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The “pre‐sidedress nitrogen test (PSNT)” can be used to help make more accurate nitrogen fertilizer recommendations. Originally developed by the University of Vermont, several universities have worked to determine the critical soil nitrogen levels to help identify whether a certain field would or would not respond to a sidedress nitrogen application. The PSNT can help assess the current nitrogen availability, but should be considered a guide, not a guarantee, to estimate nitrogen rates for in‐season application.
PSNT compares soil nitrate test result (as ppm NO3 ‐N) to some critical value.
Critical values range from 15 to 30 ppm NO3 ‐N.
Result above the critical level; unlikely
Is index or threshold, not necessarily a calibrated value.
Can help assess when additional nitrogen might be needed.
Not always clear how
Soil nitrogen is a moving target.
Nitrogen cycling and uptake occurs during entire growing season.
Nitrate levels drop rapidly during early vegetative growth stage (7‐leaf to 8‐leaf).
Soil nitrogen availability at any point in time is affected by field conditions, weather, timing, etc.
Simple add/subtract of inputs and outputs won’t necessarily match up with soil nitrate result.
Most valuable when used to supplement preplant soil testing.
Can be helpful when excess precipitation occurs after nitrogen application.
PSNT results may be most useful when part of nitrogen is broadcast before planting, then followed by sidedress application.
Nitrate can be highly variable across the field and even within the row, especially if nitrogen was banded.
Nitrate does not move laterally across top soil.
Collect a total of 30 to 45 soil core samples for each composite sample.
Higher frequency of soil core samples most important with preplant banded nitrogen or if manure applied
Sampling depths (see Fig. 1)
Required: Surface soil core sample from zero to 12 inches (0‐30 cm)
Optional: Separate subsoil core sample from 12 to 24 inches to verify subsoil nitrate concentrations
24 inches to verify subsoil nitrate concentrations. i. Recommendations under “normal” conditions not significantly improved with second foot
Collect subsoil core samples from alternate surface core sample locations (i.e., “everyother” probe with coring tool)
Each composite sample should represent field management zone of not more than 40 acres
Critical level applies to 4‐leaf to 6‐leaf growth stage
Typically occurs during late May through early June
Soil nitrate levels drop rapidly during onset of rapid vegetative growth (after 6‐leaf stage)
Collecting adequate number of cores per sample is crucial.
Nitrate does not move laterally through soil.
Ammonium does not move laterally through soil
Applied anhydrous ammonia (NH3 ) does move outward from injection point until hydrolyzed to ammonium form (NH4 +) when soil moisture is present
“Sets‐of‐three” approach (see Figure 2)
Simplest approach, but considered less accurate than following methods
Three (3) core samples required per location
Sample 10 to 15 locations within field zone
Take the first core sample right between two rows (e.g., 15 inches from either row in 30‐inch rows)
Take second core sample 3 inches away from row to left
Take third core sample at 3 inches from the row to right
Move to next location and collect next set of core samples
Composite all cores to prepare final sample from field management zone
“Sets‐of‐five” approach (see Figure 3)
Preferred method when nitrogen fertilizer band position is known.
Five (5) cores required per sampling zone
Sample 7 to 8 locations within field zone
Take first core sample from band position
Take next core sample one‐fourth (1/4th) of distance between bands and perpendicular to band direction
Take next core sample one‐half (1/2) of distance between bands and perpendicular to band direction
Repeat previous two steps on opposite side of band
Move to next location and collect next set of core samples
Composite all cores to prepare final sample from field management zone
“Sets‐of‐eight” approach (see Figure 4)
Is more complicated, but considered more accurate.
