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Enabling the Flow of Ecosystem
Services from Agriculture to
Improve Puerto Rico’s Water Quality
and Mitigate Global Climate Change
Authors:
Dr. Luis Perez-Alegria, University of Puerto Rico
Dr. Jonathan Winsten, Winrock International
Dr. Neville Millar, Michigan State University
Mr. Fabian Carmona, University of Puerto Rico
Presenter: Dr. Kristin Fisher, Winrock International
Background
β€’ Plantain/banana is #1 crop in Puerto Rico by acres (>25% of
cropland) and annual revenue ($80.5 million).
β€’ Plantain/banana is a very important crop throughout the tropics
and grown on an estimated 10.5 million hectares.
β€’ Very limited information available on environmental impact or
ways to lessen impact.
β€’ Agriculture is the leading source NPS pollution to ground and
surface waters in the U.S.
β€’ N2O is only 6% of U.S. GHG emissions, but 79% is from
agriculture.
β€’ Nitrous oxide (N2O) has 298 times the radiative forcing of carbon
dioxide (CO2).
Approach and Methods
Goal: Lay foundation for farmers to produce ecosystem
services (water quality and/or GHG mitigation).
β€’ Working with large commercial farm on south central coast
(intensive ag area).
β€’ Taking field measurements of N2O, NO3, plant growth, and yields
from 3 treatments plus control.
β€’ Data used for cal/val of APEX model (via Nutrient Tracking Tool).
β€’ Calibrated NTT model will be available to estimate nutrient and
GHG losses in Puerto Rico.
Experimental Treatments
β€’ Control: Business as usual for farm (640 kgs N ha-1).
β€’ Treatment 1: Control release fertilizer (640 kgs N/ha-1)
β€’ Treatment 2: UPR Ag Experiment Station N rate
recommendation for plantain (241 kgs N/ha-1)
β€’ Treatment 3: No N applied (to understand lower
bound)
Manual Chambers for N2O Measurement
1
32
GHG chamber placement
Irrigation/fertigation line
Plantain row
Alley (between rows)
Plantain
GHG chamber
β€’ 3 x chamber per β€˜site’
β€’ 3 x β€˜sites’ per treatment
β€’ 4 treatments (control + 3
treatments)
β€’ 1 background chamber per
treatment
β€’ 40 chambers used per sample
day
β€’ 4 samples pulled per chamber
β€˜Top’ view
Chambers used to capture
nitrous oxide flux.
β€’ 9 chambers/treatment
Also Measuring:
β€’ Soil nutrient levels
β€’ Plant height and biomass
β€’ Plantain yield
N2O Flux Results
0.0
1.0
2.0
3.0
4.0
5.0
6.0
0 20 40 60 80 100 120 140 160
Control (BAU)
Slow release N
UPRM-AES
No additional N
kgN2O-Nha-1
Days After Planting
Lysimeters used to capture
root zone leachate.
β€’ 2 lysimeters/treatment
Gutters used to capture surface
runoff
β€’ 1 gutter/treatment
