Horizon Net Zero Dawn – keynote slides by Ben Abraham
September 1 - 0130 - Vinayak Shedekar
1. Water and Nutrient Losses from
long-term soil health systems
Vinayak Shedekar
Research Scientist, Dept. of Food, Agricultural and Biological Engineering
The Ohio State University, Columbus, Ohio
Will Osterholz
Research Soil Scientist, USDA-ARS Soil Drainage Research Unit, Columbus, Ohio
Michael Brooker, Nathan Stoltzfus, Chris McNabb, Will Osterholz, Margaret Kalcic,
Jay Martin, Jed Stinner, Kevin King, Greg LaBarge
2. Michalak et al. 2013
NOAA
Phosphorus Nitrogen
SOIL DRAINAGE RESEARCH UNIT
3. Cover crops and no-till can improve
soil health
SOIL DRAINAGE RESEARCH UNIT
4. Cover crops and no-till can improve
soil health?
2.3 2.7
3.7 3.0
4.3
0
1
2
3
4
5
CT noCC 2Yr CC 10Yr Hay LT CC LT CC
SOM (%)
WardLab A&Llab
Biological Indicators
30 yr 45+ yr
30 yr 45+ yr
Transitional Mature
Transitional Mature
SOIL DRAINAGE RESEARCH UNIT
5. 5
THEOHIOSTATEUNIVERSITYCOLLEGEOFFOOD,AGRICULTURAL,ANDENVIRONMENTALSCIENCES
3. Soil health, cover crops and water quality
We know how soil health practices can improve
soil health and profitability. But…
“Good soil health” = “Good water quality”?
How do cover crops affect water and P loss?
Does it matter if the soil health systems are…
• Mature vs Transitional?
Can we scale-up soil health benefits to water
quality at watershed scales?
6. Soil health and water quality
nexus in sustainable
agroecosystems
OSU
Vinayak Shedekar
Nathan Stoltzfus
Chris McNabb
Mike Brooker
Jay Martin
Greg LaBarge
Alan Sundermeier
(Retired)
Margaret Kalcic
(University of Wisconsin)
USDA-ARS
Will Osterholz
Kevin King
Jed Stinner
NCR SARE funded Research & Extension Grant (LNC20-439)
SOIL DRAINAGE RESEARCH UNIT
8. Soil health assessment
• Organic matter
• C and N enzyme activity
• Wet aggregate stability
• POX-C
• Soil Protein
• Respiration
• Haney soil health test
• PLFA (microbes)
SOIL DRAINAGE RESEARCH UNIT
9. SC Ohio – Organic matter (%)
SOIL DRAINAGE RESEARCH UNIT
DB
MH
11. SC Ohio – Water stable aggregates
SOIL DRAINAGE RESEARCH UNIT
DB-T
MH
DB
12. Edge-of-field water quantity and quality monitoring
Flow meter
Automated water
sampler
Battery and heater
H-flume
V-notch weir
Solar panel
Rain gauge
SOIL DRAINAGE RESEARCH UNIT
15. THEOHIOSTATEUNIVERSITYCOLLEGEOFFOOD,AGRICULTURAL,ANDENVIRONMENTALSCIENCES
Research
About me
NCR SARE funded Research & Extension Grant (LNC20-439)
~2 in./yr (~15% )
less water discharge
12 lb/acre/yr (~50%)
less nitrate loss
0.05 lb/acre/yr
(~25%)
less dissolved P
loss
SH No SH
SH No SH
SH No SH
Mature SH vs No SH
Preliminary Results
(2021)
Does it matter if the soil health systems
are…
Mature vs Transitional vs under No SH
Practices?
1 in = 2.54 cm
1lb/ac = 1.12 kg/ha
16. Total water discharge
Jan. 2021 – Dec. 2021
LT Soil Health No SH
practices
LT Soil
Health
No SH practices
30
20
10
0
Water
discharge (cm)
17. Tile Flow after 1.6 cm(0.6) in rainfall event (Mar. 12, 2021)
1,173 m3
945 m3 = 0.78 cm = 50%
= 0.43 cm = 28%
Flow rate
(cfs)
Rainfall
(in)
19. SOIL DRAINAGE RESEARCH UNIT
Nitrate Concentrations
Jan. 2021 – Dec. 2021
LT Soil Health Conventional LT Soil Health Conventional LT Soil
Health
Conventional
LT Soil
Health
Conventional
Nitrate Load (lbs/ac)
1lb/ac = 1.12 kg/ha
20. SOIL DRAINAGE RESEARCH UNIT
Nitrate loads compared to USDA-ARS edge-of-field sites
1lb/ac = 1.12 kg/ha
21. SOIL DRAINAGE RESEARCH UNIT
DRP Concentrations
Jan. 2021 – Dec. 2021
LT Soil
Health
Conventional LT SH Conventional LT
SH
Conv. LT
SH
Conv.
