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Grassland Fertilization: Exotic Grass Planting Case Studies - McPherson and Jerauld Counties

Updated June 02, 2021
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Pete Bauman

SDSU Extension Natural Resources and Wildlife Field Specialist

A grassland plot with a variety of exotic grass plantings growing throughout.
Figure 1. An example of a low-diversity, exotic grass planting of intermediate wheatgrass, smooth bromegrass and alfalfa that is managed primarily for hay production. Courtesy: P. Bauman

Written collaboratively by Pete Bauman, Karla Hernandez and Sandy Smart.

Part five of this series discussed the effects of fertilization on native grassland plantings. This last installment addresses the options for fertilization on low-diversity exotic grassland plantings.

Low-Diversity Exotic Grassland Plantings

Low diversity non-native hayfields and pastures.

There exists a fair number of fields across South Dakota that were intentionally planted to low-diversity, non-native grasses and forbs. A common example of such fields are historic alfalfa or alfalfa/grass mix hayfields that have reverted to a grassy state. These areas are now more or less dominated by species, such as smooth brome, intermediate wheatgrass or crested wheatgrass, with remnant populations of alfalfas, clovers or other legumes. A second fairly common example of low-diversity non-native fields are expired Conservation Reserve Program (CRP) fields. These were originally established with some combination of smooth brome, intermediate wheatgrass, alfalfa, sweet clover and possibly include some native warm-season grass species.

Nitrogen applications to low-diversity, non-native hayfields and pastures.

In all scenarios discussed in this series on nitrogen (N), the most-practical grassland community in which to consider N application would likely be low-diversity, non-native grasslands managed as hayfields. These are comprised of species able to utilize N and where nutrients are removed from the system when hay is harvested (Figure 1).

Case Study Five: Leola Area, McPherson County

2004 fertilizer nitrogen and phosphorus influence on pasture yield in McPherson County, South Dakota.

Study two was conducted by South Dakota State University (SDSU) researchers in 2004 on two pasture sites near Leola in McPherson County. While this study included two sites, in neither case did the study indicate whether the pastures were truly native sod. Site 1 was dominated by Kentucky bluegrass with some native and introduced broadleaf plants (please refer to Case Study One in this series). Site 2 was dominated by introduced species, including intermediate wheatgrass, smooth bromegrass and alfalfa, making its classification as native pasture highly suspect. Therefore, Site 2 is included in this section of planted, non-native pastures.

At Site 2, researchers applied urea (46-0-0) and triple super phosphate (0-46-0) to the pasture. Phosphorus (P) rates were 0 and 40 pounds/acre, and at this application rate, dry matter production (5,887 pounds/acre) did not increase over the control, which yielded 5,609 pounds/acre with no added P. The actual increase only being 278 pounds/acre.

Application rates for N at Site 2 were 0, 30, 60, 90 and 120 pounds/acre. Production was 5,167 pounds/acre without N application. Yield rose consistently with N application to a maximum of 6,994 pounds/acre produced at 120 pounds/acre of N; this was a total increase of 1,827 pounds/acre over the non-treatment base yield of 5,167 pounds/acre. Yield however, only increased significantly from 0 to 30 pounds N/acre to 6,007 pounds/acre (840 pounds/acre over the base yield of 5,167 pounds/acre).

Interpretation

As described in Case Study Two of this series, it is important to understand that, while overall production may increase, not all of that production results in actual forage consumed by the animal. Here in Case Study Five, even at the highest N application rate (120 pounds/acre) only an additional 1,827 pounds/acre of forage was produced. At a 30% grazing harvest efficiency, livestock would consume only an additional 548 pounds/acre of forage. At today’s market prices, the investment of $0.49/pound of N would cost approximately $59/acre in fertilizer expenses, only to achieve an additional 548 pounds/acre of forage, with an approximate cost of $215/ton.

In a hay-making situation at 80% harvest efficiency, however, one might be able to bale up to 1,461 pounds/acre of the additional 1,827 pounds/acre produced at the maximum 120 pounds N/acre rate. This would reduce investment in fertilizer for the extra forage to approximately $80/ton, which may still pose a significant financial risk in the hay market. In this case, where high N-affinity non-native species are the target, boosting production through artificial N application poses little ecological risk. One exception is the inherent risk that N fertilization may not be successful under adverse environmental conditions, such as drought.

Reference: Gerwing et al. 2004

Case Study Six: Alpena Area, Jerauld County

2013 nitrogen effects on production of CRP fields planted to non-native intermediate wheatgrass, smooth brome and alfalfa.

In this study the landowner had historic CRP fields that were planted primarily to non-native, intermediate wheatgrass with smooth bromegrass and alfalfa common throughout the fields. The landowner managed the grass fields nearly exclusively for hay production and wildlife habitat and was interested in the effects of N fertilization on production.

On May 13, 2013, N (46-0-0) fertilizer treatments were applied to several portions of planted hayfields at a rate of 100 pounds/acre of bulk N product, or 46 pounds N/acre at a cost of $34.47/acre. In addition, paired portions of the fields were left unfertilized, as were all portions of the native pastures at the site.

