Healthy Animals = Healthy Planet - Eric Boles, University of Arkansas, from the 2012 Annual Conference of the National Institute for Animal Agriculture, March 26 - 29, Denver, CO, USA.
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Eric Boles - Healthy Animals = Healthy Planet
1. Eric Boles
Center for Agricultural and Rural Sustainability
Biological and Agricultural Engineering Department
University of Arkansas
eboles@uark.edu
Marty Matlock
Greg Thoma
Healthy Animals:
Healthy Planet
17. Sustainability 2050: The Challenge
What we do in
the next 10 years
will shape Earth
and Humanity for
the next 100
years
When technology and culture collide
technology prevails, culture changes
17
18. Billions
0
1
2
3
4
5
6
7
8
9
10
1950 1970 1990 2010 2030 2050
Less Developed Regions
More Developed Regions
Source: United Nations, World Population Prospects: The 2004 Revision (medium scenario), 2005.
We are all in this together
18
19. Human Activities Dominate Earth
Croplands and pastures are the largest terrestrial biome, occupying over
40% of Earthâs land surface
19
21. Measuring Sustainability:
Metrics: Quantifiable phenomena to measure an endpoint
Index: Aggregation of metrics to a single number, requires
normative criteria for integration of metrics with different units
Baseline: Benchmark used to measure change over time
Life Cycle Assessment (LCA): One method for measuring the
inputs and outputs in a process in a step towards quantifying
sustainability
Is there a standard method for LCAs?
⢠ISO 14040 and 14044 Standards
⢠PAS 2050 for greenhouse gasses
⢠No standard for Life Cycle Inventory
⢠No guidelines for most other metrics
21
26. LCA allows for impact
assessment from cradle to
grave
Raw
Material
A
Raw
Material
A
Raw
Material
B
Raw
Material
B
Product
1
Product
1
26
27. LCA allows for impact
assessment from cradle to
grave
Raw
Material
A
Raw
Material
A
Raw
Material
B
Raw
Material
B
Product
1
Product
1
Boundaries matter
27
29. Life Cycle Assessment:
Reconciling Functional Units
CO2
CH4
N2O
Green
House Gas
Potentials
1 g CO2-equiv. / g CO2
21 g CO2-equiv. / g CH4
310 g CO2
-equiv. / g NO2
29
30. Emerging Consensus on LCA
Framework
⢠Need for comparable metrics that span sectors, industries and
geographies
⢠Metrics should be grounded in scientific methodologies, namely
Life Cycle Assessment â guards against burden shifting
⢠Sustainability Metrics and Life Cycle Inventory data (LCI) should
be transparent, validated, widely available, and inexpensive
⢠The same LCA data and models should be used by producers,
retailers, policymakers, NGOs and consumers
31. 40
Major Challenges in the Food
System
⢠Consumers are far removed from
producers.
⢠Complexity of the supply chain results in
ineffective feedback systems and irrational
decisions.
⢠Volatility of food prices create immediate
human suffering and political instability,
especially for the bottom billion.
⢠The future prosperity of humanity depends
on increasing prosperity for the bottom
billion.
32. The Food Marketing Chain
Production Processing
Distribution
RetailDirect Mktg Wholesale
Consumption
Safety
Security
Stability
33. Carbon Footprint of Fluid Milk in the US
Funded by the Dairy Research Institute
Greg Thoma
Darin Nutter
Rick Ulrich
Marty Matlock
Jennie Popp
Dae Soo Kim
Cashion East
Nathan Kemper
Zara Niederman
University of Arkansas
David Shonnard
Felix Adom
Charles Workman
Michigan Technological University
34. Calculating a carbon
footprint requires:
⢠A full system-level accounting of greenhouse gases
emitted in association with a product or service
â Energy consumption
â Manure & nutrient management
⢠The system begins with extraction from nature and
includes packaging disposal (cradle to grave)
⢠Life Cycle Assessment is a systems analysis tool
commonly used as a framework for these
calculations
35. 35
⢠ISO 14044 compliant, with external review
⢠Goal: Determine GHG emissions
associated with consumption of one gallon of
milk to US consumer.
⢠Scope: Cradle to grave. Specifically
including pre-combustion burdens for primary
fuels and disposal of packaging.
