Moving Forward with Fertilizer Management: The Carrot...
Transcript of Moving Forward with Fertilizer Management: The Carrot...
Moving Forward with Fertilizer
Management:
The Carrot or the Stick?
Rob Mikkelsen/Rob Norton
Director, Western North America
Director, Australia & New Zealand
Dr. Rob MikkelsenWestern RegionMerced, [email protected]
The Californian Challenge
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Gross Farm gate value for Australia $41.8 billion (NFF)
Merced
T.K. Hartz, UC Davis
Crop Production Value (Millions) Commodity Value US $M
Grapes (all) 2,937
Almonds (shelled) 2343
Nursery Products 2,273
Alfalfa and other hay 1797
Lettuce (all) 1,580
Strawberries 1,578
Tomatoes (all) 1,317
Rice 1,183
Flowers/foliage 1,015
Broccoli 663
Oranges 608
Pistachio 569
Walnuts 558
Carrots 517
Lemons 473
Celery 354
Central Valley
Sacramento Valley
San Joaquin Valley
Salinas Valley
Sierra
Nevadas
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Annual average precipitation ≈ 350 cm (14 inches)T.K. Hartz, UC Davis
2 - 3 crops per year …
T.K. Hartz, UC Davis
T.K. Hartz, UC Davis
Salinas Valley
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sU.S. Fertilizer N Consumption
Source: AAPFCO Commercial Fertilizer Reports
Nitrogen in the Environment:
Sources, Problems and ManagementKitchen and Goulding (2001)
• “ nitrogen use efficiency …rarely exceeds 70% ……. often ranges from 30-60%”
• “conversion of N inputs to products for arable crops can be 60-70% or even more”
U.S. EPA SAB Integrated N Committee report on reactive N
(May 28, 2010 DRAFT): “… finds that crop N-uptake efficiencies
can be increased by up to 25% over current practices through a
combination of knowledge-based practices and advances in fertilizer
technology (such as controlled release and inhibition of nitrification).”
Nitrogen Balance in the U.S., 1987-2007
IPNI
Preliminary
NuGIS,
2010
PPI, 2002
Technical
Bulletin
Source: Fixen – 17th AFA Annual Forum and Exhibition, March, 2011. Cairo, Egypt
Some countries historically challenged with high N balances
NuGIS Watershed N Balance-1987
NuGIS Watershed N Balance-1992
NuGIS Watershed N Balance-1997
NuGIS Watershed N Balance-2002
NuGIS Watershed N Balance-2007
Partial N balance (lb N/A)
(N inputs – removal)
What’s the impact?
• Economics
• Environmental impacts
– Nitrate in drinking water
– Eutrophication & hypoxia
– Biodiversity loss
– Smog and PM2.5 from ammonia emission
– Ozone depletion – N2O
– Greenhouse gases – N2O and CO2
California’s Climate Change Policy(AB 32 Global Warming Solutions Act)
Caps GHG emissions
• 1990 levels by 2020
• 80% below 1990 by 2050
Multi-sector market-based program to start in 2012
Mandatory reporting for largest sectors
Little understanding to agriculture so far… emerging discussion
60% of N2O and 55% of CH4 are from agriculture
Draft from: UC Davis Ag Sustainability Institute
62% of N2O
emissions (&
N applied)
from 6 crops
The Key is to
Limit Potential
“Surplus N”
Van Groenigen et al. 2010. Europ. J. Soil Sci.
“ … agricultural
management
practices to reduce
N2O emissions
should focus on
optimizing fertilizer-N
use efficiency under
median rates of N
input, rather than on
minimizing N
application rates.”
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Total NAccumulationN Accumulation
Rate
Nitrogen
Matching supply and demand
• Crop type
• Temperature (=growth)
• Root depth
• Soil Texture
• Enhanced efficiency fertilizers
• Utilize non-fertilizer N
• Water management
• Etc.
• Etc.
Salinas
Santa Maria
T.K. Hartz, UC Davis
Salinas/Santa Maria surface water quality :Mean of monthly sampling of 10 monitoring sites, 2005
Water quality
parameter
Measurement
unit
Mean
value
NO3-N mg liter-1 46
U.S. drinking water
standard is 10 mg
liter-1 NO3-N
Well > 20 mg L-1 NO3-N
Groundwater at risk
Salinas Valley irrigation well quality :
In California, farm water discharge requires :
a permit, or
a waiver
„Conditional‟ waivers granted in 2004
Requirements :
Complete water quality training
Prepare a farm water quality plan
Participate in a regional water quality
monitoring program
15-hour water quality short course :
Step by step training to :
• Identify potential water quality problems
• Present potential management practice options
- fertilization
- irrigation
- conservation practices
• Evaluate effectiveness of practices
• Produce written farm water quality plan
Between 2005-07 more than 2,000 people completed the course
T.K. Hartz, UC Davis
Management practice
% of acres on which
practice was
implemented
Crop nutrient budget used 80
Soil residual nitrate tested and
factored into fertilizer decisions
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Nitrate content of the irrigation
water factored into fertilizer
decisions
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Irrigation system optimized for soil
water infiltration rate
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December, 2006 survey of vegetable growers :
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Surface water nitrate trend
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Are we making progress in water quality ?
