FERTILIZATION OF ESTABLISHED
BAHIAGRASS PASTURE IN FLORIDA
Sid Sumner, Wayne Wade, Jim Selph, Jerry Southwell, Vicky Hoge,
Pat Hogue, Ed Jennings, Pat Miller, and Travis Seawright*
INTRODUCTION
There are about 2.5 million acres of bahiagrass pasture used for beef production in Florida. A major expense of maintaining this resource is its annual fertilization. Recognizing this expense, and the importance of good fertilization practices, the Florida Cattleman's Association recommended in 1985 that the University of Florida, IFAS, reevaluate the fertilization needs of pasture grasses.
A three-year research study conducted at the Ona Agricultural Research and Education Center
in the early 1960s (McCaleb et al., 1966) showed that bahiagrass yield was not increased by
phosphate (P2O5) fertilization, and a response to potash (K2O) fertilization was not obtained at
rates higher than 24 pounds per acre (lb/A) annually, even with 120 lbs nitrogen (N)/A applied as
a split application. Based on soil test values reported in the study, IFAS fertilizer
recommendations called for annual applications of 48 lb of P2O5 and 96 lb of K2O/A (Jones et
al., 1974). Later modifications of IFAS recommendations indicated that 40 lb P2O5 and 80 lb
K2O/A should have been applied annually (Whitty et al., 1977).
Research at the Beef Research Unit near Gainesville (Blue, 1970) showed that around 70% of
the P applied to a limed Leon fine sand pasture over an 18-year period had remained in the
surface soil. Further study (Rodulfo and Blue, 1970) showed that bahiagrass responded to added
P2O5 when grown in the surface horizon of a virgin soil, but did not respond to P2O5 when
grown in the surface horizon of soil from previously-fertilized pasture.
Considering evidence that the P2O5 and K2O requirements of bahiagrass need to be evaluated
under conditions present on commercial ranches that have been in production for many years, a
field study was conducted with the following objectives: 1) to determine if bahiagrass pasture
responds to P2O5 and K2O fertilization when N fertilization is 60 lb/A/yr, a rate commonly used
by ranchers (IFAS, 1986); and 2) to compare the response of bahiagrass pasture when fertilized
according to IFAS standard recommendations based on soil tests with the response of bahiagrass
fertilized at lower rates of N, P2O5 and K2O.
FIELD STUDY METHODS
In 1986, one site in each of nine south Florida counties was selected. Site locations and descriptions are presented in the appendix. Each site was a bahiagrass pasture on which a cow/calf management system had been in effect for more than 10 years. A site in Pasco County was discontinued after the first year due to severe mole cricket damage of the bahiagrass pasture.
At each site, five 50 x 100 ft areas were selected and assigned one of five fertilization
treatments. These were: 1) no fertilizer; 2) 60 lb N/A applied in March; 3) 60 lb N, 45 lb P2O5
and 45 lb K2O/A applied in March; 4) 60 lb N/A applied in March and 60 lb N/A applied again
in September; and 5) 60 lb N. 90 lb P2O5 and 45 lb K2O/A applied in March and 60 lb N and 45
lb K2O/A applied in September. Nitrogen, phosphate, and potash were applied as ammonium
nitrate, superphosphate, and potassium chloride, respectively. Treatment 5 represented
University of Florida, IFAS standard recommendations (Whitty et al, 1977) for fertilizing
bahiagrass pasture based on test of soil samples from each site when the demonstration was
initiated.
Soil samples were obtained from each treatment area immediately prior to fertilization in
March and September each year of the demonstration. Each soil sample consisted of a composite
of five 6-inch deep cores from each treatment area. Soil samples were analyzed for pH and for
Mehlich-I extractable P, K, calcium (Ca), zinc (Zn), copper (Cu), magnesium (Mg), and
manganese (Mn).
Two 4 x 8 ft wire cattle-exclusion cages were placed on each 50 x 100 ft treatment area in March. Cages were positioned on an area where the bahiagrass had been previously staged to a 2-inch stubble height, if needed, with a plot harvester. Forage from a 20-sq-ft area inside and outside each cage was harvested to a 2-inch stubble every 30 to 60 days from April or May through December. On each harvest date, each cage was moved to a pasture area harvested outside that cage, thus cages were moved around the 50 x 100 ft treatment areas throughout the year.
