Agronomy Journal Journal of Natural Resources and Life Sciences Education
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Published online 1 May 1989
Published in Agron J 81:508-512 (1989)
© 1989 American Society of Agronomy
677 S. Segoe Rd., Madison, WI 53711 USA
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Soil Potassium Distribution in Grazed K-31 Tall Fescue Pastures as Affected by Fertilization and Endophytic Fungus Infection Level

S. R. Wilkinson* and J. A. Stuedemann

USDA-ARS, Southern Piedmont Conservation Res. Ctr, Watkinsville, GA 30677

D. P. Belesky

USDA-ARS, Northern Appalachian Soil and Water Conservation Res. Ctr, Beckley, WV

* Corresponding author.

Fertilizer requirements of grazed pastures may be influenced by the spatial distribution of nutrients in animal excreta. This experiment was conducted to determine the effect of two levels of fertilization and endophytic fungus (Acremonium coenophialum Morgan-Jones et Gams) infection of Kentucky-31 tall fescue (Festucu arundinaceu Shreb) on the lateral and vertical distribution of soil K after 3 yr of grazing. Each pasture consisted of 0.7 ha of a Cecil sandy clay loam (clayey, kaolinitic, thermic Typic Hapludult,) and was grazed using the put-and-take method. Forage was removed only by grazing. Endophytic fungus levels were 20% (Low endophytic fungus, LE) and 52% (high endophytic fungus HE), and fertilizer rates were 134-15-56 kg N-P-K (Low fertilizer LF), and 336-37-139 kg N-P-K ha–1 yr (high fertilizer HF) in a 2 x 2 factorial replicated twice in a randomized block design. Each pasture was divided into 12 zones with each zone sampled separately to a depth of 122 cm before the grazing experiment began and then annually for 3 yr. Potassium did not accumulate in the majority of the pasture area at either fertility level except near the waterer, mineral feeder, and shade. Potassium accumulation rates in this area, determined by linear regression, were 7, 23, 23, and 46 kg K yr-I for LELF, LEHF, HELF, and HEHF treatments, respectively. These amounts were equivalent to 18, 24, 59, and 47% of the fertilizer K applied to the 0.7 ha pastures for the LELF, LEHF, HELF, and HEHF treatments, respectively. This rtccumulation was a result of animal grazing and resting behavior. Much of the K accumulated below 15 cm. Transfer of K by grazing steers to camping zones and subsequent leaching increased with fertility level and endophyte infection level. This redistribution reduces effectiveness of K recycling under grazing, and increases fertilizer K requirements in non-camping zones.

Received for publication May 9, 1988.


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