DRP Load (lbs/ac)
1lb/ac = 1.12 kg/ha
22. SOIL DRAINAGE RESEARCH UNIT
DRP loads compared to USDA-ARS edge-of-field sites
1lb/ac = 1.12 kg/ha
23. SOIL DRAINAGE RESEARCH UNIT
Total P Concentrations
Jan. 2021 – Dec. 2021
LT Soil
Health
Conventional LT SH Conventional LT
SH
Conv. LT
SH
Conv.
Total P Load (lbs/ac)
1lb/ac = 1.12 kg/ha
25. SOIL DRAINAGE RESEARCH UNIT
Thanks to the cooperating farmers
and OSU and ARS technicians!
26. Preliminary findings suggest that long-term
soil health practices improve water quality:
• Less volume of water discharge through both tile drainage and
surface runoff
• Lower DRP and TP losses, despite greater DRP and TP
concentrations in surface runoff
• Lower concentrations and losses of nitrate
• For conclusive evidence … long-term monitoring is
crucial
SOIL DRAINAGE RESEARCH UNIT
27. THEOHIOSTATEUNIVERSITYCOLLEGEOFFOOD,AGRICULTURAL,ANDENVIRONMENTALSCIENCES
Research
About me
NCR SARE funded Research & Extension Grant (LNC20-439)
~5 cm/yr (~15% )
less water discharge
13 kg/ha/yr (~50%)
less nitrate loss
0.06 kg/ha/yr (~25%)
less dissolved P
loss
SH No SH
SH No SH
SH No SH
Mature SH vs No SH
Preliminary Results
(2021)
Does it matter if the soil health systems
are…
Mature vs Transitional vs under No SH
Practices?
28. Soil Health and Water Quality
For more information
contact Vinayak at: shedekar.1@osu.edu
Will at: will.osterholz@usda.gov
Funding support
North Central Region SARE Research & Extension Grant Program
North Central Region SARE Partnership Grant Program
Healthy Soil Healthy Environment Extension Signature Program
USDA-NIFA AFRI Foundational Science Program
Editor's Notes
In Ohio the water quality conversation is dominated by phosphorus, and rightly so because P runoff from farms causes massive algae blooms in Lake Erie. However, the area we’re at today drains to the Gulf of Mexico, where the bigger concern is nitrate. So I’ll cover our bases and touch on both phosphorus and nitrogen losses today.
There has been more and more research coming out showing that cover crops and no-till can improve soil health, especially when they’re combined. These practices are the core of regenerative ag systems
These are some results from an earlier project (SARE partnership grant project with Alan Sundermeier, Vinayak Shedekar and Rafiq Islam) looking at a few indicators of soil health across a spectrum of soil health practices.
Soil organic matter, the number soil property we look at when thinking about soil health.
May take 10+ years to realize these benefits!
Rainfall at DB = 0.59 inches
DB1: Event samples start at <arch 11, 19 or 20hour, end at midnight – 5hour flow event
Total Flow at DB1 = 6047.4
DB3: No runoff
MH1: Event samples start at March 11, 19hour, end at midnight
MH3:No runoff
DB1 flows Feb. 22 to Feb. 23
MH1 (Tile): Flow starts Feb 22, 7AM and ends Feb. 23, 7pm
DB3 flows from Feb. 23 at 9pm to Feb 23 at 1am
MH3: Shows bottles – but no flow on Feb. 22 and 23. Starts flowing on Feb. 24, at 12noon, ends at Feb. 24, 10pm
Cover crops are very effective for reducing nitrate concentrations and loads – we’ve seen this at other locations in Ohio, and researchers in other states have also found the same.
While the concentration difference is important, it’s really the reduction in drainage that is the big driver of the load difference
10 ppm is the EPA drinking water advisory limit
I wanted to put these losses in a bit of context, and luckily my ARS unit has a huge dataset of edge-of-field data from 40 fields in Ohio
These USDA fields are all located in the northwest quadrant of the state, so there are some soils differences
Point out these are averages of 4 to 9 years of monitoring, not an ideal comparison with one year of data but I think it’s still informative. We lucked out a bit in that 2021 was not an extreme high or low precipitation year.
Now the layout of this graph is a little different, instead of having the surface and tile stacked they’re side-by-side
Subsurface drainage accounts for about 90% of the annual NO3-N loss, similar to what we saw from DB and MH
So based on just this one year of data DB would be right at the low end of what we see across this network, MH is more middle of the pack.
We’ve seen in other sites that cover crops are associated with marginal increase in DRP concentrations in tile drainage
It’s the reduction in discharge really driving the effect
The line is at 0.05 ppm, the GLWQ Agreement target
Subsurface drainage accounts for about 70% of the annual DRP loss
Greatest P losses from fields have history of applying manure at N rates and have built up STP concentrations >300ppm and have applied P prior to large rain events