Total fresh forage harvested inside and outside each cage was weighed and sampled for
analysis. Dry matter content was determined on samples dried in a forced-air dryer at 60°C. Dry
matter yield was calculated from fresh weight data and dry matter content. Crude protein content
and total digestible nutrients (TDN) were determined with a near-infrared analyzer. Forage
samples were ashed at 600 deg C and acid digested to determine P, K, Ca, Mg, Zn, Mn, Cu and
iron (Fe).
The field study was initiated in March 1987 and completed in December 1989.
FORAGE YIELDS AND ADDITIONAL PRODUCTION COST
Two important terms are used in this publication to describe the type of forage harvested
during the study. Regrowth forage is bahiagrass harvested inside an animal exclusion cage which
had grown from a 2-inch stubble since the last harvest. Available forage is bahiagrass harvested
outside the cage and is forage actually available to the grazing animal. Yield data were obtained
from regrowth harvests.
There was a consistent increase in forage yield to 60 lb of N/A applied in March over the no
fertilizer treatment (Table 1, Appendix Table 1A). Over three years the treatment receiving 60 lb
N/A averaged 1,760 lb more dry matter per acre annually than the treatment receiving no
fertilizer. It presently costs about $20/A to apply 60 lb of N. including $4 per acre spreading cost.
This expense appears justifiable, costing about $23 for each ton of additional dry forage
produced (Table 2).
In comparison to 60 lb of N/A only, a positive response in dry matter yield was obtained when
45 lb of P2O5 and 45 lb of K2O/A were applied in March along with 60 lb of N/A (Table 1).
However, the increased production was only 400 lb of dry forage per acre annually. It costs about
$14/A for the P2O5 and K2O and approximately $72 for each additional ton of dry forage
produced.
Applying 60 lb of N/A in March and then again in September produced an average of 480 lb
more dry matter per acre than one 60 lb N application in March (Table 1). It would cost about
$20/A for the second N application, and the cost for each additional ton of dry forage would be
about $84 (Table 2). Several research studies have shown a linear response in dry matter yield of
bahiagrass to increasing rates of N fertilization, even when N was applied as split applications
(Blue, 1966; Blue and Graetz, 1977). However, these studies did not evaluate a situation in
which one half of the N was applied as a second application as late as September, a practice used
on some ranches in Florida because of heavy summer rains.
In comparison to two applications of 60 lb N/A, a positive response was obtained in dry matter
yield with the addition of 90 lb of P2O5 in March, and 90 lb/A of K2O equally split between
March and September, along with 120 lb of N (Table 1). The increased yield averaged 700 lb
more dry forage per acre annually than the 120 lb of N/A alone. It presently costs about $29/A
for the P2O5 and K2O applied, thus costing approximately $82 for each additional ton of dry
forage produced.
EFFECT OF N ON BAHIAGRASS GROWTH DISTRIBUTION
Increased yield due to the application of N in March was immediate, and continued throughout
the summer period (Figure 1). Early spring growth of pasture forage is important because of low
forage availability after the winter months, and demands by cows which are usually nursing
calves and being rebred. Typical low spring rainfall was experienced in all three years of this
field study, and yet substantial responses in forage growth and forage quality to N fertilization
were obtained both in April and in May. This points out the importance of applying N fertilizer
to bahiagrass pasture as early as February or March.
The response to N application in September was also immediate but limited only to the
September or October harvests. Forage growth in general was reduced after October, because of
shorter days, so a response to N fertilization might not be expected. The results of this field study
document the poor response of bahiagrass to N applied in September, and suggest that N should
be applied to bahiagrass as a single application in the spring, but if split, the second application
should be well before September. Research data developed previously at Gainesville (Blue,
1966; Blue and Graetz, 1977) support this conclusion.
EFFECT OF N ON BAHIAGRASS QUALITY
When averaged across all harvests in a season, crude protein content of bahiagrass regrowth
forage increased with increasing rates of N fertilization (Table 1), but increases were relatively
small. Crude protein increases were most pronounced immediately following N application in
March and September and rapidly diminished within 4 to 8 weeks (Figure 2). Short-term
increases in crude protein content of the magnitude observed would be important in spring grass
when cows grazing this forage are usually nursing young calves and being rebred.
