Nitrogen (N) is a limiting nutrient to the productivity of terrestrial ecosystems (Chapin et al., 2011;Wieder et al., 2015), particularly of forest ecosystems, which globally act as important carbon sinks (Pan et al., 2011). Nevertheless, anthropogenic N emissions since the industrial revolution have drastically increased atmospheric N inputs into forests (Gruber & Galloway, 2008), which has influenced the carbon sequestration function of forests (Law, 2013), climate feedbacks (Bonan, 2008), biodiversity (Phoenix et al., 2006, and water and air quality (Stevens, 2019), through changing the soil N and carbon cycles. Thus, it is pivotal to improve our understanding of forest soil N cycle and its response to atmospheric N deposition.Microbial N transformations, including the depolymerization of high-molecular-weight organic N, organic N mineralization, nitrification, and denitrification are critical in the soil N cycle (Kuypers et al., 2018;Schimel & Bennett, 2004). Depolymerization, mineralization, and nitrification control the pool sizes of soil labile N (denoted as extractable organic N [EON], ammonium [NH 4 + ], and nitrate [NO 3 − ] hereafter) (Chapin et al., 2011;Hietz et al., 2011), while denitrification contributes most to ecosystem N losses by gaseous N losses through nitrous oxide, nitric oxide, and N 2 gas (Stark & Hart, 1997). Thus, they are important in regulating N bioavailability in soils (Schimel & Bennett, 2004). Microbes are exerting a role of being an N transformation "valve," thereby controlling these multi-step transformations and further controlling the pool sizes of initial substrates (IS), residual substrates (RS), and cumulative products (CP) of each N transformation process (Kuypers et al., 2018). The fractions of soil N transformations (denoted as f hereafter, f = CP/IS) directly represent the fraction of substrates that is converted to products, and therefore can provide a straightforward evaluation of soil N-cycle patterns. Although soil N transformations have been extensively studied (Cheng et al., 2019;, there is still a lack of direct evidence on the fractions transformed by different soil N processes (Fang et al., 2012;Rütting et al., 2015), in part due to the challenges of determining the real CP pools in the complex and continuously dynamic microbial N networks.The methodologies used to study soil N transformations mainly include measurements of soil net and gross N transformation rates (