Ground Level
Nitrogen Loss and Nitrogen Use Efficiency
β€’ Measuring concentrations of N in lysimeters and
surface traps to estimate total losses.
β€’ Measuring residual N in soil and N content of plant
biomass.
β€’ Will calculate nitrogen use efficiency as contribution to
literature.
Preliminary NO3 Results
Nitrate leaching estimation procedure:
Soil moisture at any day after
planting:
𝑆𝑀𝑖+1 = 𝐼𝑅𝑖+1 + 𝑅𝑖+1 βˆ’ 𝐸𝑇𝑐𝑖+1 βˆ’ 𝑅𝑂𝑖+1 + 𝑆𝑀𝑖
Where:
𝑃𝑖+1 = 𝑆𝑀𝑖+1 βˆ’ 𝐹𝐢
𝐸𝑇𝑐 = 𝐾𝑐 πΈπ‘‡π‘œ
𝑅𝑂 =
(𝑅 βˆ’ 0.2𝑆)2
(𝑅 + 0.8𝑆)
𝑆 =
25400
𝐢𝑁
βˆ’ 254
𝑃𝑑𝑛 =
𝑃𝑖𝑑 𝐢
100
𝑃𝑖+1 = π‘ƒπ‘’π‘Ÿπ‘π‘œπ‘™π‘Žπ‘‘π‘’π‘‘ π‘€π‘Žπ‘‘π‘’π‘Ÿ π‘‘π‘’π‘π‘‘β„Ž π‘šπ‘š
𝐼𝑅𝑖+1 = π‘‡π‘œπ‘‘π‘Žπ‘™ π‘–π‘Ÿπ‘Ÿπ‘–π‘”π‘Žπ‘‘π‘–π‘œπ‘› π‘€π‘Žπ‘‘π‘’π‘Ÿ π‘œπ‘› π‘‘π‘Žπ‘¦ 𝑖 + 1 (π‘šπ‘š)
𝑅𝑖+1 = π‘…π‘Žπ‘–π‘›π‘“π‘Žπ‘™π‘™ π‘‘π‘’π‘π‘‘β„Ž π‘œπ‘› π‘‘π‘Žπ‘¦ 𝑖 + 1 π‘šπ‘š
𝐸𝑇𝑐𝑖+1 = 𝐸𝑇 π‘Žπ‘π‘π‘’π‘šπ‘’π‘™π‘Žπ‘‘π‘’π‘‘ π‘‘π‘’π‘Ÿπ‘–π‘›π‘” π‘‘π‘Žπ‘¦ 𝑖 + 1 π‘šπ‘š
𝑅𝑂𝑖+1 = π‘Šπ‘Žπ‘‘π‘’π‘Ÿ π‘™π‘œπ‘ π‘ π‘’π‘  𝑑𝑒𝑒 π‘‘π‘œ π‘Ÿπ‘’π‘›π‘œπ‘“π‘“ π‘œπ‘› 𝑖 + 1 π‘šπ‘š
𝑆𝑀𝑖 = π‘†π‘œπ‘–π‘™ π‘€π‘Žπ‘‘π‘’π‘Ÿ π‘π‘œπ‘›π‘‘π‘’π‘›π‘‘ π‘œπ‘› π‘‘π‘Žπ‘¦ 𝑖 π‘šπ‘š
𝐾𝑐 = πΆπ‘Ÿπ‘œπ‘ π‘π‘œπ‘’π‘“π‘–π‘π‘–π‘’π‘›π‘‘
𝐸𝑇0 = π‘…π‘’π‘“π‘’π‘Ÿπ‘’π‘›π‘π‘’ 𝐸𝑇 𝑏𝑦 π‘ƒπ‘’π‘›π‘šπ‘Žπ‘› βˆ’ π‘€π‘œπ‘›π‘‘π‘’π‘–π‘‘β„Ž π‘šπ‘š
𝑆 = π‘€π‘Žπ‘₯π‘–π‘šπ‘’π‘š π‘π‘œπ‘‘π‘’π‘›π‘‘π‘–π‘Žπ‘™ π‘‘π‘–π‘“π‘“π‘’π‘Ÿπ‘’π‘›π‘π‘’ 𝑏𝑒𝑑𝑀𝑒𝑒𝑛
rainfall and runoff at the moment of rainfall
initiation (mm)
𝑃𝑖𝑑 = π‘Šπ‘Žπ‘‘π‘’π‘Ÿ π‘‘π‘’π‘π‘‘β„Ž π‘π‘’π‘Ÿπ‘π‘œπ‘™π‘Žπ‘‘π‘’π‘‘ π‘šπ‘š
𝑃𝑑𝑛 = π‘‡π‘œπ‘‘π‘Žπ‘™ π‘›π‘–π‘‘π‘Ÿπ‘Žπ‘‘π‘’ π‘šπ‘Žπ‘ π‘  π‘™π‘œπ‘ π‘ 
π‘˜π‘”
β„Žπ‘Ž
𝐢 = π‘π‘–π‘‘π‘Ÿπ‘Žπ‘‘π‘’ π‘π‘œπ‘›π‘π‘’π‘›π‘‘π‘Ÿπ‘Žπ‘‘π‘–π‘œπ‘› 𝑖𝑛 π‘ π‘œπ‘–π‘™ π‘ π‘œπ‘™π‘’π‘‘π‘–π‘œπ‘›
π‘šπ‘”
𝐿
𝐢𝑁 = πΆπ‘’π‘Ÿπ‘£π‘’ π‘›π‘’π‘šπ‘π‘’π‘Ÿ, 𝑆𝐢𝑆 1972
Source: Paulino-Paulino et al. (2008). JAUPR. 92 (3-
4):135-152
Preliminary Yield Results
β€’ Wind damage affected harvest and yield measurement.
Next Steps
β€’ Field measurement results being used to cal/val NTT
model.
β€’ NTT model will be used to estimate potential
reductions across Puerto Rico.
β€’ Identify areas for greatest reductions
β€’ Calculate full economic costs and estimate C offset
supply curve
Preliminary Conclusions
β€’ Significantly reduced N2O flux from reduced N rates.
β€’ Impact on yield is still to be determined; observations
showed yields to be similar across treatments.
Further Research and Extension
β€’ Develop peer-reviewed GHG emission reduction factor
(scale) for plantain/banana based on N rate.
β€’ Work with American Carbon Registry to publish offset
methodology for β€œstacked” credits.
β€’ Education and outreach to plantain producers on
participation in environmental markets.