Nitrogen fertilization also increased TDN of bahiagrass, but increases, when averaged over the
entire year, were relatively small (Table 1). Increases in TDN were most evident immediately
following N application (Figure 3). Fertilization with P and K had little effect on crude protein
content and TDN of bahiagrass
| Table 1. Effect of fertilization treatment on annual yield and quality of regrowth bahiagrass harvested from April to December from nine commercial ranch sites in south Florida. | |||||
| Item | No
fert. |
N(a)
March |
NPK(b)
March |
N(a) March,
N(a) Sept. |
NPK(c) March,
NK(d) Sept. |
| Annual yield. t/A | |||||
| 1987 | 3.32(i) | 4.06(i) | 4 4.09(j) | 4.36(j) | 4.51(j) |
| 1988 | 3 97 | 5.06(j) | 5.32(j) | 5 11 (jk) | 5.72(k) |
| 1989 | 4.60(i) | 5 47(j) | 5.82(jk) | 5.91 (jk) | 6.30(k) |
| Avg. | 3.73 | 4.58 | 4.78 | 4.82 | 5.18 |
| Crude protein. %(h) | |||||
| 1987(e) | 9.8 | 10.3 | 10.4 | 11.0 | 10.8 |
| 1988' | 8.9 | 9.0 | 9.4 | 10.0 | 10.4 |
| 1989(g) | 10.5 | 10.3 | 10.7 | 11.2 | 11.4 |
| Avg. | 9.8 | 10.0 | 10.2 | 10.8 | 10.9 |
| TDN. %(h) | |||||
| 1987 | 54.0 | 54.2 | 54.6 | 54.7 | 54.6 |
| 1988 | 52.5 | 52.7 | 53.0 | 53.2 | 53.6 |
| 1989 | 53.6 | 54.2 | 53.9 | 54.3 | 54.5 |
| Avg. | 53.4 | 53.8 | 54.0 | 54.2 | 54.3 |
| (a) at 60 Ib/A. | |||||
| (b)N at 60 Ib/A, P2O5 at 45 Ib/A, K2O at 45 Ib/A. | |||||
| (c)n at 60 Ib/A, P2O5 at 90 Ib/A, K2O at 45 Ib/A. | |||||
| (d)n at 60 Ib/A, K2O at 45 Ib/A. | |||||
| (e) Each 1987 value is an average of 144 samples taken from 9 sites over 8 harvests. | |||||
| (f) Each 1988 value is an average of 96 samples taken from 8 sites over 6 harvests. | |||||
| (g)Each 1989 value is an average of 112 samples taken from 8 sites over 7 harvests. | |||||
| (h)values are expressed as a % of the dry matter. | |||||
| (i,j,k)Annual yield means in a line which are followed by a different superscript differ at the.05 probability as determined by Duncan's Multiple | |||||
| Range. Mean square for error was .38, .51, and .48 ton/A in 1987, 1988, and 1989, respectively. | |||||
| Table 2. Benefits and cost of bahiagrass fertilization treatments. | |||
| Fertilization treatment comparisons | Increased yield of dry forage(a) | Increased cost of fertilizer to produce forage(b) | Cost of each additional ton dry forage of produced(c) |
| Ib/acre | Ib/acre | $/acre | $/ton |
| 60 lb N in March
vs. no fertilizer |
1760 | 20 | 23 |
| 60 lb N in March plus
60 lb N in September vs. 60 lb N in March |
|||
| 480 | 20 | 84 | |
| 60 lb N,45 lb P2O5
45 lb K2O in March vs. 60 lb N in March |
|||
| 400 | 14 | 72 | |
| 60 lb N. 90 lb P2O5
45 lb K2O in March plus 60/2/lb N, 45lb K2O in September vs 60 lb N in March plus 60 lb N in September |
|||
| 700 | 29 | 82 | |
| (a)Based on three-year forage yield averages. | |||
| (b)N, P2O5 and K2O are charged at 0.27, 0.17 and 0.15 $ per lb, respectively. Spreading cost was $4/A and charged only to N application since P2O5 and K2O were applied in addition to N. | |||
| (c)Cost per ton of additional forage ($) = increased cost per acre for additional fertilizer ($)/(increased yield of dry forage (Ib)/2000). | |||
QUALITY OF REGROWTH VS AVAILABLE FORAGE
Forage quality values for available forage responded to fertilization in a manner similar to that
for regrowth forage (data not shown). However, available forage was lower in crude protein
content and digestibility than regrowth forage, and from July through the fall this difference
became progressively larger (Figure 4). The crude protein and TDN requirements for a brood
cow nursing a calf and having average milking ability are about 10% and 58% of the dry matter,
respectively (National Research Council, 1984). During the spring, summer, and early fall, cattle
would selectively graze bahiagrass having quality similar to regrowth forage which would come
close to meeting the requirements of lactating brood cows for crude protein and TDN. However,
in late fall and winter when bahiagrass stops growing and forage availability becomes limited,
the quality of forage eaten by cattle would be similar to that shown for available forage harvested
in October and December. This forage would only meet the needs of dry, pregnant cows, which
are about 8% and 54% of the dry matter, respectively (National Research Council, 1984).
