Liquid hog manure (LHM) and solid cattle manure (SCM) are valuable soil amendments for the nutrients and organic matter they augment. However, desire to mitigate the N 2 O, CO 2 , and CH 4 uxes associated with their use has led to the question of whether biochar co-applied with LHM and SCM could mitigate these greenhouse gas uxes. A split-plot design was used at two agricultural eld sites with contrasting soil types (Brown and Black) in Saskatchewan, Canada, to assess the effect of LHM and SCM (100 kg N ha -1 ), alone and in combination with two different biochars applied at 8 Mg C ha -1 ; produced using either slow or fast pyrolysis of willow (Salix spp.) feedstock. Intact cores were collected from the plots and the N 2 O, CO 2 , and CH 4 uxes were measured during a six-week lab incubation. The cumulative N 2 O emissions (37.9-1956.8 mg m -2 ), net CO 2 uxes (665.2-1233.2 g m -2 ), and CH 4 consumption (28.3-90.0 mg m -2 ) were consistent with previously reported Canadian temperate agricultural soils, with and without LHM, SCM, or biochar addition. The impact of manure amendment on greenhouse gas uxes was more apparent with LHM than SCM; re ecting higher inorganic N content, narrower C:N, and more easily mineralizable carbon in LHM. Overall, co-applying biochar with the manure sources reduced the manure-related N 2 O emissions 31.5 to 43.1% and increased CH 4 consumption 94.1% to 2.1× compared with manure alone. Regardless of soil type, neither of the biochars co-applied with the manures affected the net CO 2 uxes compared with manure alone. The N 2 O emissions were principally in uenced by the impact of biochar addition on NO 3 -N supply and pH, while the net CO 2 uxes were controlled by the opposing effects of heterotrophic (i.e., CO 2 production) and autotrophic (i.e., CO 2 consumption) respiration. The CH 4 consumption was related to the NH 4 -N supply and its in uence on autotrophic methanotrophy. Co-application of biochar along with manure, particularly the combination of slow pyrolysis biochar and LHM, decreased N 2 O emissions and increased CH 4 consumption in these young temperate prairie soils; presumably, through enhanced abiotic sorption and biotic N immobilization, in addition to promoting greater methanotrophic activity.