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(Reference retrieved automatically from Web of Science through information on FAPESP grant and its corresponding number as mentioned in the publication by the authors.)

An extended model of phosphorus metabolism in growing ruminants

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Dias, R. S. [1] ; Lopez, S. [2] ; Patino, R. M. P. [3] ; Silva, T. S. [4] ; Silva Filho, J. C. [5] ; Vitti, D. M. S. S. [4] ; Pecanha, M. R. S. R. [4] ; Kebreab, E. [6] ; France, J. [1]
Total Authors: 9
[1] Univ Guelph, Ctr Nutr Modelling, Guelph, ON N1G 2W1 - Canada
[2] Univ Leon, Dept Anim Prod, CSIC, IGM, E-24071 Leon - Spain
[3] Univ Sucre, Fac Ciencias Agr, Sincelejo, Sucre - Colombia
[4] Univ Sao Paulo, Ctr Energia Nucl Agr, BR-13400970 Sao Paulo - Brazil
[5] Univ Fed Lavras, Dept Zootecnia, BR-37200000 Lavras, MG - Brazil
[6] Univ Calif Davis, Dept Anim Sci, Davis, CA 95616 - USA
Total Affiliations: 6
Document type: Journal article
Source: JOURNAL OF ANIMAL SCIENCE; v. 89, n. 12, p. 4151-4162, DEC 2011.
Web of Science Citations: 3

A major objective of this study was to extend the Vitti-Dias model used to describe P metabolism in ruminants, by adding 2 new pools to the original model to represent the rumen and saliva. An experiment was carried out using 24 male sheep, initial BW of 34.5 kg, aged 8 mo, fed a basal diet supplied with increasing amounts of dicalcium phosphate to provide 0.14, 0.32, 0.49, and 0.65% P in the diet. Sheep were individually housed indoors in metabolic cages and injected with a single dose of 7.4 MBq of (32)P into a jugular vein. Feed intake and total fecal and urinary outputs were recorded and sampled daily for 1 wk, and blood samples were obtained at 5 min, and 1, 2, 4, 6, 24, 48, 72, 96, 120, 144, and 168 h after (32)P injection. Saliva and rumen fluid samples were taken on d 6, 7, and 8. Then, animals were slaughtered and samples from liver, kidney, testicle, muscle, and heart (soft tissue) and bone were collected. Specific radioactivity and inorganic P were then determined in bone, soft tissue, plasma, rumen, saliva, and feces, and used to calculate flows between pools. Increased P intake positively affected total P (r = 0.97, P < 0.01) and endogenous P excretion in feces (r = 0.85, P < 0.01), P flow from plasma to saliva (r = 0.73, P < 0.01), from saliva to rumen (r = 0.73, P < 0.01), and from lower gastrointestinal tract to plasma (r = 0.72, P < 0.01). Urinary P excretion was similar for all treatments (P = 0.35). It was, however, related to plasma P (r = 0.63, P < 0.01) and to net P flow to bone (accretion - resorption; r = -0.64, P < 0.01). Phosphorus intake affected net P flow to soft tissue (P = 0.04) but not net P flow to bone (P = 0.46). Phosphorus mobilized from bone was directed toward soft tissue, as suggested by the correlations between P flow from bone to plasma and net P flow to soft tissue (r = 0.89, P < 0.01), and P flow from plasma to soft tissue and net P flow to bone (r = -0.76, P < 0.01). The lack of effect of dietary P on net P accretion in bone suggests that P demand for bone formation was low and surplus P was partially used by soft tissue. In conclusion, the model resulted in appropriate biological description of P metabolism in sheep and added knowledge of the effects of surplus dietary P on P metabolism. Additionally, the model can be used as a tool to assess feeding strategies aiming to mitigate P excretion into the environment. (AU)

FAPESP's process: 04/14532-5 - Environmental impact of phosphorus excretion in livestock: quantitative analysis of flow phosphorus using bio-mathematical models
Grantee:Dorinha Miriam Silber Schmidt Vitti
Support Opportunities: Research Projects - Thematic Grants