LCA Methodology
36. Life Cycle Assessment Case Study:
Carbon Equivalent GHG in Dairy
Production Processing
DistributionConsumption
38. 38
Life Cycle Inventory â
Data Drives the Work
Surveys:
1) Dairy Producer (~535; 9% response rate)
2) Farm to processor transportation data
(~211,000 round trips â 2007 only)
3) Milk Processor (50 plants responded)
Published Literature:
1) Peer Reviewed Literature
a) Enteric Methane, Nitrogen and Methane from manure management
b) Life cycle inventory data for crop production (NASS, Budgets, USLCI)
2) Other Publications (e.g. IPCC, EPA)
3) Expert opinion (e.g., hay production budgets from Ag Extension)
39. Major Assumptions
⢠Infrastructure excluded
⢠Biogenic carbon
â Sequestration not included; nor respiration
⢠Economic allocation as base case
â Biological / causal model for milk : beef
â Milk solids model for cream : fluid milk
⢠IPCC Tier 2 models for manure management
⢠Product loss: 12% retail + 20% consumer
(ERS food availability study)
39
43. GHG Emissions from Milk: The
Big Picture
43
17.6 lb CO2e/ gallon
95% confidence band :
15.3 to 20.7 lb CO2e/
gallon
Farm Gate
44. Overall Takeaways
⢠Do more with less
â Improving efficiency
â Innovation âmanure and nutrient management
â Technology transfer
⢠Operations with smaller carbon footprint have generally
adopted better management practices and have higher feed
conversion
⢠A âone size fits allâ solution does not exist
â Opportunities exist to improve across the spectrum
⢠Strive for continuous improvement by adopting better
management practices and utilizing decision support tools
44
45. Need to put water in context
Water Stress
â˘Is a function of the amount of
water use and the amount of
water available (water
use/water availability)
â˘Predictor of direct economic
costs
Virtual Water
â˘Only calculates the total
volume of water used to
produce good/service
regardless of type of water
Water is different than GHG
46. Two Major Categories of Water
Blue Water
â˘Water withdrawn from surface or
groundwater for consumption
â˘Direct Economic Costs
Green Water
â˘Soil moisture from precipitation
â˘âFreeâ
47. Evaluating the Water Footprint in
the Production of Liquid Milk
Dr. Matlock
Center for Agriculture and Rural Sustainability
48. ⢠Goal: Understanding the
(geographical) hotspots for dairy
operations with regard to water
consumption
⢠To place the dairy sector in the larger
context of water consumption and
availability
Dairy Farm Water Use:
Context & Potential for Impact
51. Current Climate WaSSI &
Dairy Herd Demographics
Most impacts are from crops rather than direct use
52. Direct Dairy Water Use
Watershed with highest direct use for dairy is Central Valley in California
53. Dairy Water Use to USGS Total
Agricultural Water Use
Compared to total agricultural use, dairy direct use is very low.
Therefore, where the feed is grown matters more than where
the cattle are grown.
54. Summary Findings
⢠Diary water use is largely water embodied in the
crops used to feed cows
⢠Water quality impacts from the dairy industry is
largely associated with feed production (fertilizer)
⢠Climate change impacts on dairy will be on water
availability for feed
55. National Scan-level Carbon
Footprint Study for
Production of Swine
Greg Thoma
Jason Frank
Charles Maxwell
Cash East
Darin Nutter
Funded by the National Pork Board
56. Goal and ScopeGoal and Scope
Determine GHG1
emissions
associated with delivery of one
serving of pork to US consumer.
Cradle to grave. From crop
production through consumption
and package disposal
1
Greenhouse gases, expressed as CO2 equivalents
Outline of Swine LCA:
defining the system
57. Energy consumed at every point in the value chain
Pork Supply Chain
Crop Prodn
Confined
Live animal
Transport
Consumer
Pesticides
Fertilizer
Water
Nitrous
Oxide
Diesel
CO2
Pastured
Manure
Electricity
Diesel
Landfill or
MSW Combustion
Diesel
CO2
Plastic wrap
Styrofoam
plate
Cleaners
Cooling
Water
Electricity
Raw
Materials
Electricity Diesel
Gas
CO2
Cooling
Solid
Waste
Feed
Production
Live Swine
Production
Processing/ PackagingTransport Distribution Retail Consumer
CH4 CO2
Recycle
CFCs/
HCFCs
Abattoir/
Packaging
Distribution
Feed/Processing
&Transport
Electricity
COLOR KEY: Energy Inputs GHG effects
CFCs/
HCFCs
CH4
CH4
Retail outlet
Refrigerants
Refrigerants
LP/Nat.Gas
Bulk Packing Export
Nitrous
Oxide
NH3
CO2
Wastewater
Treatment
(anaerobic)
