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Tackling the future challenges of Organic Animal Husbandry - vTI

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! Agriculture and Forestry Research, Special Issue No 362 (Braunschweig, 2012) ISSN 0376-0723<br />

Download: www.vti.bund.de/en/startseite/vti-publications/landbauforschung-special-issues.html<br />

ported by Ayano (2005) for P. maximum unimproved that was fertilized with different animal manures<br />

(Table 2). This might be due to different factors such as <strong>the</strong> soil fertility as well as <strong>the</strong> feed<br />

<strong>of</strong>fered <strong>the</strong> animals that produced <strong>the</strong> manure used for fertilizing <strong>the</strong> grasses. However, <strong>the</strong> trend in<br />

<strong>the</strong> change in concentration <strong>of</strong> P with plant maturity is in line with <strong>the</strong> report <strong>of</strong> Minson (1990). The<br />

P contents however fell within <strong>the</strong> recommended (1-4.8 g/kg) range for different classes <strong>of</strong><br />

ruminant animals as stated by McDowell (1992; 1997). The values recorded for Ca content <strong>of</strong> <strong>the</strong><br />

grasses as influenced by <strong>the</strong> manure types in this study is in consonance with <strong>the</strong> report <strong>of</strong> Chang et<br />

al. (1994) in which <strong>the</strong> Ca content <strong>of</strong> zero-manured barley had higher concentration. This might be<br />

as a result <strong>of</strong> salinity associated with manure application (Chang et al., 1991), also chelating properties<br />

<strong>of</strong> manure could be responsible in which elements such as calcium are bond into a chelate with<br />

<strong>the</strong> soil colloids and are release gradually and this is one <strong>of</strong> <strong>the</strong> importance <strong>of</strong> manure as <strong>the</strong>y are<br />

known for binding up mineral elements against being washed away during erosion. The requirement<br />

<strong>of</strong> different ruminant animals in terms <strong>of</strong> Ca concentration ranged between 1.8 to 8.2 g/kg as<br />

reported by McDowell (1992; 1997). The crude protein (CP) recorded for <strong>the</strong> grasses as affected by<br />

<strong>the</strong> animal manure were within <strong>the</strong> range <strong>of</strong> 82– 112.8 g/kg reported by Bilal et al. (2001) when<br />

farmyard manure was applied to P. purpureum (Table 2). The values were generally above <strong>the</strong> critical<br />

limit below which forage intake by ruminants and rumen microbial activity could be negatively<br />

affected (Van Soest, 1994). These values were also above <strong>the</strong> minimum range <strong>of</strong> 65–80 g/kg<br />

prescribed for optimum performance <strong>of</strong> tropical ruminant animals (Minson, 1981).<br />

Table 2. Effects <strong>of</strong> manure type and age at harvest on <strong>the</strong> phosphorus (P) calcium (Ca) and<br />

crude protein (CP) composition <strong>of</strong> three grass species.<br />

Factors P Ca CP<br />

Manure type<br />

Cattle 1.67 d 7.11 d 101.60 a<br />

Swine 2.48 b 7.91 c 100.84 a<br />

Poultry 3.33 a 9.51 b 88.95 c<br />

Sheep and goats 1.90 c 9.76 ab 93.62 b<br />

Control 1.89 c 10.41 a 84.94 c<br />

SEM 0.2 0.4 2.9<br />

Species<br />

P. maximum (Local) 1.80 b 8.19 b 92.52 b<br />

P. maximum (Ntchisi) 1.75 b 10.01 a 91.33 b<br />

P. purpureum 3.22 a 8.62 b 98.22 a<br />

SEM 0.1 0.4 2.4<br />

Age at harvest (WAP)<br />

4 2.24 b 9.19 b 110.60 a<br />

8 2.53 a 10.15 a 101.54 b<br />

12 2.59 a 8.65 b 90.52 c<br />

16 1.66 c 7.78 c 73.32 d<br />

SEM 0.2 0.4 1.9<br />

P-value<br />

Manure

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