FERTILIZATION EFFECT ON MINERALS IN BAHIAGRASS
Fertilization with P2O5 and K2O increased P and K content of bahiagrass regrowth forage, and the degree of increase was related to the amount of P2O5 and K2O applied (Table 3, Appendix Table 2A).
Dietary P levels recommended by the National Research Council (1984) for the types of beef
cattle grazing in Florida range from 0.18% of the dry matter for dry cows to 0.23% of the dry
matter for lactating cows of average milking ability (most Florida brood cows), and to 0.29% of
the dry matter for lactating cows with superior milking ability. Phosphorus levels in regrowth
forage were highest in 1987 (Table 3). Only one site had average P level below that
recommended for most beef cattle and that was in treatments not fertilized with P2O5. Levels of
P in bahiagrass were lowest in 1988, and average P levels of treatments not receiving P2O5 at
two sites were slightly below that required by most lactating cows.
The P content in available forage was lower than the P content in regrowth forage (Figure 5). The P level was particularly low in available forage in the fall and winter. These levels would cause P deficiency in lactating brood cows not supplemented with P. A deficiency in P could have a negative effect in rebreeding
Although a mineral supplement containing P is recommended for all grazing cattle in Florida, mineral supplementation would be more critical if pastures are not fertilized with P2O5. A mineral supplement similar to one commonly recommended for Florida (Cunha et al., 1964) would satisfy the P needs of cattle, and would be more economical than fertilizing bahiagrass to provide P nutrition for cattle.
The National Research Council (1984) recommends a dietary K level for beef cattle of 0.5 to 0.7% of the dry matter. Bahiagrass K levels were below this range at several sites in 1988. Other minerals were present in bahiagrass forage in adequate amounts as recommended by the National Research Council, with the exception of Cu. The National Research Council recommends that cattle diets contain 4 to 10 ppm of Cu. Forage copper levels were at or below the lower end of this range in many cases. Possibilities of a Cu deficiency for cattle grazing Florida pastures has long been recognized, so the addition of this element to the mineral supplement is recommended routinely (Cunha et al., 1964).
SOIL ANALYSES FROM DEMONSTRATION SITE
Soil P values were very low (< 10 ppm) to low (10 to 15 ppm) at seven sites and medium (16 to 30 ppm) at only one site (Table 4). Soil K values were very low (< 20 ppm) to low (20 to 35 ppm) at five sites, medium (36 to 60 ppm) at two sites and high (61 to 125 ppm) at only one site. All soil parameters were variable among sites and with there being no obvious relationships between any parameter and bahiagrass yield. Fertilization treatment also had no effect on any soil parameters. These data indicate that soil testing as now commonly used to manage the fertilization of Florida bahiagrass pastures is of limited value. This could be because soil test data and plant response relationships were developed with annual crops and bahiagrass is a deep-rooted perennial plant.
FERTILIZER RECOMMENDATIONS FOR ESTABLISHED BAHIAGRASS
From data developed in this field study in conjunction with other data from the literature, the following recommendations are presented for fertilizing established bahiagrass pasture in Florida. These recommendations support revised University of Florida, IFAS recommendations (Kidder et al., 1990).
1. With the annual application of 60 lb or less N/A of bahiagrass pasture, do not apply any P2O5 and K2O for at least 3 years. The field study is continuing (1990) and future recommendations of 60 lb/A of N only may be extended to periods longer than 3 years.
2. For the most efficient use of the fertilizer budget, only after 60 lb of N have been applied to every bahiagrass acre to be used for grazing should consideration be given to applying P2O5 and K2O. At N rates of 100 to 120 lb/A, apply 25 lb/A of P2O5 and 50 lb/A of K2O if these plant nutrients test low for the soil. Do not apply P2O5 and K2O if these nutrients test medium or higher for the soil.
