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Page 1: Fertilizer Industry St. Petersburg, FL A Wicked Troika - · PDF fileA Wicked Troika Food Security, Fertilizer and the Environment : November 16, 2011 Otto C. Doering, III Professor

A Wicked Troika Food Security, Fertilizer and the Environment :

November 16, 2011

Otto C. Doering, III Professor of Agricultural Economics, Purdue

Fertilizer Industry Roundtable St. Petersburg, FL

Page 2: Fertilizer Industry St. Petersburg, FL A Wicked Troika - · PDF fileA Wicked Troika Food Security, Fertilizer and the Environment : November 16, 2011 Otto C. Doering, III Professor
Page 3: Fertilizer Industry St. Petersburg, FL A Wicked Troika - · PDF fileA Wicked Troika Food Security, Fertilizer and the Environment : November 16, 2011 Otto C. Doering, III Professor

This Troika as a Wicked Problem

Tame vs. Wicked

Tame vs. Wicked

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The Problem

Tame Problem • The clear definition of the

problem also unveils the solution

• The outcome is true or false. Successful or unsuccessful

• The problem does not change over time.

Wicked Problem • No agreement about what

the problem is. Each attempt to create a solution changes the problem.

• The solution is not true or false – the end is assessed as “better” or “worse” or “good enough.”

• Problem changes over time.

Tame vs. Wicked

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The Role of Stakeholders

Tame Problem • The causes of a problem

are determined primarily by experts using scientific data.

Wicked Problem • Many stakeholders are likely

to have differing ideas about what the “real” problem is and what are its causes.

Tame vs. Wicked

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Nature of the Problem Tame Problem • Scientifically based

protocols guide the choice of solution(s).

• The problem is associated with low uncertainty as to system components and outcomes.

• There are shared values as to the desirability of the outcomes.

Wicked Problem • Solution(s) to problem is

(are) based on “judgments” of multiple stakeholders.

• The problem is associated with high uncertainty as to system components and outcomes.

• There are not shared values with respect to societal goals.

Tame vs. Wicked

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The “Stopping Rule”

Tame Problem • The task is completed

when the problem is solved.

Wicked Problem • The end is accompanied by

stakeholders, political forces, and resource availability. There is no definitive solution.

Tame vs. Wicked

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High

Low

HighLow Value Conflict

Wicked Problems Engaged Sustainability Science Adaptive Management

Tame Problems Normal Science Conv. Env. Mgt.

Uncertainty

Tame vs. Wicked

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Key Challenges

Some key food production challenges

Water

Yield Plateaus

Intensification

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Korea and Yield plateaus are evident for several cereal crops in some major producing countries: China for rice, wheat in northwest Europe and India, maize in China and……..perhaps also for irrigated maize in the USA.

Cassman et al, 2003, ARER 28: 315-358

Maize

China

Brazil

USA - rainfed

USA - irrigated

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1960 1970 1980 1990 2000 2010Year

Wheat

China

India

Northwest Europe

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Rice

India

R. KoreaChina

Indonesia

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Yiel

d (M

g ha

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Yiel

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Cassman, 1999. PNAS, 96: 5952-5959

?

Cassman et al., 2003, ARER 28: 315-358

Cassman et al., 2010, Handbook of Climate Change

Grassini et al., 2011. FCR 120:142-152

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Bottom Line on Yield Trends

• Cereal crop area limited by increasing urbanization due to population growth and economic development, scarcity of unfarmed areas with soil quality suitable for supporting intensified systems, and concerns about loss of wildlife habitat and biodiversity

• Current rates of gain in crop yields not adequate to meet expected demand for food, feed, fiber, and fuel on existing crop land

• Little scope for increasing irrigated crop area due to competition for water with other sectors

• Little increase in yield potential of maize or rice for the last 30-40 years; yield stagnation in some areas

• Is there scope for a quantum leap in yields from biotechnology?

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Bottom Line on Yield Trends • Cereal crop area limited by increasing urbanization due to

population growth and economic development, scarcity of unfarmed areas with soil quality suitable for supporting intensified systems, and concerns about loss of wildlife habitat and biodiversity

• Current rates of gain in crop yields not adequate to meet expected demand for food, feed, fiber, and fuel on existing crop land

• Little scope for increasing irrigated crop area due to competition for water with other sectors

• Little increase in yield potential of maize or rice for the last 30-40 years; yield stagnation in some areas

• Little scope for quantum leap in yields from biotechnology • Need for ecological (sustainable) intensification

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Sustainable Intensification

How high can average farm yields go using crop and soil management practices that conserve natural resources, protect environmental quality, and give an acceptable rate of economic return?

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Drier savanna

Moist savanna

Humid forest

Midaltitude savanna

Not all land is suitable for intensification: requires soils of adequate quality and reliable rainfall or irrigation

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Ecological Intensification

Achieving high-yield crop production systems that protect soil and environmental quality and conserve natural resources Characteristics of EI systems: Yields that are 80-85% of genetic yield potential Uses best adapted crop germplasm 70-80% N fertilizer uptake efficiency (vs 30-50% now) Improves soil quality (nutrient stocks, SOM) Uses integrated pest management (IPM) Achieves a net reduction in GHG emissions Has a large net positive energy balance In irrigated systems: 90-95% water use efficiency ¶Cassman, 1999. in Proc. Natl. Acad. Sci (USA):5952-5959

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Ecological intensification is knowledge-intensive and requires:

• New knowledge derived from field research focused on improving productivity, soil quality, and environmental services simultaneously

• An integrated systems approach

• Decision-support tools for responsive, real-time, in-season crop and soil management (precision agriculture)

Need for good quality soil and long-term weather databases (daily temp, rainfall, solar radiation)

Could farmers in developing countries have a comparative advantage due to scale of farming?