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Nitrogen fertilizer sales in Monterey County :
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Are we making progress in water quality ?
Authority to regulate water quality :
U.S. Environmental Protection Agency
California Water Resources Control Board
Regional Water Resources Control Board
T.K. Hartz, UC Davis
59. The purpose of the nutrient management element of the Farm Plan is to eliminate or minimize nutrient discharges to groundwater and surface
water to meet water quality standards using best practicable treatment or control, and to assure compliance with this Order. The nutrient
management element of the Farm Plan must be certified by appropriate professional certification, such as Certified
Crop Advisor to be protective of water quality…
60. The nutrient management element of the Farm Plan must include…
a. Average total crop nutrient demand and method(s) of determination per crop;
b. Average total water demand per crop and total water applied per crop;
c. Monthly record of fertilizer applications per crop, including fertilizer type and quantity applied (including but not
limited to fertilizers, compost, manure, and humic acids);
d. Nitrate concentration of irrigation source water;
e. Timing of fertilizer application to maximize crop uptake,
f. Estimation of the amount of fertilizer applied in excess of crop needs,
g. Estimation of excess or residual fertilizer/nutrients in the root zone at the end of the crop growing season;
h. Identification of planned nutrient management practices (such as irrigation efficiency, nutrient budgeting, and
nutrient trapping) to eliminate or minimize nutrients in irrigation runoff or percolation to groundwater;
i. Identification of planned management practices related to fertilizer handling, storage, disposal, and mgnt
New requirements: Tiers on farm size, location, herbicides, crops grown
such as beet, broccoli, cabbage, cauliflower, celery,
chinese cabbage, collard, endive, kale, leek, lettuce,
mustard, onion, parsley, pepper, spinach and strawberry
fertilizer use reporting
farm-wide nutrient budget estimation
on-farm monitoring and reporting of NO3-N concentration
in surface runoff and root zone leachate
compliance dates to meet NO3-N standards
- 2015 for surface runoff
- 2021 for leachate
T.K. Hartz, UC Davis
kg N / ha
uptake
removal in
harvest
Processing tomato 240-280 160-180
Celery 190-220 120-150
Cantaloupe 150-180 70-90
Lettuce 110-140 60-80
Spinach 80-100 70-90
Develop a general N fertilization template for each crop,
• modify it based on field-specific factors
Account for all N inputs and outputs
Understand crop N requirements :
Certified Crop Advisors
T.K. Hartz, UC Davis
the reliable solution is to eliminate tailwater …
T.K. Hartz, UC Davis
Nitrogen loading to the environment
Basic principle :
Fertilizer N applied but not removed in harvested products are
at risk of leaving the field in surface water or groundwater
Therefore, water quality protection requires proportionality between
N application and harvest removal
T.K. Hartz, UC Davis
T.K. Hartz, UC Davis
Can a 10 PPM NO3-N standard consistently be met ?
For surface water:
irrigation runoff NO3-N mirrors irrigation water NO3-N
T.K. Hartz, UC Davis
Can a 10 PPM NO3-N standard consistently be met ?
For surface water:
will conservation practices have any impact on NO3-N?
T.K. Hartz, UC Davis
Can a 10 PPM NO3-N standard consistently be met ?
For surface water:
10 PPM NO3-N is still „biostimulatory‟
T.K. Hartz, UC Davis
Water quality regulation has the potential to disrupt nutrient
management practices, to compromise yields, and potentially
to drive land use decisions …
Importance of nutrient stewardship
• Manage or be managed
• Regulations on nutrient management
– Reef Regulations on sugar industry in the wet tropics
– Use of soluble P fertilizers on the Swan coastal plain.
– Fertilizer management in the Mississippi Basin
– Regulations on N use on particular dairy pastures in New Zealand.
• Industry BMP’s aim to describe, educate and then benchmark nutrient management.
Barriers to making these things work
• Tradition, Reliability, Cost, Complexity
• Agronomic education of growers – who pays?
• Professional work force in Agriculture?
• Not a simple business transaction.
• Technology moves faster than our capacity to adopt it.
• Everybody in the supply chain needs to make $.
• Who will do the research – highly applied
• Government mixed message and consistencyGH Regs -Methane from dairies to be regulated encourage methane
digesters
Air Resources Board: Prohibit methane combustion from bioenergy without
NOx scrubbing
IPNICommitted to sustainable nutrient management• Right source, right rate, right time, and right place is a simple
slogan that integrates a century of science and experience into nutrient stewardship.
• Who decides what is right? Who decides the best application, best method of placement, or best nutrient source?
– There is no right answer … right must be site-specific, dictated not only by soil and environmental conditions, but by social and environmental concerns and objectives.
• Research backstops the principles of 4Rs with science, but the stakeholders decide what is right.
Better Crops, Better Environment … through Science
http://www.ipni.net
http://anz.ipni.net