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  • 1. Enabling the Flow of Ecosystem Services from Agriculture to Improve Puerto Rico’s Water Quality and Mitigate Global Climate Change Authors: Dr. Luis Perez-Alegria, University of Puerto Rico Dr. Jonathan Winsten, Winrock International Dr. Neville Millar, Michigan State University Mr. Fabian Carmona, University of Puerto Rico Presenter: Dr. Kristin Fisher, Winrock International
  • 2. Background β€’ Plantain/banana is #1 crop in Puerto Rico by acres (>25% of cropland) and annual revenue ($80.5 million). β€’ Plantain/banana is a very important crop throughout the tropics and grown on an estimated 10.5 million hectares. β€’ Very limited information available on environmental impact or ways to lessen impact. β€’ Agriculture is the leading source NPS pollution to ground and surface waters in the U.S. β€’ N2O is only 6% of U.S. GHG emissions, but 79% is from agriculture. β€’ Nitrous oxide (N2O) has 298 times the radiative forcing of carbon dioxide (CO2).
  • 3. Approach and Methods Goal: Lay foundation for farmers to produce ecosystem services (water quality and/or GHG mitigation). β€’ Working with large commercial farm on south central coast (intensive ag area). β€’ Taking field measurements of N2O, NO3, plant growth, and yields from 3 treatments plus control. β€’ Data used for cal/val of APEX model (via Nutrient Tracking Tool). β€’ Calibrated NTT model will be available to estimate nutrient and GHG losses in Puerto Rico.
  • 4.
  • 5. Experimental Treatments β€’ Control: Business as usual for farm (640 kgs N ha-1). β€’ Treatment 1: Control release fertilizer (640 kgs N/ha-1) β€’ Treatment 2: UPR Ag Experiment Station N rate recommendation for plantain (241 kgs N/ha-1) β€’ Treatment 3: No N applied (to understand lower bound)
  • 6. Manual Chambers for N2O Measurement
  • 7. 1 32 GHG chamber placement Irrigation/fertigation line Plantain row Alley (between rows) Plantain GHG chamber β€’ 3 x chamber per β€˜site’ β€’ 3 x β€˜sites’ per treatment β€’ 4 treatments (control + 3 treatments) β€’ 1 background chamber per treatment β€’ 40 chambers used per sample day β€’ 4 samples pulled per chamber β€˜Top’ view
  • 8. Chambers used to capture nitrous oxide flux. β€’ 9 chambers/treatment Also Measuring: β€’ Soil nutrient levels β€’ Plant height and biomass β€’ Plantain yield
  • 9. N2O Flux Results 0.0 1.0 2.0 3.0 4.0 5.0 6.0 0 20 40 60 80 100 120 140 160 Control (BAU) Slow release N UPRM-AES No additional N kgN2O-Nha-1 Days After Planting
  • 10. Lysimeters used to capture root zone leachate. β€’ 2 lysimeters/treatment Gutters used to capture surface runoff β€’ 1 gutter/treatment Ground Level