CH4
Rendering
58. Some Underlying Assumptions
⢠9.5 piglets/litter and 3.5 litters per sow
⢠Finished live weight: 268 lb
â Carcass = 0.75 live weight
â Boneless = 0.65 carcass
⢠Typical corn, soy meal, distillerâs grain diets
â With supplements accounted; 82% digestibility
⢠IPCC Tier 2 GHG emission factors for manure systems2
â 1kg of manure=2kg methane
⢠Biogenic Carbon
â crop sequestration & animal respiration excluded
1 American Society of Agricultural Engineers, 2005 ASAE D384.2 MAR2005.
2 Dong, H., et al. (2006) Chapter 10 6 IPCC Guidelines for National Greenhouse Gas Inventories.
59. Some Underlying Assumptions
⢠10% waste (spoiled or uneaten) by consumers
⢠Economic allocation
â Feed byproducts
â Rendering co-products
⢠Space allocation
â Retail
â In-home
60. Conceptual Farm Model
Finished
pigs
Nursery â Finish
Barn
Manure
Management
Feed
Energy
Emissions;
Fertilizer
Weaned pigs
Emissions
Sow Barn:
Breeding; Gestation;
Lactation
Manure
Management
Feed
Gilt
Emissions;
Fertilizer
Emissions
Energy
Material and energy flows are integrated over a sowâs productive life. The farm
gate total consumption of feed and energy required to grow all the litters
produced by one sow is allocated to the total finished weight of her litters.
62. The Big Picture
⢠2 .2 lb CO2e per 4oz serving
â (8.8 kg CO2e/kg pork consumed)
â with a 95% confidence interval from 1.95 to 2.55 lb CO2e.
⢠The contribution of emission burden:
⢠10.3%: sow barn (including feed and manure handling);
⢠54.3%: nursery to finish (including feed and manure handling);
⢠7.4%: processing (6.4%) and packaging (1.1%);
⢠12%: retail (electricity and refrigerants);
⢠15.9%: the consumer (refrigeration and cooking).
63. Network Diagram - Legend
1 kg
In Home
2.08
1 kg
Overall
7.82
2.05 kg
Finish Barn
3.4
Reference Flow
(quantity of material or energy)
GHG contribution
(cumulative kg CO2e contributed
by this branch of the network)
Process or Material
Contributing to Footprint
Connecting Line Weight is
Proportional to GHG
Contribution
64. 8.09 MJ
electricity,
1.73
0.519 m3
Natural gas,
1.18
3.95 kg
Corn Feed
1.5
0.904 lfdays
Retail
1.2
1 kg
In Home
1.13
1 kg
Overall
7
2.49 kg
Corn Grain
0.661
1.07 kg
Corn Grain
0.369
0.825 kg
DDGS
0.553
0.0328 kg
N Fertilizer
0.362
2.05 kg
Finish Barn
3.52
0.0927 kg
Sow Barn
0.572
0.922 kg
Deep Pit
1.02
1.54 kg
Processing
0.494
0.000187 kg
Referigerant
0.563
7.49 MJ
Electricity
1.74
0.491 m3
Natural Gas
1.18
1.19 kg
Soybean Meal
0.49
1 kg
Cooking
0.898
Cradle to grave footprint:
Base case: Deep pit
This flow is a credit for
avoided production of
nitrogen fertilizer
65. Live Swine Production
The model has 1 kg
boneless pork as the
comparative unit; thus
2.05 kg live animal
weight must leave the
farm gate.
67. Consumption is also important
0.125 m3
Natural gas,
0.286
3.95 kg
Corn Feed
1.5
0.904 lfdays
Retail
1.2
1 kg
In Home
1.49
1 kg
Overall
7.35
2.49 kg
Corn Grain
0.661
1.07 kg
Corn Grain
0.369
0.825 kg
DDGS
0.553
2.05 kg
Finish Barn
3.52
0.0927 kg
Sow Barn
0.572
0.922 kg
Deep Pit
1.02
1.54 kg
Processing
0.494
0.000187 kg
Referigerant
0.563
12.9 MJ
Electricity
2.99
0.117 m3
Natural Gas
0.281
1.19 kg
Soybean Meal
0.49
1 kg
Cooking
1.25
71. Uncertainty
⢠All variables have some variability
⢠Propagation of uncertainty performed by Monte
Carlo simulation
72. Conclusions
⢠Estimated GHG emissions consistent with international
studies
⢠Pork footprint is comparable to other protein sources.