3. When applying up to 120 lb of N/A, it appears to be most efficient to apply all of the N as a single application in the spring. If a split application is used, the second should be applied before the first of July.
4. Apply N fertilizer to bahiagrass pasture in February or March. Bahiagrass produces growth in the early spring, so a response in both forage growth and forage quality to N fertilizer will be obtained. Bahiagrass should continue to benefit into the growing season from an early N application.
5. A mineral supplement containing P and trace elements should be available to all cattle grazing bahiagrass pastures, especially those grazing pastures not fertilized with P2O5.
| Table 3. Average phosphorus and potassium levels in regrowht bahiagrass receiving different fertilizer treatments at nine commercial ranch sites from April through December of 1987, 1988, and 1989. | ||||||
| Item | No
Fert. |
N(a)
March |
NPK(b)
March |
N(a)
March, N(a) Sept. |
NPK(c)
March, NK(d) Sept. | |
| Phosporus, %(h) | ||||||
| 1987(e) | 0.30 | 0.31 | 0.34 | 0.29 | 0.36 | |
| 1988 | 0.22 | 0.21 | 0.27 | 0.21 | 0.28 | |
| 1989 | 0.27 | 0.25 | 0.31 | 0.24 | 0.35 | |
| Avg. | 0.27 | 0.26 | 0.31 | 0.25 | 0.33 | |
| Potassium,%(h) | ||||||
| 1987 | 0.70 | 0.79 | 0.86 | 0.77 | 0.93 | |
| 1988 | 0.41 | 0.40 | 0.45 | 0.36 | 0.50 | |
| 1989 | 0.88 | 0.97 | 1.04 | 0.84 | 1.19 | |
| Avg. | 0.68 | 0.74 | 0.81 | 0.69 | 0.90 | |
| (a)(b)(c)(d)(e)(f)(g)(h) See respective footnotes on table 1 | ||||||
| Table 4. Soil analysis for eight south Florida commercial ranch sites across all fertilization treatments and for fertilization treatments across all sites.(e) | ||||||||
| Item | pH | P | K | Mg | Ca | Zn | Cu | Mn |
| -------------------ppm Mehlich-l extractable----------------------- | ||||||||
| County Location | ||||||||
| Desoto | 6.3 | 11 | 14 | 77 | 372 | 1.2 | 0.3 | 1.0 |
| Hardee | 6.1 | 10 | 19 | 51 | 802 | 1.2 | 0.8 | 1.8 |
| Highlands | 5,5 | 9 | 70 | 90 | 824 | 1.6 | 0.4 | 1.1 |
| Hillsborough | 4.7 | 11 | 29 | 44 | 428 | 2.4 | 0.2 | 1.0 |
| Manatee | 4.9 | 7 | 36 | 59 | 446 | 2.2 | 0.2 | 1.7 |
| Okeechobe | 6.1 | 25 | 40 | 48 | 617 | 4.2 | 1.1 | 3.6 |
| Polk | 6.2 | 3 | 22 | 88 | 678 | 0.8 | 0.2 | 0.7 |
| Sarasota | 5.0 | 6 | 21 | 43 | 474 | 1.5 | 0.4 | 0.4 |
| Fertilization treatment | ||||||||
| No fertilizer | 5.6 | 12 | 35 | 62 | 570 | 1.8 | 0.4 | 1.5 |
| N March(a) | 5.6 | 10 | 28 | 62 | 582 | 1.8 | 0.5 | 1.5 |
| NPK March(b) | 5.6 | 10 | 29 | 62 | 587 | 1.9 | 0.5 | 1.3 |
| N March, N Sept(c) | 5.6 | 10 | 29 | 62 | 597 | 2.0 | 0.4 | 1.5 |
| NPK March, NK Sept (d) | 5.6 | 9 | 38 | 62 | 576 | 1.9 | 0.4 | 1.4 |
| (a,b,c,d)See respective footnotes on table 1. | ||||||||
| (e) Data obtained from composite of five 6-inch cores from each treatment on each site for three spring and three fall samplings. County values are the average of 30 samples and treatment values are the average of 120 samples. | ||||||||
REFERENCES CITED
Blue, W. G. 1966. "The effect of nitrogen sources, rates, and application frequencies on
Pensacola Blue, W. G. 1970. "The effect of lime on retention of fertilizer phosphorus in Leon fine sand."
