Proceedings of the 2007 CPM Short Course and MCPR Trade Show

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Proceedings of the 2007 CPM Short Course and MCPR Trade Show December 4 6, 2007 Minneapolis Convention Center Do not Reproduce or Redistribute Without Written Consent of the Author(s)

Soil N Mineralization and the Value of Soil N Testing Larry G. Bundy Dept. of Soil Science Univ. of Wisconsin

Overview Why is soil N mineralization important? Can N mineralization be measured? Is there potential for future improvement? What soil N tests are useful?

Nitrogen Mineralization Temperature Moisture Climate Cropping system Soil properties C & N inputs Organic N Mineralization Immobilization Inorganic N Losses

Contribution of Soil N to Yield State CC SC -------- % 1/ -------- Illinois 54 64 Iowa 45 75 Minnesota 60 76 Wisconsin 71 77 Mean 2/ 56 70 1/ Yield with zero N as % of yield at EONR. 2/ Mean of 271 CC and 427 SC sites. Sawyer et al., 2005.

Contribution of soil N & fertilizer N to corn yield in WI Yield, bu/acre 200 Control (no N) EONR 150 100 50 0 n = 26 n = 27 n = 7 CC SC CC HYPS HYPS MYPS Soil N contributes most of crop N need Reliable estimates of this contribution are needed Major effects on N efficiency and potential losses

Nitrogen Mineralization Temperature Moisture Climate Cropping system Soil properties C & N inputs Organic N Mineralization Immobilization Inorganic N Losses

Importance of N Mineralization Estimates Essential for improved N rate recommendations Many attempts to develop methods None have proven satisfactory

Current Status of N Mineralization Tests Chemical tests Soil treated/extracted with chemical Product of treatment measured Correlation between product and N mineralization or crop response

Cropping System Effects PBB N Availability Test Corn - Corn Soybean - Corn 140 100 Yield, bu/acre 120 100 80 60 40 20 r = 0.76** Rel. yield (%) 80 60 40 20 r = 0.24NS 0 0 0 5 10 15 20 25 0 10 20 30 40 50 60 ppm N ppm N Vanotti et. al. (1995) Schoessow (1996) Gianello and Bremmer (1988)

Basis for the Illinois Soil N Test Amino sugar-n fraction related to corn N response (Mulvaney et al. 2001) Illinois soil N test (ISNT) proposed (Khan et al. 2001) Measures amino sugar-n plus other soil N components Related to amino sugar N fraction Related to corn N response

Results with the Illinois soil nitrogen test in Wisconsin 300 250 Critical value of 225 mg kg -1 EONR (kg ha -1 ) 200 150 100 50 0 r 2 = 0.0013 n = 80 0 50 100 150 200 250 300 350 400 ISNT (mg kg -1 )

Relationship of ISNT to soil organic matter - Wisconsin 400 300 y = 12.9715 + 62.5734x r 2 = 0.88 n = 80 ISNT (mg kg -1 ) 200 100 0 0 1 2 3 4 5 Organic matter (%)

Yield optimizing N rate (kg ha -1 ) 400 300 200 100 Regional ISNT vs. YONR 0 (Laboski et al., 2006) IA (n = 43) IL (n = 5) MI (n = 4) MN (n = 1) NE (n = 34) WI (n = 9) R 2 = 0.22*** n = 96 0 100 200 300 400 500 600 ISNT, 0-15 cm (mg kg -1 ) *** Statistically significant at the 0.001 probability level

Regional ISNT vs. SOM (Laboski et al., 2006) Soil organic matter, 0-15 cm (%) 10 8 6 4 2 0 y = -0.21 + 0.015x R 2 = 0.91*** n = 96 IA (n = 43) IL (n = 5) MI (n = 4) MN (n = 1) NE (n = 34) WI (n = 9) 0 100 200 300 400 500 600 ISNT, 0-15 cm (mg kg -1 ) *** Statistically significant at the 0.001 probability level

SUMMARY-ISNT The ISNT is not a reliable predictor of corn N response. The ISNT is measuring a constant fraction of the soil organic N rather than the readily mineralizable component.

Current Status of N Mineralization Biological tests Tests Usually soil incubation under fixed conditions Inorganic N production measured Correlation between mineralized N and crop response Strength is that same processes are used as under field conditions

Regional Evaluation of N Mineralization Tests 1/ Seven states in NC region, 67 sites (IL, KS, MI, MN, MO, NE, WI) EONR for corn measured at each site 16 chemical and biological tests Relationship between test result and EONR determined 1/ NC-218 Regional Research Committee

Relationship between N availability tests and corn EONR at 67 sites in the Chemical test NC region Relationship (r) Phosphate borate buff. (11.2) dist., 8 min 0.07 Dist. with 2M KCl + MgO, 8 min -0.01 Incubation with hot 2M KCl, 20 hr. 0.08 Na borate buff. dist (11.5), 8 min. <0.01 Na tetraphenylboron extraction, 5 min -0.10