⢠Manure management is a large opportunity
⢠Consumption contributes a significant fraction of the
total footprint
⢠Fuels and Electricity are important, while not the
largest contributors to the overall footprint, still present
opportunities for increased efficiency
⢠Processing is relatively efficient per kg processed
⢠Transportation is less of a contributor than expected
74. Agricultural Sustainability Metric Initiatives
Field to Market â The Keystone Alliance for
Sustainable Agriculture
⢠Focused on commodity agriculture
⢠Metrics are outcomes based, technology neutral (undefined)
⢠Metrics are regional to national in scale
The Sustainability Consortium
⢠Focused on supply chain
⢠Metrics are outcomes based, technology neutral
⢠Metrics are local to global scale
74
75. 40
Field to Market Alliance
⢠Field to Market is a collaborative stakeholder group of
producers, agribusinesses, food and retail companies, and
conservation organizations that are working together to
develop a supply-chain system for agricultural sustainability.
⢠We are developing outcomes-based metrics
â We will measure the environmental, health, and
socioeconomic impacts of agriculture first in the United
States
â We began with national scale environmental indicators
for corn, soy, wheat, and cotton production in the U.S.
76. 76
Field To Market Steering Committee
Members and Participants
⢠American Farm Bureau Federation
⢠American Soybean Association
⢠Bayer CropScience
⢠Bunge
⢠Cargill
⢠Conservation International
⢠Conservation Technology Information
Center
⢠Cotton Incorporated
⢠CropLife America
⢠CropLife International
⢠DuPont
⢠Fleishman-Hillard
⢠General Mills
⢠Grocery Manufacturers of America
⢠John Deere
⢠Kellogg Company
⢠Land OâLakes
⢠Manomet Center for Conservation
Science
⢠Mars, Incorporated
⢠Monsanto Company
⢠National Association of Conservation
Districts
⢠National Association of Wheat
Growers
⢠National Corn Growers Association
⢠National Cotton Council of America
⢠National Potato Council
⢠Syngenta
⢠The Coca-Cola Company
⢠The Fertilizer Institute
⢠The Nature Conservancy
⢠United Soybean Board
⢠World Resources Institute
⢠World Wildlife Fund
⢠University of Arkansas Division of
Agriculture
⢠University of Wisconsin-Madison
College of Agricultural and Life
Sciences
77. Definition of Sustainable
Agriculture
1. Meeting the needs of the present while enhancing the
ability of future generations to meet their needs
2. Increasing productivity to meet future food demands
3. Decreasing impacts on the environment
4. Improving human health
5. Improving the social and economic well-being of
agricultural communities
âFeeding 9.25 billion people without one hectare more of
land or one drop more of waterâ
77
78. ⢠Total annual energy
use increased by 28
percent
⢠Water use
increased by 17
percent
⢠Greenhouse gas
emissions increased
by 34 percent.
⢠Soil loss decreased
by 33 percent.
78
Corn Sustainability Metrics
79. 79
⢠Total annual soil loss
decreased by 11
percent
⢠Climate impact
increased by 15
percent
⢠Total energy use
decreased by 29
percent
⢠Total water use
increased by 39
percent.
Soybean Sustainability Metrics
80. ⢠Total annual soil loss
and climate impact did
not change.
⢠Total energy use
decreased by 45
percent
⢠Total water use
decreased 26 percent.
80
Cotton Sustainability Metrics
81. Wheat Sustainability Metrics
81
⢠Total annual soil loss
decreased by 54
percent.
⢠Climate impact
increased 5 percent
⢠Total energy use
decreased by 18
percent
⢠Total water use
decreased 11 percent.
82.
83. The Sustainability Consortium
The Sustainability Consortium was
organized in 2009 by The University of
Arkansas and Arizona State University in
collaboration with the Walmart Foundation.
TSC is an independent organization of
diverse global participants who work
collaboratively to build a scientific
foundation that drives innovation to
improve consumer product sustainability
through all stages of a product's life cycle.