Soil Blue, W. G., and D. A. Graetz. 1977. "The effect of split applications on nitrogen uptake by
Cunha, T. J., R. L. Shirley, H. L. Chapman, Jr., C. B. Ammerman, G. K. Davis, W G. Kirk, and
Jones, D. W., C. E. Freeman, J. T. Johnson, and E. B. Whitty. 1974. "Fertilizer recommendations
IFAS. 1986. Survey of beef-forage practices, south-central Florida - 1986 summary. Pub. Kidder, G., E. A. Hanlon, and C. G. Chambliss. 1990. "IFAS standardized fertilization
McCaleb, J. E., C. L. Dantzman, and E. M. Hodges. 1966. "Response of pangolagrass and
National Research Council. 1984. Nutrient requirements of beef cattle. 6th ed. National
Rodulfo, S., and W. G. Blue. 1970. "The availability to forage plants of accumulated phosphorus
Whitty, E. B., D. W. Jones, G. Kidder, C. G. Chambliss, D. L. Wright, and J. J. Street. 1977.
APPENDIX
SITE DESCRIPTIONS AND LOCATION
Desoto County - Carlton 2 x 4 Ranch
Site is located approximately 7 miles south of Arcadia on State Road 31. It is mapped as
Malibar fine sand on flat high ground. The pasture was limed and fertilized prior to the study as
follows: 2/ 26/82 -1 ton/acre dolomite; 3/9/82 - 60 lb N. 30 lb P2O5 and 55 lb K2O/acre;
11/22/82 - 40 lb N. 10 lb P2O5 and 20 lb K2O/acre. The pasture received no fertilizer after
11/82. Stocking rate was approximately 2.6 acres per cow.
Hardee County - J. P. Platt Ranch
Site is located approximately 6 miles east of Zolfo Springs on State Road 66 at the Grass
Valley Ranch. The site is relatively flat and located on a poorly drained Pomona fine sand soil.
Annual fertilization practices since 1980 have been 70 lb N, 18 lb P2O5 and 35 lb K2O/acre in
the spring with 65 lb N applied in the fall. The pasture received 1 ton/acre of dolomite in 1982.
Stocking rate was approximately 2 acres per cow.
Highlands County - Oscar Clemons Ranch
Site is located approximately 5 miles north of State Road 70 on county road 721. Soil is
mapped as an Immokalee sand. The site is flat and poorly drained. The pasture was fertilized
with 1 ton/acre of lime every 3 years and 300 lbs/acre of 16-8-8 every other year prior to the
study. Stocking rate was approximately 1 acre per cow.
Hillsborough County - Warren Allen Ranch
Site is located east of Brandon near Lithia off county road 640. The study is located on a flat
poorly drained Ona fine sand. Fertilization practices were: 4/85 - 65 lb N/acre; 6/85 - 60 lb N, 30
lb P2O5 and K2O/acre; 3/86 - 60 lb N. 30 lb P2O5 and K2O/acre; 7/86 - 65 lb N. 30 lb P2O5
and 45 lb K2O/ acre. All fertilizer treatments included a complete micronutrient mix except in
4/85. Stocking rate was approximately 2.5 acres per cow.
Manatee County - Russell Reagan Ranch
Site is located near Bradenton, approximately 8 miles east of Interstate 75 off of State Road 64
on Rye Road. It is located on high ground and not subject to standing water. Soil type is mapped
as an Eau Gallie fine sand. The pasture was established over 20 years ago and had not received
fertilizer since 1981 and perhaps earlier. Stocking rate was approximately 1.5 acres per cow.
Okeechobee County - Dirr Farms
Site is located east of Kissimmee River and west of Okeechobee on State Road 70. The plots are
located on a poorly drained flatwoods Immokalee fine sand. The pasture was renovated in 1976
and was fertilized annually from 1974-1984 with 30 lb N and 25 lb P2O5 and K2O respectively,
plus micronutrients. Fertilizer had not been applied since 1984. The 150 acre pasture was stocked
with approximately 80 dry cows and 4 bulls.
Pasco County - Joe Barthle Ranch
Site is located west of Dade City on the west side of county road 581, 1.3 miles north of
county road 578 and 1.2 miles south of Johnston road. The plots are located on a well-drained
Kendrick fine sand. The site was fertilized in 1984 with poultry layer waste at the rate of 2
tons/acre. Stocking rate was approximately 4 acres per cow.