Preferred approach when nitrogen fertilizer is broadcast or fertilizer band location is not known
Eight (8) cores required per sampling zone
Sample 4 to 5 locations within field zone
Collect first core sample directly in row
Move laterally to next row and collect second core sample perpendicular to row and 1/8th of row spacing distance
Move laterally to next row and collect third core sample perpendicular to this row and twoeighths (2/8ths or 1/4th) of row spacing distance
Move laterally to next row and collect fourth core sample perpendicular to this row and three‐eighths (3/8ths) of row spacing distance
Repeat progressively until total of eight core samples are collected from location
Move to next location and collect next set of core samples
Composite all cores to prepare final sample from field management zone
Analyze nitrate‐nitrogen (NO3 ‐N) on all samples
Additional analysis for ammonium‐nitrogen (NH4 ‐N) in selected situations
Significant ammonium levels most likely if one or more of following conditions have occurred:
Anhydrous ammonia was primary fertilizer source and soil temperature in application zone has been consistently 60°F or below following application
Nitrification inhibitor was used a) e.g., nitrapyrin or dicyandiamide (DCD)
Soil pH was below 5.5
In these situations, low levels of soil nitrate may indicate limited conversion of ammonium to nitrate, rather than simply loss of nitrate
Accurate interpretation requires proper number of core samples in composite sample from field management zone
No firm agreement on just how much nitrogen is needed when PSNT result is less than critical level
Critical level of 25 ppm NO3 ‐N appears common for eastern, higher‐rainfall corn‐growing areas
Typically have low subsoil nitrate levels at planting
Colorado State research suggests critical level for western, lower‐rainfall corn‐growing areas may be about 15 ppm NO3 ‐N
Typically have higher subsoil nitrate levels at planting than higher‐rainfall areas
Nitrogen rate should be higher when PSNT result is closer to zero; lower rate needed when PSNT result is closer to critical value
How much lower or higher is not always clear
Expect that any additional nitrogen would be beneficial in at least nine of ten situations when PSNT result is below critical levels, according to research
Recommended nitrogen rate is likely to be beneficial, but also likely to be more than needed for optimum yields in one of every three situations
Probably most useful under “normal” conditions
Following equation provides reasonable estimate of Iowa State nitrogen recommendations using PSNT:
Nrec = [(25 ‐ PriceFactor ) ‐ SoilTestN ) * 8 ] * CropAdjustment, where:
Nrec = lb N/ac, recommended in‐season nitrogen fertilizer application rate
25 = critical level as ppm NO3 ‐N
PriceFactor = adjustment based on favorable or unfavorable grain/fertilizer ratio (see Table 1)
SoilTestN = 0 ‐ 12" soil test nitrate as ppm NO3‐ N from PSNT samples
8 = assumes 8 lb. preplant N raises soil nitrate test by 1 ppm
CropAdjustment = multiplier when manure or alfalfa is in rotation (see Table 1).
Grain/fertilizer ratio
Ratio of bushels of corn required to buy some amount of nitrogen fertilizer
Favorable ratio
1 bushel buys about 7 lb. nitrogen
About 100 to 120 bushels of corn required to buy one ton of anhydrous ammonia (82‐0‐0)
About 35 to 40 bushels of corn required to buy a ton of nitrogen solution (28‐0‐0)
Unfavorable ratio
1 bushel of corn buys about 15 lb. nitrogen
About 200 to 250 bushels of corn required to buy a ton of anhydrous ammonia (82‐0‐0)
About 70 to 90 bushels of corn required to buy a ton of nitrogen solution (28‐0‐0)
Price factor adjustment
• Favorable grain/fertilizer ratio
0
• Unfavorable grain/fertilizer ratio
5
Crop Adjustment Multiplier
• Corn following corn
0.00
• Corn following soybeans
0.00
• Corn following alfalfa
• Favorable grain/fertilizer ratio
0.65
• Unfavorable grain/fertilizer ratio
0.75
• Manure applied in two of prior four years
• Favorable grain/fertilizer ratio
0.65
• Unfavorable grain/fertilizer ratio
0.75
Considered more appropriate for situations with severe potential for fertilizer nitrogen losses
25 ppm NO3 ‐N critical level may not be appropriate
Collect samples no later than 6‐leaf growth stage
Nitrogen cycling and uptake occurs during entire growing season
Soil nitrate decreases rapidly after 7‐leaf to 8‐ leaf growth stage
Separate surface and subsoil samples are recommended (0 to 12 in. and 12 to 24 in.)