SDSU Extension field staff were invited to conduct yield and soil assessments at the site. Samples were collected on August 5 and 8, 2013 at near-peak production of the native grasses. Clippings were collected utilizing standardized methods with a 0.96 ft2 clipping ring. Samples were dried in a drying oven at SDSU and weighed on a digital gram scale. Average production of the N-fertilized plots (n=3) was 7,950 pounds/acre, which did not differ from the unfertilized plots (n=8; 6,263 pounds/acre; p=0.28). The average numerical yield difference between fertilized and unfertilized was 1,687 pounds/acre. Fertilized and unfertilized plots were in all cases dominated by intermediate wheatgrass and smooth brome. as would be expected in this low-diversity planted system.

Three soil core sub-samples were collected utilizing a 12-inch soil probe, along with the vegetation samples from each of the sample areas listed above. Soil samples were analyzed for N and carbon content at the SDSU soil lab. Soil carbon averaged 42.1% in fertilized plots and was not different than the 42.2% soil carbon recorded in unfertilized plots (p=0.83). However, soil N was 0.64% in fertilized plots, which differed from the 0.84% soil N recorded in unfertilized plots (p=0.02).

In addition to fertilized and unfertilized hayfield samples, SDSU Extension staff also analyzed the base production in five areas of the unfertilized native pastures. Cattle were excluded from the sample sites with grazing exclosures. The native pastures on this farm were heavily infested with non-native, cool-season grass species, and the plant community was dominated by smooth brome and Kentucky bluegrass with intermediate wheatgrass and crested wheatgrass also common. Native cool-or-warm-season grasses were largely non-existent, except for a limited occurrence of buffalo grass and sedges in some locales. Unfertilized production from these pastures averaged 3,580 pounds/acre (n=5) and was less than unfertilized portions of the non-native hayfields, which averaged 6,263 pounds/acre (n=8) (p=0.04). This is largely due to the heavy dominance of intermediate wheatgrass in unfertilized hayfield samples, which was extremely tall and robust when compared to the smooth brome/Kentucky bluegrass mix prevalent in grazed pastures.

Soil carbon and soil N were also compared between unfertilized pasture and unfertilized planted hayfields. Soil carbon averaged 42.2% in unfertilized hayfield plots and was not different from the 41.8% soil carbon recorded in unfertilized pasture plots (p=0.37). However, soil N content was 1.22% in unfertilized pasture plots, which was higher than the 0.84% soil N recorded in the unfertilized hayfield plots (p=0.003).

Interpretation

While not statistically different, N-fertilized plots outperformed unfertilized plots on average by about 1,687 pounds/acre at a cost of about $34.47/acre, or about $40.87/ton of additional biomass produced. At an average of roughly $100–$120/ton value for CRP grass (August 2013), the profit margin on fertilization of this grass hay may have been approximately $60–$80/ton, or $84–$101/acre (Source: Dakota Hay Auction). Hay harvest costs need also be factored into the profitability equation for a true estimation of profit potential.

These fields were managed exclusively for hay production and habitat, with hay harvest rotated through the fields on a biennial basis. It is unlikely then that litter accumulation due to higher biomass production as a result of N fertilization would constitute a major concern for this simple plant community. In this case, where non-native species with high N-affinity are the target, boosting production through artificial N application poses little ecological risk. An exception would be the inherent risk that the production benefits of N fertilization might not be realized under adverse environmental conditions, such as drought. The 2013 growing season was very favorable for intermediate wheatgrass and smooth brome growth, and likely both species maximized the availability of additional N.

Table 1. 2013 Fertilizer Trials - Alpena, South Dakota

Native/
Planted CRP
Fertilized/
Unfertilized
Average of
Total Soil N (%)
Average of
Total Soil C (%)
Yield Avg. Lbs./Acre
Yield Total
Avg. Lbs./Acre
by Treatment
Primary Plant
Community Composition
N
UF
0.98
42.06
4150
3,580
Low-diversity, native pasture with heavy infestation of introduced grasses (smooth brome, Kentucky bluegrass, intermediate wheatgrass and a few native grasses).
N
UF
1.13
40.08
2450
N
UF
1.59
42.56
3550
N
UF
1.08
42.35
3050
N
UF
1.33
42.06
4700
CRP
UF
0.95
41.75
3050
6,263
Historic CRP fields dominated by non-native intermediate wheatgrass, smooth brome and alfalfa.
CRP
UF
0.67
42.31
6400
CRP
UF
0.77
41.71
9400
CRP
UF
0.79
43.19
8950
CRP
UF
0.97
42.21
8100
CRP
UF
0.84
42.61
6250
CRP
UF
0.76
42
4050
CRP
UF
1
41.87
3900
CRP
F
0.69
41.31
7200
7,950
Historic CRP fields dominated by non-native intermediate wheatgrass, smooth brome and alfalfa.
CRP
F
0.66
43.41
7850
CRP
F
0.58
41.59
8800