Polk County - Jerry Keen Ranch
Site is located approximately 11.5 miles west of Lake Wales on State Road 60. The site is a
poorly drained flatwoods Myakka fine sand. The pasture is over 20 years old, was rotovated in
the fall of 1985 and overseeded with cool-season annual grasses. Fertility practices have been as
follows: 1980 - 1 ton dolomite/acre; 1982 - 50 lb N/acre; 1983 - 40 lb N. 10 lb P2O5 and 20 lb
K2O/acre; 1984 - 90 lb N. 25 lb P2O5 and K2O/acre, plus micronutrients; 1985 - 120 lb N. 20 lb
P2O5 and 35 lb K2O/acre, plus 1 ton dolomite/acre; and 1986 - 65 lb N/acre. Stocking rate was
approximately 2 acres per cow.
Sarasota County - Mabry Carlton Ranch
Site is located 21 miles east of Interstate 75 on State road 72. It is west of Gill Road and
approximately 3 miles west of the Desoto Co./Sarasota Co. line. The site is on a relatively flat
Myakka fine sand. The pasture had not been fertilized for 10 years prior to 1987. Stocking rate
was approximately 5 acres per cow.
Fert.
Table 1A. Annual yield and average crude protein and TDN content of regrowth bahiagrass receiving different fertilizer
treatments at nine commercial ranch sites in south Florida from April to December (3-year average).
County
of siteItem
No
N(a)
MarchNPK(b)
MarchN(a) March
N(a) Sept.NPK(c) March
NK(d) Sept.
Desoto
Yield, t/A
2.70
3.76
4.25
4.40
4.33
CP, %(e)
8.0
8.6
8.9
9.3
9.4
TDN, %(e)
52.4
52.7
53.2
53.7
53.9
Hardee
Yield, t/A
4.33
5.19
5.25
5.40
5.83
CP, %
10.0
10.6
10.6
11.1
11.1
TDN, %
54.1
55.0
54.9
53.1
55.1
Highlands
Yield, t/A
3.85
5.89
5.43
5.76
6.24
CP, %
10.8
11.1
10.9
11.6
12.0
TDN, %
54.7
55.2
54.9
55.4
55.5
Hillsborough
Yield, t/A
3.13
4.28
4.26
4.61
4.99
CP, %
9.2
9.8
9.9
10.8
11.1
TDN, %
53.0
53 7
53 7
53 9
54 3
Manatee
Yield, t/A
4.87
5.37
6.26
5.54
5.91
CP, %
11.2
10.9
11.3
11.6
11.8
TDN, %
53.7
52.3
53.8
53.8
54.0
Okeechobee
Yield t/A
6.19
6.25
7.36
7.36
7.60
CP, %
10.3
10.7
10.9
11.9
11.8
TDN, %
53.6
53.8
53.7
54.1
54.3
Pasco(f)
Yield, t/A
1.58
2.09
1.71
2.44
2.85
CP, %
10.0
10.4
9.8
11.0
10.9
TDN, %
53.9
53.9
54.1
54.3
53.7
Polk
Yield, t/A
2.72
3.81
3.45
3.25
4.33
CP, %
9.4
9.4
9.8
10.4
10.4
TDN, %
53.0
53.4
52.8
53.7
53.7
Sarasota
Yield, t/A
2.90
3.07
3.15
3.28
3.19
CP, %
9.6
8.9
10.0
10.0
10.0
TDN, %
53.1
53.1
53.6
54.0
53.9
(a)N at 60 Ib/A.
(b)N at 60 Ib/A, P2O5 at 45 Ib/A, K2O at 45 Ib/A.
(c)N at 60 Ib/A, P2O5 at 90 Ib/A, K2O at 45 Ib/A.
(d)n at 60 Ib/A, K2O at 45 Ib/A.
(e)values are averages of 42 samples, and presented as % of dry matter.
(f)Average of one year.
Table 2A. Average mineral content of regrowth bahiagrass receiving different fertilizer treatments at nine commercial ranch sites in south
Florida from April through December (3-year average).
County
of siteMineral(a)
No
Fert.N(b)
MarchNPK(c)
MarchN(b) March
N(b) Sept.NPK(d) March
NK(e) Sept.
