Table 4.
LUB (mg·kg−1 DM) | Dose | Significance of contrast | ||||||||
---|---|---|---|---|---|---|---|---|---|---|
Variable | 0.0 | 1.38 | 5.5 | 22.0 | SEM | Dose × sex P-value2 | P-value2 | Control vs. 1.38 mg·kg−1 | Control vs. 5.5 mg·kg−1 | Control vs. 22.0 mg·kg−1 |
Unshrunk BW, kg | ||||||||||
Initial | 451 | 454 | 455 | 452 | 10.0 | 0.996 | 0.937 | |||
Day 7 | 464 | 469 | 470 | 469 | 10.4 | 0.968 | 0.935 | |||
Day 14 | 474 | 484 | 484 | 478 | 12.3 | 0.962 | 0.655 | |||
Day 28 | 496 | 508 | 506 | 501 | 12.2 | 0.990 | 0.627 | |||
Day 56 | 529 | 545 | 542 | 539 | 15.2 | 0.974 | 0.411 | |||
Final | 567 | 583 | 582 | 582 | 19.4 | 0.916 | 0.257 | |||
NH3, g | ||||||||||
Days 0 to 7 | 415 | 394 | 387 | 326 | 49 | 0.746 | 0.022 | 0.439 | 0.300 | 0.004 |
Days 0 to 14 | 953 | 835 | 801 | 699 | 106 | 0.802 | 0.006 | 0.062 | 0.020 | < 0.001 |
Days 0 to 28 | 2,097 | 1,783 | 1,686 | 1,563 | 265 | 0.573 | 0.006 | 0.027 | 0.006 | < 0.001 |
Days 0 to 56 | 4,619 | 4,089 | 3,888 | 3,763 | 540 | 0.420 | 0.019 | 0.050 | 0.011 | 0.004 |
Days 0 to 91 | 7,783 | 7,093 | 6,860 | 6,751 | 855 | 0.281 | 0.052 | 0.076 | 0.023 | 0.013 |
NH3, g/kg BW | ||||||||||
Days 0 to 7 | 0.89 | 0.84 | 0.82 | 0.70 | 0.106 | 0.619 | 0.003 | 0.278 | 0.139 | <0.001 |
Days 0 to 14 | 2.01 | 1.73 | 1.66 | 1.47 | 0.223 | 0.698 | <0.001 | 0.010 | 0.002 | <0.001 |
Days 0 to 28 | 4.21 | 3.53 | 3.33 | 3.13 | 0.509 | 0.463 | <0.001 | 0.004 | <0.001 | <0.001 |
Days 0 to 56 | 8.66 | 7.50 | 7.14 | 6.99 | 0.871 | 0.258 | <0.001 | 0.004 | <0.001 | <0.001 |
Days 0 to 91 | 13.6 | 12.2 | 11.7 | 11.6 | 1.19 | 0.161 | 0.004 | 0.009 | 0.002 | <0.001 |
1Emissions were measured from an individual CPE (n = 8) over 15-min sampling periods using calibrated, gas-specific analyzers (Thermo Environmental Instruments (TEI), Waltham, MA). This procedure was continuous so that a maximum of 11 sampling periods were available for determination of daily emission rates/animal for each CPE. Daily gas emissions were defined as those within the span beginning at 0800 hours and ending at 0759 hours the next morning. Cumulative emissions were standardized by the BW measured on the day corresponding to the emissions time-period for reporting.
2If the dose × sex interaction was not significant (P > 0.05), contrasts were constructed to evaluate the main effect of dose for the pooled sexes. Statistical significance for dose was declared when P ≤ 0.05 and tendencies were declared when 0.05 < P ≤ 0.10.