  • 11. Nitrogen Loss and Nitrogen Use Efficiency β€’ Measuring concentrations of N in lysimeters and surface traps to estimate total losses. β€’ Measuring residual N in soil and N content of plant biomass. β€’ Will calculate nitrogen use efficiency as contribution to literature.
  • 13. Nitrate leaching estimation procedure: Soil moisture at any day after planting: 𝑆𝑀𝑖+1 = 𝐼𝑅𝑖+1 + 𝑅𝑖+1 βˆ’ 𝐸𝑇𝑐𝑖+1 βˆ’ 𝑅𝑂𝑖+1 + 𝑆𝑀𝑖 Where: 𝑃𝑖+1 = 𝑆𝑀𝑖+1 βˆ’ 𝐹𝐢 𝐸𝑇𝑐 = 𝐾𝑐 πΈπ‘‡π‘œ 𝑅𝑂 = (𝑅 βˆ’ 0.2𝑆)2 (𝑅 + 0.8𝑆) 𝑆 = 25400 𝐢𝑁 βˆ’ 254 𝑃𝑑𝑛 = 𝑃𝑖𝑑 𝐢 100 𝑃𝑖+1 = π‘ƒπ‘’π‘Ÿπ‘π‘œπ‘™π‘Žπ‘‘π‘’π‘‘ π‘€π‘Žπ‘‘π‘’π‘Ÿ π‘‘π‘’π‘π‘‘β„Ž π‘šπ‘š 𝐼𝑅𝑖+1 = π‘‡π‘œπ‘‘π‘Žπ‘™ π‘–π‘Ÿπ‘Ÿπ‘–π‘”π‘Žπ‘‘π‘–π‘œπ‘› π‘€π‘Žπ‘‘π‘’π‘Ÿ π‘œπ‘› π‘‘π‘Žπ‘¦ 𝑖 + 1 (π‘šπ‘š) 𝑅𝑖+1 = π‘…π‘Žπ‘–π‘›π‘“π‘Žπ‘™π‘™ π‘‘π‘’π‘π‘‘β„Ž π‘œπ‘› π‘‘π‘Žπ‘¦ 𝑖 + 1 π‘šπ‘š 𝐸𝑇𝑐𝑖+1 = 𝐸𝑇 π‘Žπ‘π‘π‘’π‘šπ‘’π‘™π‘Žπ‘‘π‘’π‘‘ π‘‘π‘’π‘Ÿπ‘–π‘›π‘” π‘‘π‘Žπ‘¦ 𝑖 + 1 π‘šπ‘š 𝑅𝑂𝑖+1 = π‘Šπ‘Žπ‘‘π‘’π‘Ÿ π‘™π‘œπ‘ π‘ π‘’π‘  𝑑𝑒𝑒 π‘‘π‘œ π‘Ÿπ‘’π‘›π‘œπ‘“π‘“ π‘œπ‘› 𝑖 + 1 π‘šπ‘š 𝑆𝑀𝑖 = π‘†π‘œπ‘–π‘™ π‘€π‘Žπ‘‘π‘’π‘Ÿ π‘π‘œπ‘›π‘‘π‘’π‘›π‘‘ π‘œπ‘› π‘‘π‘Žπ‘¦ 𝑖 π‘šπ‘š 𝐾𝑐 = πΆπ‘Ÿπ‘œπ‘ π‘π‘œπ‘’π‘“π‘–π‘π‘–π‘’π‘›π‘‘ 𝐸𝑇0 = π‘…π‘’π‘“π‘’π‘Ÿπ‘’π‘›π‘π‘’ 𝐸𝑇 𝑏𝑦 π‘ƒπ‘’π‘›π‘šπ‘Žπ‘› βˆ’ π‘€π‘œπ‘›π‘‘π‘’π‘–π‘‘β„Ž π‘šπ‘š 𝑆 = π‘€π‘Žπ‘₯π‘–π‘šπ‘’π‘š π‘π‘œπ‘‘π‘’π‘›π‘‘π‘–π‘Žπ‘™ π‘‘π‘–π‘“π‘“π‘’π‘Ÿπ‘’π‘›π‘π‘’ 𝑏𝑒𝑑𝑀𝑒𝑒𝑛 rainfall and runoff at the moment of rainfall initiation (mm) 𝑃𝑖𝑑 = π‘Šπ‘Žπ‘‘π‘’π‘Ÿ π‘‘π‘’π‘π‘‘β„Ž π‘π‘’π‘Ÿπ‘π‘œπ‘™π‘Žπ‘‘π‘’π‘‘ π‘šπ‘š 𝑃𝑑𝑛 = π‘‡π‘œπ‘‘π‘Žπ‘™ π‘›π‘–π‘‘π‘Ÿπ‘Žπ‘‘π‘’ π‘šπ‘Žπ‘ π‘  π‘™π‘œπ‘ π‘  π‘˜π‘” β„Žπ‘Ž 𝐢 = π‘π‘–π‘‘π‘Ÿπ‘Žπ‘‘π‘’ π‘π‘œπ‘›π‘π‘’π‘›π‘‘π‘Ÿπ‘Žπ‘‘π‘–π‘œπ‘› 𝑖𝑛 π‘ π‘œπ‘–π‘™ π‘ π‘œπ‘™π‘’π‘‘π‘–π‘œπ‘› π‘šπ‘” 𝐿 𝐢𝑁 = πΆπ‘’π‘Ÿπ‘£π‘’ π‘›π‘’π‘šπ‘π‘’π‘Ÿ, 𝑆𝐢𝑆 1972 Source: Paulino-Paulino et al. (2008). JAUPR. 92 (3- 4):135-152
  • 14. Preliminary Yield Results β€’ Wind damage affected harvest and yield measurement.
  • 15. Next Steps β€’ Field measurement results being used to cal/val NTT model. β€’ NTT model will be used to estimate potential reductions across Puerto Rico. β€’ Identify areas for greatest reductions β€’ Calculate full economic costs and estimate C offset supply curve
  • 16. Preliminary Conclusions β€’ Significantly reduced N2O flux from reduced N rates. β€’ Impact on yield is still to be determined; observations showed yields to be similar across treatments.
  • 17. Further Research and Extension β€’ Develop peer-reviewed GHG emission reduction factor (scale) for plantain/banana based on N rate. β€’ Work with American Carbon Registry to publish offset methodology for β€œstacked” credits. β€’ Education and outreach to plantain producers on participation in environmental markets.

Editor's Notes

  1. As expected, N2O emissions from UPR recommendation and from no N added treatments are significantly lower than BAU or Slow release treatment.