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Nitrogen Dilemma

The Dilemma of Nitrogen:

Too Much of a Good Thing

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Nitrogen Drivers in 1860 and Now

Grain Production

Meat Production

Energy Production

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Global Nr Creation by Human Activity 1850 to 2005 In 2005 ~190 Tg Nr was created by humans.

Haber Bosch

Fossil Fuel

Total Nr Production • Fossil fuel combustion, 25 Tg Nr yr-1 • Cultivation-induced BNF, 40 Tg Nr yr-1 • Haber-Bosch process

• Fertilizer 100 Tg Nr yr-1 • Industrial feedstock 23 Tg Nr yr-1

Nr C

reat

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Nr /

yr

Legumes

Total

Natural Range, terrestrial {

Population

Galloway et al., 2003

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Nitrogen Deposition mg Nr/m2/yr

1860 2000

5000 2000 1000 750 500 250 100 50 25 5

Galloway et al., 2004

• Nitrogen emitted as NOx to atmosphere by fossil fuel combustion • Nitrogen emitted as NH3 and NOx from food production • Once emitted, it is transported and deposited to ecosystems • In 1860, human activities had limited influence on Nr deposition • By 2000, the picture had changed

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• xxxxxx

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Reactive Nitrogen in the United States: An Analysis of Inputs, Flows, Consequences and Management Options -- EPA Science Advisory Board’s Integrated Nitrogen Committee final report

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Natural Biological Nr Fixation

Nr Introduction into the US Tg Nr/yr

3.5 1.9

7.7

10.9

4.2

6.4

NOx transportation

NOx stationary

Cultivation Biological Nr Fixation

Haber Bosch-Nr Fertilizer

Haber Bosch-Nr Industry

Natural, 6.4 Tg Nr/yr Anthropogenic, 29 Tg Nr/yr

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Identification of Control Points to Management Reactive N in the US

The overarching objective is to maintain the benefits of nitrogen while minimizing the losses to the environment

For control points of Nr in the cascade we set the following priorities:

• Where is Nr creation not needed?

• Where can Nr use be made more efficient?

• Where can Nr wastes be managed?

Page 25: Fertilizer Industry St. Petersburg, FL A Wicked Troika - · PDF fileA Wicked Troika Food Security, Fertilizer and the Environment : November 16, 2011 Otto C. Doering, III Professor

Atmosphere

Terrestrial

Agricultural

Aquatic

Populated

greenhouse effect

Food Production +

strat. ozone depletion

Natural BNF

smog PM-2.5

5.4

6.4

22.8

Acidification Vegetated

Biodiversity loss

Eutrophication

Management of Nitrogen: Three Priorities

As shown above, ~35 Tg Nr/yr are introduced in the USA by natural processes, food production and energy production. Once introduced, it has beneficial and detrimental impacts on ecosystems and humans.

Energy Production

Acidification Biodiversity loss

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Atmosphere

Food Production +

Energy Production

Natural BNF

5.4

6.4

22.8

First Priority: Nr not Needed

By using existing technology, EPA can expand its NOx control efforts to include 90% decreases of emissions from heavy-duty on-road, all off-road mobile sources and currently uncontrolled electricity generation and industrial processes. This would decrease Nr formation by 2 Tg Nr/yr.

greenhouse effect strat. ozone depletion

smog PM-2.5

Terrestrial

Aquatic

Acidification Biodiversity loss

Eutrophication

Agricultural Populated

Acidification Vegetated

Biodiversity loss

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Atmosphere

Food Production +

Energy Production

Natural BNF

5.4

6.4

Second Priority: Increase Nr Use Efficiency

By using currently available technology crop and animal N-uptake efficiencies can be increased through a combination of knowledge-based practices and advances in fertilizer and feeding technologies. This would decrease the amount of Nr applications to crop lands by ~3 Tg Nr/yr.

greenhouse effect strat. ozone depletion

smog PM-2.5

Terrestrial

Aquatic

Acidification Biodiversity loss

Eutrophication

22.8 Agricultural Populated

Acidification Vegetated

Biodiversity loss

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Atmosphere

Food Production +

Energy Production

Natural BNF

5.4

6.4

Third Priority: Manage Nr Wastes

By improving human waste treatment practices using existing technology we would decrease Nr losses by 0.5 to 0.8 Tg Nr/yr.

The same technologies could be used for animal waste for a decrease of 0.5 Tg Nr/yr.

greenhouse effect strat. ozone depletion

smog PM-2.5

Terrestrial

Aquatic

Acidification Biodiversity loss

Eutrophication

22.8 Agricultural Populated

Acidification Vegetated

Biodiversity loss

Page 29: Fertilizer Industry St. Petersburg, FL A Wicked Troika - · PDF fileA Wicked Troika Food Security, Fertilizer and the Environment : November 16, 2011 Otto C. Doering, III Professor

U.S. Trends in Corn Grain Produced per unit Applied Fertilizer N

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For the US, there are several actions that can be taken to decrease both Nr creation, and Nr losses to the environment:

• Fossil fuel combustion • Fertilizer uptake • Feed retention • Manure management • Sewage treatment

If all were taken, there would be a 25% decrease in Nr loss to the environment.

Take Away Message

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The Challenges

What are our Food Security, Fertilizer and Environmental Challenges?

Short Term - Long Term

Public Sector - Private Sector

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A Start

Where Do We Start?

Recognizing the problem - building consensus Defining the problem in terms of its nature Aligning institutions with the integrated job to be done Metrics Matter Setting Goals for Action

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Our Earth