Nitrate in groundwater has the potential to provide a substantial amount of plant-available nitrogen to crops. Accounting for the nitrate in irrigation water allows for substantial decreases in fertilizer costs. To measure the concentration of your irrigation water, you can have the nitrate content analyzed at a commercial test lab. It is important to note that results from these tests can be expressed in units of ppm NO3- or ppm NO3-—N. The more useful measurement for calculating irrigation water contribution to plant-available N is NO3-—N. To convert from NO3- to NO3-—N, multiply your ppm NO3- by 0.225.
EXAMPLE:
A recent study1 showed that nitrate concentrations in ground water can consistently reach concentrations greater than 45 ppm NO3-. To convert this nitrate content to lbs N supplied per acre-foot of water, we must first convert from 45 NO3- to NO3—N, (45 ppm NO3-*0.225 = 10ppm NO3—N). Using the table below, 10ppm NO3—N would translate to 27 lbs of plant-available nitrogen per acre-foot of irrigation applied.
| Concentration of nitrate-N in ppm (mg/L) | ||||||||||
Acre-Ft | 1 | 5 | 10 | 15 | 20 | 25 | 30 | 35 | 40 | 45 | 50 |
0.1 | 0 | 1 | 3 | 4 | 5 | 7 | 8 | 10 | 11 | 12 | 14 |
0.2 | 1 | 3 | 5 | 8 | 11 | 14 | 16 | 19 | 22 | 25 | 27 |
0.3 | 1 | 4 | 8 | 12 | 16 | 21 | 25 | 29 | 33 | 37 | 41 |
0.4 | 1 | 5 | 11 | 16 | 22 | 27 | 33 | 38 | 44 | 49 | 55 |
0.5 | 1 | 7 | 14 | 21 | 27 | 34 | 41 | 48 | 55 | 62 | 69 |
0.6 | 2 | 8 | 16 | 25 | 33 | 41 | 49 | 58 | 66 | 74 | 82 |
0.7 | 2 | 10 | 19 | 29 | 38 | 48 | 58 | 67 | 77 | 86 | 96 |
0.8 | 2 | 11 | 22 | 33 | 44 | 55 | 66 | 77 | 88 | 99 | 110 |
0.9 | 2 | 12 | 25 | 37 | 49 | 62 | 74 | 86 | 99 | 111 | 123 |
1 | 3 | 14 | 27 | 41 | 55 | 69 | 82 | 96 | 110 | 123 | 137 |
1.25 | 3 | 17 | 34 | 51 | 69 | 86 | 103 | 120 | 137 | 154 | 171 |
1.5 | 4 | 21 | 41 | 62 | 82 | 103 | 123 | 144 | 164 | 185 | 206 |
1.75 | 5 | 24 | 48 | 72 | 96 | 120 | 144 | 168 | 192 | 216 | 240 |
2 | 5 | 27 | 55 | 82 | 110 | 137 | 164 | 192 | 219 | 247 | 274 |
2.5 | 7 | 34 | 69 | 103 | 137 | 171 | 206 | 240 | 274 | 308 | 343 |
3 | 8 | 41 | 82 | 123 | 164 | 206 | 247 | 288 | 329 | 370 | 411 |
Adapted from Determining the Amount of Nitrogen in Irrigation Water from East San Joaquin Water Quality Coalition. These materials are not maintained by UC ANR and may not meet current accessibility standards. If you need assistance accessing this content or require an accessible format, please contact East San Joaquin Water Quality Coalition (esjcoalition.org).
References
1. Harter, T., J. R. Lund, J. Darby, G. E. Fogg, R. Howitt, K. K. Jessoe, G. S. Pettygrove, J. F. Quinn, J. H. Viers, D. B. Boyle, H. E. Canada, N. DeLaMora, K. N. Dzurella, A. Fryjoff-Hung, A. D. Hollander, K. L. Honeycutt, M. W. Jenkins, V. B. Jensen, A. M. King, G. Kourakos, D. Liptzin, E. M. Lopez, M. M. Mayzelle, A. McNally, J. Medellin-Azuara, and T. S. Rosenstock. (2012). Addressing Nitrate in California's Drinking Water with a Focus on Tulare Lake Basin and Salinas Valley Groundwater. Report for the State Water Resources Control Board Report to the Legislature. Center for Watershed Sciences, University of California, Davis. 78 p.