Table 3.
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 final BW, kg3 | 567 | 583 | 582 | 582 | 19.4 | 0.916 | 0.257 | |||
HCW, kg | 349 | 364 | 365 | 365 | 11.7 | 0.865 | 0.035 | 0.019 | 0.014 | 0.014 |
NH3 | ||||||||||
Total emissions, g/animal | 7,783 | 7,093 | 6,860 | 6,751 | 855 | 0.281 | 0.052 | 0.076 | 0.023 | 0.013 |
Standardized by BW, g/kg | 13.6 | 12.1 | 11.7 | 11.6 | 1.19 | 0.161 | 0.004 | 0.009 | 0.002 | <0.001 |
Standardized by HCW, g/kg | 22.3 | 19.5 | 18.7 | 18.5 | 1.97 | 0.147 | 0.001 | 0.004 | <0.001 | <0.001 |
CH4 | ||||||||||
Total emissions, g/animal | 10,466 | 10,692 | 10,763 | 10,476 | 638 | 0.712 | 0.895 | — | — | — |
Standardized by BW, g/kg | 18.4 | 18.3 | 18.5 | 18.0 | 1.06 | 0.439 | 0.858 | — | — | — |
Standardized by HCW, g/kg | 30.0 | 29.3 | 29.5 | 28.7 | 1.81 | 0.376 | 0.601 | — | — | — |
CO2 | ||||||||||
Total emissions, kg/animal | 720 | 758 | 734 | 755 | 47.3 | 0.616 | 0.302 | — | — | — |
Standardized by BW, g/kg | 1,268 | 1,299 | 1,261 | 1,299 | 61.3 | 0.322 | 0.268 | — | — | — |
Standardized by HCW, g/kg | 2,061 | 2,081 | 2,013 | 2,070 | 107.8 | 0.269 | 0.331 | — | — | — |
H2S | ||||||||||
Total emissions, g/animal | 20.6 | 19.9 | 20.3 | 20.0 | 6.04 | 0.581 | 0.975 | — | — | — |
Standardized by BW, g/kg | 0.035 | 0.033 | 0.035 | 0.033 | 0.0110 | 0.417 | 0.905 | — | — | — |
Standardized by HCW, g/kg | 0.057 | 0.055 | 0.055 | 0.055 | 0.0176 | 0.379 | 0.776 | — | — | — |
N2O4 | ||||||||||
Total emissions, g/animal | −27.4 | −36.8 | −36.4 | −34.7 | 10.2 | 0.279 | 0.627 | — | — | — |
Standardized by BW, g/kg | −0.046 | −0.062 | −0.060 | −0.060 | 0.0154 | 0.306 | 0.693 | — | — | — |
Standardized by HCW, g/kg | −0.075 | −0.097 | −0.095 | −0.095 | 0.0264 | 0.311 | 0.742 | — | — | — |
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. Emissions were measured from 0800 hours on day 1 until 0500 hours on day 91.
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.
3Unshrunk; initial BW did not differ by dose (P = 0.937; Table 6).
4Measured values from CPE were less than the values reported from ambient air, resulting in negative values.