Reference: Bauman and Hernandez

Resources and References:

  • Nutrient Network: Includes links to several articles on the topic.
  • Alpert, P., E. Bone, and C. Holzapfel. 2000. Invasiveness, invisibility and the role of environmental stress in the spread of non-native plants. Perspectives in plant ecology, evolution, and systematics. 3:52-66.
  • Borer, E.T., E.W. Seabloom, D.S. Gruner, W.S. Harpole, H. Hillebrand4, E.M. Lind1, P.B. Adler, J. Alberti, T.M. Anderson, J.D. Bakker, L. Biederman, D. Blumenthal, C.S. Brown, L.A. Brudvig, Y.M. Buckley, M. Cadotte, C. Chu, E.E. Cleland. M.J. Crawley, P. Daleo, E.I. Damschen, K.F. Davies, N.M. DeCrappeo, G. Du, J. Firn, Y. Hautier, R.W. Heckman, A. Hector, J. HilleRisLambers, O. Iribarne, J.A. Klein, J.M. H. Knops., K.J. La Pierre, A.D.B. Leakey, W. Li, A.S. MacDougall, R.L. McCulley, B.A. Melbourne, C.E. Mitchell, J.L. Moore, B. Mortensen, L.R. O’Halloran, J.L. Orrock, J. Pascual, S.M. Prober, D.A. Pyke, A.C. Risch, M. Schuetz, M.D. Smith, C.J. Stevens, L.L. Sullivan, R.J.Williams, P.D. Wragg, J.P. Wright, and L.H. Yang. 2014. Herbivores and nutrients control grassland plant diversity via light limitation. Nature. 00:1-4.
  • Dickson, T.L. and B.L. Foster. 2011. Fertilization decreases plant biodiversity even when light is not limiting. Ecology Letters. 14:380-388.
  • Foster, B.L., and K.L. Gross. 1998. Species richness in a successional grassland: effects of nitrogen enrichment and plant litter. Ecology. 79:2593-2602.
  • Gerwing, J., A. Bly, L. Butler, D. Curtis, and G. Erickson. 2004. Fertilizer N and P influence on pasture yield in McPherson County SD in 2004 (projects 35004 and 35104). Soil/water research. South Dakota State University. 2004 progress report. Agriculture Experiment Station. Plant Science Department. Soil PR 04-7:1-3.
  • Harpole, W.S., and D. Tilman. 2007. Grassland species loss resulting from reduced niche dimension. Nature. 446:791-793.
  • Hautier, Y., P.A. Niklaus, and A. Hector. Competition for light causes plant biodiversity loss after eutrophication. 2009. Science. 324:636-638.
  • Hautier, Y., E.W. Seabloom, E.T. Borer, P.B. Adler, W.S. Harpole, H. Hillebrand, E.M. Lind, A.S. MacDougall, C.J. Stevens, J.D. Bakker, Y.M. Buckley, C. Chu, S.L. Collins, P. Daleo, E.I. Damschen, K.F. Davies, P.A. Fay, J. Firn, D.S. Gruner, V.L. Jin, J.A. Klein, J.M.N. Knops, K.J. La Pierre, W. Li, R.L. McCulley, B.A. Melbourne, J.L. Moore, L.R. O’Halloran, S.M. Prober, A.C. Risch, M. Sankaran, M. Schuetz, and A. Hector. 2014. Eutrophication weakens stabilizing effects of diversity in natural grasslands. Nature. 508:521-525.
  • Hector, A., Y. Hautier, P. Saner, L. Wacker, R. Bagchi, J. Joshi, M. Scherer-Lorenzen, E. M. Spehn, E. Bazeley-White, M. Weilenmann, M. C. Caldeira, P. G. Dimitrakopoulos, J. A. Finn, K. Huss-Danell, A. Jumpponen, C. P. H. Mulder, C. Palmborg, J. S. Pereira, A. S. D. Siamantziouras, A. C. Terry, A. Y. Troumbis, B. Schmid, and M. Loreau. 2010. General stabilizing effects of plant diversity on grassland productivity through population asynchrony and overyielding. Ecology. 91:2213-2220.
  • Lamb, E.G. 2008. Direct and indirect control of grassland community structure by litter, resources, and biomass. Ecology. 89:216-225.
  • Seabloom, E. W., C.D. Benfield, E.T. Borer, A.G. Stanley, T.N. Kaye, P.W. Dunwiddie. 2011. Provenance, life span, and phylogeny do not affect grass species' responses to nitrogen and phosphorus. Ecological Applications. 21:2129-2142.
  • Silvertown, J.P, P. Poulton, E. Johnston, G. Edwards, M. Heard, and P.M. Bliss. 2006. The Park Grass Experiment 1856-2006: Its contribution to ecology. Journal of Ecology. 94:801-814.
  • Stevens, C.J., N.B. Dise, J.O. Mountford, and D.J. Gowing. 2004. Impact of nitrogen deposition on the species richness of grasslands. Science. 303:1876-1879.