Assumes excess rainfall has depleted both surface and subsurface nitrogen
About one‐third of fertilizer nitrogen typically found in lower root zone under “normal” rainfall
Requires NO3 ‐N or NO3 ‐N plus NH4 ‐N results
Required depth: Surface soil core sample from zero to 12 inches
Optional depth: Separate subsoil core sample from 12 to 24 inches
Analyze for nitrate only
Used to verify subsoil nitrate concentrations
Collect subsoil core samples from alternate surface core sample locations (i.e., “every‐other” probe with coring tool)
Core sample #1 and subsequent odd‐numbered core samples: Both 0" ‐ 12" and 12" – 24"
Core sample #2 and subsequent even‐numbered core samples: 0" – 12" only
Following equation provides reasonable estimate of Purdue nitrogen recommendations using PSNT:
Nrec = [ExpectedN ‐ SoilTestN ) * 5, where:
Nrec = lb N/ac, recommended in‐season nitrogen fertilizer application rate
ExpectedN = expected ppm NO3 ‐N or ppm NO3 ‐N+NH4 ‐N from Table 2 at original
SoilTestN = ppm NO3 ‐N or ppm NO3 ‐N+NH4 ‐ N from soil sample results
5 = suggested fertilizer nitrogen rate; assumes 5 lb nitrogen required for each 1 ppm reduction of SoilTestN below ExpectedN
Suggested nitrogen rate assumes corn is healthy and remaining growing season is expected to be “normal” or “typical”
Fertilizer N rate applied before rains began
ppm NO3 ‐N only*
ppm NO3 ‐N+ ppm NH4 ‐N**
130
30
36
140
32
39
150
36
42
160
38
44
170
41
47
180
44
50
190
47
53
200
50
56
210
52
58
220
55
61
230
58
64
240
61
67
* Assumes background level of ammonium at 6 ppm and “normal” levels of soil N below the 12‐inch sampling depth.
** Assumes “normal” levels of soil N below the 12‐inch sampling depth.
Magdoff, F., D. Ross, and J. Amadon. 1984. A soil test for nitrogen availability to corn. Soil Sci. Soc. Am. J. 48:1301‐1304.
Bauder, T. and R. Waskom. 2003. Best management practices for Colorado corn. Colorado State Univ. Ext. Bull XCM574A. pg. 58.
Spellman, D.E., et. al. 1996. Pre‐sidedress nitrate soil testing to manage nitrogen fertility in irrigated corn in a semi‐arid environment. Comm. Soil Sci. Plant Anal. 27:561‐574.
Blackmer, A.D. and R.D. Voss. 1997. Nitrogen Fertilizer Recommendations for Iowa. Iowa State Univ. Coop. Ext. Publication Pm‐1714. 4 pg.
Shapiro, C. & G. Hergert. 2013. “With heavy rains, how likely is N leaching” in Univ. of Nebraska Coop. Ext. Svc. “CropWatch” newsletter. 31 May 2013. https://cropwatch.unl.edu/heavy‐rains‐how‐likely‐n‐leaching‐unlcropwatch‐ may‐31‐2013 accessed 18March2019.
Sawyer. 2016. Late‐Vegetateive Corn Stage Soil Sampling for Nitrate‐N. Integrated Crop Mgmt. News. Iowa State Univ. http://crops.extension.iastate.edu/cropnews/2016/06/late‐vegetativecorn‐ stage‐soil‐sampling‐nitrate‐n, accessed 14July2016.
Camberato, J. and R.L. Nielsen. 2017. Soil Sampling to Assess Current Soil N Availability. Agronomy Dept., Purdue Univ., West Lafayette, IN. http://www.kingcorn.org/news/timeless/AssessAvailableN.html accessed 12March2019.
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