Desoto
P, %
0.24
0.22
0.29
0.25
0.28
K, %
0.41
0.47
0.65
0.53
0.70
Ca, %
0.49
0.54
0.48
0.47
0.46
Mg, %
0.44
0.43
0.42
0.50
0.40
Zn, ppm
59
58
50
47
44
Cu, ppm
5
10
5
6
7
Mn, ppm
60
40
49
29
38
Fe, ppm
86
93
89
88
84
Hardee
P, %
0.34
0.30
0.34
0.28
0.39
K, %
0.65
0.77
0.83
0.62
0.92
Ca, %
0.49
0.46
0.45
0.50
0.44
Mg, %
0.31
0.36
0.27
0.34
0.27
Zn, ppm
39
41
36
39
39
Cu, ppm
7
6
5
6
5
Mn, ppm
52
55
54
61
66
Fe, ppm
71
75
69
72
72
Highlands
P, %
0.25
0.33
0.32
0.30
0.40
K, %
0.67
0.94
0.82
0.86
1.01
Ca, %
0.45
0.39
0.38
0.38
0.39
Mg, %
0.24
0.24
0.23
0.24
0.22
Zn, ppm
31
35
31
37
35
Cu, ppm
4
6
4
5
5
Mn, ppm
25
52
41
51
71
Fe, ppm
74
61
59
59
57
Hillsborough
P, %
0.32
0.31
0.37
0.30
0.38
K, %
0.79
0.86
0.87
0.68
0.99
Ca, %
0.35
0.35
0.40
0.35
0.32
Mg, %
0.36
0.34
0.37
0.49
0.34
Zn, ppm
75
79
63
68
64
Cu, ppm
4
5
5
5
5
Mn, ppm
93
87
90
90
88
Fe, ppm
84
79
73
77
73
Manatee
P, %
0.29
0.25
0.32
0.26
0.33
K, %
0.91
0.85
0.95
0.84
0.99
Ca, %
0.35
0 35
0.33
0.39
0.33
Mg, %
0.28
0.28
0.28
0.36
0.28
Zn, ppm
45
52
52
53
47
Cu, ppm
5
10
5
5
6
Mn, ppm
104
88
102
93
96
Fe, ppm
74
88
71
81
86
Okeechobee
P, %
0.32
0.31
0.35
0.31
0.34
K, %
0.93
0.88
1.07
0.99
1.14
Ca, %
0.40
0.45
0.40
0.45
0.40
Mg, %
0.23
0.26
0.23
0.27
0.23
Zn, ppm
50
64
52
53
53
Cu, ppm
5
6
5
6
6
Mn, ppm
61
70
58
67
78
Fe, ppm
66
70
64
67
72
Pasco
P, %
0.27
0.28
0.29
0.27
0.30
K, %
0.70
0.78
0.88
0.74
0.90
Ca,%
0.57
0.52
0.45
0.46
0.42
Mg, %
0.28
0.28
0.30
0.30
0.25
Zn, ppm
66
49
54
60
51
Cu, ppm
6
6
6
6
6
Mn, ppm
72
68
78
79
87
Fe, ppm
169
158
139
132
114
Polk
P, %
0.17
0.18
0.24
0.16
0.27
K, %
0.60
0.68
0.67
0.50
0.78
Ca, %
0.42
0.40
0.42
0.42
0.35
Mg, %
0.35
0.35
0.37
0.45
0.41
Zn, ppm
40
40
38
39
40
Cu, ppm
4
5
4
5
5
Mn, ppm
21
22
23
23
28
Fe, ppm
72
84
71
79
76
Sarasota
P, %
0.21
0.19
0.28
0.20
0.28
K, %
0.48
0.43
0.56
0.43
0.63
Ca, %
0.44
0.38
0.41
0.40
0.38
Mg, %
0.37
0.38
0.36
0.44
0.32
Zn, ppm
66
55
54
57
53
Cu, ppm
6
5
6
6
5
Mn, ppm
69
57
63
65
59
Fe, ppm
74
63
59
62
60
(a) Values presented on dry matter basis; average of 42 samples taken over 3 years.
(b)N at 60 Ib/A.
(c)N at 60 Ib/A, P2O5 at 45 Ib/A, K2O at 45 Ib/A.
(d)n at 60 Ib/A, P2O5 at 90 Ib/A, K2O at 45 Ib/A.
(e)N at 60 Ib/A, K2O at 45 Ib/A.