx.
[10] There is a large literature on the two methods used by the USDA to determine what Americans eat (a food consumption survey and the production data used in this work), and much discussion about their strengths and weaknesses. Our intent here is to simply present an easy-to-understand reference point.
[11] Center for Sustainable Systems, University of Michigan. 2010. "Carbon Footprints Factsheet". Pub. No. CSS09-05.
[12] Center for Disease Control, 2010 data: www.cdc.gov/obesity/data/trends.html.
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