Abstract
The impact of different N regimes on P intake and excretion by grazing cattle and P return to soil from feces in a P-enriched pasture was investigated. Six 0.28-ha plots were over seeded with triticale (×Triticosecale rimpaui Wittm.) and crimson clover (Trifolium incarnatum) into tall fescue (Lolium arundinacea)/bermudagrass (Cynodon dactylon). Treatments included: 100% of N in split application, 50% of N in single application, and 0% of N. In summer, plots were over seeded with cowpea (Vigna unguiculata) and fertilizer treatments were applied. Forage intake was estimated from fecal excretion and fecal degradation and nutrient return to soil at 0, 28, 56, 84, and 112 days after application were determined. Forage P was not affected by season or treatment (P > 0.10); forage P mass was greater in cool than warm season. Phosphorus intake and water-soluble P output were not affected (P > 0.10) by season or treatment. Phosphorus output increased (P = 0.087) with increasing N in cool season, but not warm season. Soil P was greater (P < 0.0001) in warm than cool season. Feces remaining, P, and water-soluble P in feces were not affected by N treatment or season, but decreased (P < 0.10) with time. Sufficient P was returned to soil from feces to support forage growth, even in the absence of N fertilization. In a high-P pasture, N did not affect intake and fecal returns of P by cattle, foliar P uptake, nor rate and extent of assimilation of P into soil from feces.
Highlights
Animal manures have been used for millennia as a source of nutrients for crops of all types
Foliar P concentration and forage P mass were affected by soil P status, P fertilization, stage of forage maturity, forage management practices, P apportionment among individual plant species, and meteorological conditions [28]
We propose that the dramatic increase of warm season (WS) soil P concentrations was possibly
Summary
Animal manures have been used for millennia as a source of nutrients for crops of all types. With the advent of modern animal agriculture, manure-derived nutrients have become concentrated in production locales that cannot fully assimilate them. Nutrients such as P are potentially a major concern when considering quality of water runoff from beef cattle operations. When using manure from an animal feeding operation, manure is evenly spread across a pasture using a mechanical spreader or irrigation. A single beef-cow dung patch covers approximately 0.06 m2 [1]; and when calculated on an annual basis, the total surface area of a pasture that receives dung may only be 27% to 40% of the total area [2]
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