Soil slurry incubations were performed to evaluate the contributions of AOA and AOB/comammox to the net nitrification potential of both soils. For the assays, fresh soil (4 g) and 30 ml of MilliQ water were weighed in 125 ml Wheaton bottles, and NH
4Cl was added to a final concentration of 1 mM. All bottles were sealed gas tight with 33 mm interlock butyl septa. To differentiate between the contribution of AOA and AOB/comammox to soil nitrification the AOB and comammox specific inhibitors
1-octyne (4 µM) and allyl-2-thiourea (ATU, 100 µM) (Sigma-Aldrich, St. Louis, MO, USA) treatments were included (Taylor et al. 2013 (
link), 2015 (
link)). The negative control, in which nitrification activity was completely inhibited, received 1 mM phenylacetylene (McCarty and Bremner 1986 (
link)). Sealed bottles were shaken at 180 r/m at 23°C for 72 h. Each treatment included four replicate soil slurries and 1 ml subsamples were collected with a 1-ml syringe through the butyl septa daily during the incubation period to measure NO
3− accumulation as described above. NO
2− accumulation was also assessed but was below the limit of quantification of 15 µM in all samples at all timepoints. Soil net nitrification potential (µg N g
−1 soil day
−1) was calculated by subtracting the initial NO
3− concentration from the accumulated NO
3− concentration, normalized to soil weight and incubation time.
Rojas-Pinzon P.A., Prommer J., Sedlacek C.J., Sandén T., Spiegel H., Pjevac P., Fuchslueger L, & Giguere A.T. (2024). Inhibition profile of three biological nitrification inhibitors and their response to soil pH modification in two contrasting soils. FEMS Microbiology Ecology, 100(6), fiae072.