Arkansas - Agricultural Communication Services - University of ...
Arkansas - Agricultural Communication Services - University of ...
Arkansas - Agricultural Communication Services - University of ...
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<strong>Arkansas</strong> Animal Science Department Report 2001<br />
Forage Preparation and Analysis. All forage samples<br />
were dried to a constant weight under forced air at 122°F. Dry<br />
forage samples were ground through a Wiley mill (Arthur H.<br />
Thomas, Philadelphia, PA) equipped with a 1-mm screen<br />
before analysis. Total plant N was determined by rapid combustion<br />
(850°C); conversion <strong>of</strong> all N-combustion products to<br />
N 2 ; and subsequent measurement by thermoconductivity cell<br />
(LECO Model FP-428; LECO Corp., St. Joseph, MI). Neutral<br />
(NDF) and acid detergent (ADF) fiber analyses were conducted<br />
by the batch procedures outlined by ANKOM<br />
Technology Corp. (Fairport, NY). No sulfite was included in<br />
the neutral detergent solution. The concentrations <strong>of</strong> N in<br />
NDF and ADF residues (NDIN and ADIN, respectively) were<br />
determined as described previously. Cell-soluble N was calculated<br />
as 100 - NDIN, where NDIN was expressed as a percentage<br />
<strong>of</strong> total plant N.<br />
Statistical Analysis. For each individual harvest,<br />
orthogonal contrasts (PROC GLM; SAS Inst., Inc., Cary, NC)<br />
were used to test each N fraction for linear, quadratic, and<br />
cubic responses to N fertilization. For each individual plot,<br />
fertilization rate (0, 50, 100, or 150 lb N/acre) was not necessarily<br />
the same on both application dates; therefore, for the<br />
first and second harvest, contrast statements were constructed<br />
based on the initial (April 28) application <strong>of</strong> ammonium<br />
nitrate. For the third harvest, contrast statements were based<br />
on the second application <strong>of</strong> fertilizer N on July 19. A combined<br />
analysis <strong>of</strong> all data from all three harvests at each site<br />
was conducted by similar methods. This analysis included<br />
seven N fertilization rates (0, 50, 100, 150, 200, 250, and 300<br />
lb N/acre) and a test for quartic effects was included in the model.<br />
Results and Discussion<br />
Nitrogen. At both sites, forages from the initial harvest<br />
on May 30 and the third harvest on August 18 exhibited a<br />
strong positive linear relationship (P < 0.0001) between N<br />
fertilization rate and the concentration <strong>of</strong> N in the forage<br />
(Table 2). This is a commonly observed response to N fertilization.<br />
The increases observed in forages fertilized with 150<br />
lb N/acre compared with those receiving no fertilization<br />
ranged from 0.56 to 1.11 percentage units, which corresponds<br />
to 3.5 to 6.9 percentage units <strong>of</strong> CP. The effects <strong>of</strong> the first<br />
application <strong>of</strong> N fertilizer on forages harvested on the second<br />
date (July 7) were not significant (P > 0.05) at either site,<br />
indicating that the residual effects <strong>of</strong> the first application were<br />
not sufficient to affect concentrations <strong>of</strong> N in forages harvested<br />
on the second date. When all data for the year was<br />
combined, strong positive linear effects (P < 0.0001) were<br />
found at both sites (Table 3). The higher concentrations <strong>of</strong> N<br />
generally observed for forages grown at the Latta site probably<br />
reflects the more recent applications <strong>of</strong> poultry waste during<br />
the preceding year that did not occur at the Stephens site.<br />
Cell-soluble N (NDSN). The percentage <strong>of</strong> total plant N<br />
found in the cell-soluble portion <strong>of</strong> the plant ranged from 55.5<br />
to 75.6% over the study and was affected by N fertilization in<br />
a manner similar to that described for total plant N (Table 4).<br />
Positive linear effects (P = 0.001 and 0.033 for the Stephens<br />
and Latta sites, respectively) were observed for the first harvest;<br />
however, no effects (P > 0.05) were observed for the<br />
second harvest date across both sites. On the third harvest<br />
date, linear (P = 0.047) and quadratic (P = 0.022) effects were<br />
observed at the Stephens and Latta sites, respectively. The<br />
overall analysis for the entire year indicated that the concentration<br />
<strong>of</strong> NDSN was related to N fertilization rate in a positive<br />
linear manner at both sites (P ≤ 0.023; Table 3).<br />
Cell-wall associated N (NDIN). Concentrations <strong>of</strong><br />
NDIN in these bermudagrass forages ranged from 24.4 to<br />
44.5% <strong>of</strong> total N on individual harvest dates (Table 5). At<br />
both sites, concentrations <strong>of</strong> NDIN declined (P ≤ 0.047) with<br />
N fertilization on the first and third harvest dates, but not on<br />
the second harvest date (P > 0.05). Apparently, the residual or<br />
carryover effects <strong>of</strong> the first application <strong>of</strong> N fertilizer were<br />
not sufficient to affect the relative percentages <strong>of</strong> N partitioned<br />
into the cell wall and cell solubles. The overall analysis<br />
for the entire year indicated that the concentration <strong>of</strong><br />
NDIN was inversely related to N fertilization rate in a linear<br />
manner at both sites (P ≤ 0.023; Table 3).<br />
Acid-detergent insoluble N (ADIN). The N fraction that<br />
is insoluble in acid detergent (ADIN) is generally assumed to<br />
be indigestible; therefore the effects <strong>of</strong> N fertilization on this<br />
fraction are <strong>of</strong> particular interest to nutritionists. Normally,<br />
this fraction is <strong>of</strong> considerable interest when spontaneous<br />
heating has occurred during the storage <strong>of</strong> dry hay or during<br />
the silage fermentation process. Unlike the other N fractions<br />
discussed in this study, substantive differences in concentrations<br />
<strong>of</strong> ADIN were observed between sites. On the first harvest<br />
date, ADIN decreased linearly (P < 0.0001) with N fertilization<br />
rate from 11.48 to 8.32% <strong>of</strong> the total N pool at the<br />
Stephens site (Table 6); however, concentrations <strong>of</strong> ADIN<br />
and fertilization rate were not related (P > 0.05) at the Latta<br />
site (overall mean = 4.69% <strong>of</strong> N). There was no relationship<br />
(P > 0.05) between ADIN and N fertilization rate at either site<br />
for the second harvest date. Linear declines in concentrations<br />
<strong>of</strong> ADIN were observed with N fertilization rate at both the<br />
Stephens (P = 0.002) and Latta (P = 0.011) sites on the final<br />
harvest date. The overall analysis for the entire year indicated<br />
that concentrations <strong>of</strong> ADIN were inversely related to N<br />
fertilization rate in a linear manner at both sites (P ≤ 0.001;<br />
Table 3).<br />
Implications<br />
The results <strong>of</strong> this study suggest that fertilization with<br />
N may result in lower percentages <strong>of</strong> the total plant N pool<br />
being associated with the cell wall. Theoretically, this should<br />
increase the degradability <strong>of</strong> N in the rumen; additional studies<br />
are being planned to verify this hypothesis.<br />
Literature Cited<br />
National Research Council. 2000. 8th rev. ed. Natl. Acad.<br />
Press, Washington, DC.<br />
Sniffen, C. J., et al. 1992. J. Anim. Sci. 70:3562.<br />
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