83
84. What TSC Does
The Sustainability Consortium drives
scientific research and the development
of standards and IT tools, through a
collaborative process, to enhance the
ability to understand and address the
environmental, social, and economic
implications of products.
84
88. Support farmers and their communities
More than a billion people rely on agriculture for subsistence. By
the end of 2015 in emerging markets, Walmart will help many
small and mid-sized farmers gain access to markets by:
1. selling $1 billion in food sourced from 1 million small and
medium farmers;
2. providing training to 1 million farmers and farm workers in
such areas as crop selection and sustainable farming practices --
the company expects half of those trained to be women; and
3.increasing the income of the small and medium farmers it
sources from by 10 to 15 percent.
In the U.S., Walmart will double its sale of locally sourced
produce and increase its purchase of select U.S. crops.
Sustainable Agriculture Initiatives
88
89. Produce more food with fewer resources and less waste
Walmart has one of the worldâs largest food supply chains and is
committed to reducing and optimizing the resources required to
produce that food and driving more transparency into its supply
chain. The goals include:
1. accelerating the agricultural focus of the Sustainability Index,
beginning with a Sustainable Produce Assessment for top
producers in its Global Food Sourcing network in 2011;
2. investing more than $1 billion in its global fresh supply
chain in the next five years; and,
3. reducing food waste in its emerging market stores and clubs
by 15 percent and by 10 percent in stores and clubs in its other
markets by the end of 2015.
Sustainable Agriculture Initiatives
89
90. Sustainably source key agriculture products
Walmart will focus on two of the major contributors to global
deforestation, palm oil and beef production.
Require sustainably sourced palm oil for all Walmart private
brand products globally by the end of 2015. Sourcing sustainable
palm oil for our U.K. and U.S. private brand products alone will
reduce greenhouse gas emissions by 5 million metric tons by the
end of 2015.
Expand the already existing practice of Walmart Brazil of only
sourcing beef that does not contribute to the deforestation of
the Amazon rainforest to all of our companies worldwide by the
end of 2015. It is estimated that 60 percent of deforestation in the
Brazilian Amazon is related to cattle ranching expansion.
Sustainable Agriculture Initiatives
90
91. We shall never achieve harmony with
land, any more than we shall achieve
absolute justice or liberty for people. In
these higher aspirations, the important
thing is not to achieve but to strive.
- Aldo Leopold
Sustainability Ethic
92. Green water = free
Blue water = $
Water withdrawn for consumptionGreen water = soil
moisture from
precipitation
Water
withdrawn
by humans
Evaporated Integrated Not returned to same
into product watershed
Blue water = surface water and groundwater withdrawn for consumption
Water
returned
to same
watershed
Surface water Groundwater
Editor's Notes
Given all of the work in different areas in both LCA we must begin coordinating efforts to make sure that different measurements and standards are comparable.
The question defines the LCI stage; ours was to define the national scale impacts of fluid milk production. Or: what activities (and associated emissions) are induced by consumption of milk? This is a bit different than defining the footprint of a single farming operation.
So starting with feeds âŚ.
Note Water availability does not always mean places where there is plentiful water
The Water Stress Index (WSI) represents the competition for water, as a function of use/availability
Some background of terminology
All of these are important , because the right methodology for Dairy must take into account not just the volume of water, but also the local water stress index, the source of water and quality of water post production.
Blue water: water withdrawn from surface or groundwater that wonât return to the same watershed (direct economic costs)
What activities required to get the feed to the animalâs trough?
Need to see this to follow calculaiton
The width of the connecting lines represents the relative contribution from the particular unit to the whole ghg emisssion. The contribution shown in each box is the cumulative contribution from all of the network nodes upstream in the supply chain plus the contribution occurring at that node.
Mention comparison to Dalgaard work ==2kg/kg live or about 2.7 kg /dressed carcass; EU 3 ~ 5 kg/kg carcass
25% from manure (with credit for avoided inorganic N)
Allocation based on economic research service sector level activity; data from aggregated industry sources
2 points: 1 consumption is >15% of footprint; electricity slightly less efficient than natural gas â grilling seems to be the best.
Interesting: feed and retail/consumption are significant; MMS dominates on âfarm ghg
Per unit greenhouse gas emissions were adversely impacted by a steady rise in nitrogen application during the period 1987 through 1995
Since 1995 nitrogen application has moderated and carbon emissions have improved considerably
Strong adoption of no-till over the past decade has also helped reduce net carbon emissions