Relationship between N availability tests and corn EONR at 67 sites in the Biological test NC region Relationship (r) Long-term (300 d) aerobic incub. (N o ) -0.11 Aerobic incub. (14-d, 30 o C), soil:sand -0.41** Anaerobic incub. (14-d, 30 o C), moist -0.12 Anaerobic incub. (14-d, 30 o C), air dried -0.03 Preplant soil nitrate test (0-3 ft) -0.13 Presidedress soil nitrate test (0-1 ft) -0.26 Presidedress soil nitrate test (0-2 ft) -0.27

Site-specific Aerobic Soil Incubation Soil collected from no-n control plots in 10 rotations in 1996. Rotations ranged from cont. corn to corn following alfalfa Aerobic incubation for 16 wk at 25 o C Mineralized N correlated with corn yield in 1996, 1997 and 1987-1996

Relationship between N mineralized during aerobic soil incubation and corn yield in crop rotations, Lancaster, WI 1/ Incubation Year weeks 1996 1997 1987-1996 ------------ r 2 ------------ 2 0.75 0.14 0.33 4 0.82 0.49 0.69 8 0.88 0.54 0.72 10 0.92 0.72 0.72 14 0.92 0.72 0.60 16 0.70 0.54 0.50 1/ van Schaik (1998)

Aerobic Soil Incubation - Results Best relationships found at 10 wk. Good r 2 for 1996, 1997, and 1987-1996 Suggests that site-specific N mineralization data from one year may be useful for predicting N needs in future years

Delta Yield A reasonable substitute for soil N supplying capability? Yield @ EONR Yield w/ no N Reflects N mineralization plus site factors

Delta Yield ( Y) Kachanoski et al. (1996) 300 expts., 1962-1992 No yield vs. EONR relationship Y vs. EONR (r 2 = 0.5 to 0.75)

Delta Yield ( Y) Lory and Scharf (2003) 298 expts. (IL, MN, MO, PA, WI) Yield vs. EONR (r 2 = 0.02) Y vs. EONR (r 2 = 0.47)

Soil-Based Measurements Preplant residual nitrate tests A component of soil N supplying capability Semi-arid and some humid regions Generally underutilized

Residual Nitrate Testing- Low Rainfall Areas Long history in low rainfall areas Recommended test for western Minnesota N rates adjusted according to equation: NG=(N rec for C-C) (0.6 x STN (0-24 in) )

Residual Nitrate Testing- Humid Areas Measures residual (carryover) nitrate Corn after corn Medium- and fine-textured soils Normal or below normal rainfall Available N exceeds crop need Not useful on sands, loamy sands

Residual N Credit for Spring Preplant Soil Nitrate (0-2 ft) Soil nitrate-n Residual N credit ppm lb N/acre 0-6 0 6.1-9 35 9.1-12 65 12.1-15 95 15.1-18 125 > 18 155

Soil-Based Measurements Presidedress soil nitrate tests Estimates N mineralization Identifies nonresponsive sites Temperature sensitivity underestimates N mineralization

Temperature effects on accuracy of PSNT-based N recommendations Percentage of sites 100 80 60 40 20 0 Correct Over-applied Under-applied 76 59 37 16 4 7 Below (n=46) Average or above (n=55) May-June average temperature

May-June temperature effects on PSNT-based N recommendations Excess N rate (kg / ha) 210 175 140 105 70 35 Soil yield potential Series1 Medium (n=45) Series2 High (n=56) 0-35 -2.5-1.5-0.5 0.5 1.5 2.5 Temperature departure ( o C)

Nitrogen rates based on yield response data Net return to N ($/a) 100 80 60 40 20 0 N:Corn price ratio 0.05 0.10 0.15 0.20 CC - High Yield Potential Soils When similar soils and cropping systems are grouped, the data base reflects the average soil N supplying capability 0 50 100 150 200 250 N rate (lb/a)

Nitrogen Rate Guidelines-Minnesota* N/corn value ratio Corn/corn Corn/soybean MRTN Range MRTN Range ------------- lb N/acre ------------ 0.05 155 130-180 120 100-140 0.10 140 120-165 110 90-125 0.15 130 110-150 100 80-115 0.20 120 100-140 85 70-100 * Highly productive soils

Potential for Future Improvements Compile field-specific N mineralization info. from aerobic incubations Consider delta yield ( Y) as substitute for N mineralization measurements.

Potential for Future Improvements Tests or groups of tests must be related to crop N response in the field Use applied modeling approach to integrate factors contributing to soil N supplying capability

Potential for Future Improvements Integrate info. from individual procedures Employ under-utilized field-based tests Soil nitrate testing Crop sensing techniques N rate guidelines based on N response functions incorporate average soil N supplying capability

Potential for Future Improvements Improved estimates of N mineralization will: Require higher level of management Increase management costs Higher N prices and environmental requirements may provide incentive