To examine potential differences in the impacts of long-term N fertilization on root-microbial interactions between mycorrhizal types, we established a plot network of 6 AM and 6 ECM dominated (>65% diameter at breast height) 10x10 m plots in the fertilized and reference watersheds. Dominant AM and ECM trees were similar between watersheds with AM trees represented by Tulip poplar (Liriodendron tulipifera), red maple (Acer rubrum), black cherry (Prunus serotina), and sugar maple (Acer saccharum). Dominant ECM trees were sweet birch (Betula lenta), red oak (Quercus rubra), and American beech (Fagus grandifolia).
To capture variability across the growing season, we sampled soils in each plot in May, June, and September of 2017. In each plot we extracted three 10 x 10 cm organic horizon layers and homogenized them into a single sample defining this as the OH soil fraction. Next, we sampled four 5 cm diameter mineral soil cores to a depth of 15 cm beneath the OH layer and homogenized these by plot. All samples were kept on ice and transported to West Virginia University for further processing within 48-72 h. Upon return to the lab, we separated rhizosphere soil from mineral soil samples via the soil-adhesion method wherein the rhizosphere soil fraction was operationally defined as soil that remained clung to roots after modest shaking (Phillips & Fahey, 2005). After removal of roots, all soils were passed through a 2 mm sieve and stored at -80°C until further analysis.
To determine the extent to which N fertilization impacts microbial allocation to extracellular enzymes, we assayed the potential activity of hydrolytic enzymes that release N (N-acetylglucosaminidase; NAG), phosphorus (acid phosphatase; AP), and simple carbon (ß-glucosidase; BG). In addition, we measured microbial allocation to complex C degrading oxidative enzymes phenol oxidase and peroxidase. Briefly, 1g of thawed soil was homogenized in 50mM sodium acetate buffer (pH 5.0). Next, hydrolytic activities were determined using a fluorometric microplate assay (Gemini XPS, Molecular Devices, USA). with methylumbelliferone-linked substrates and oxidative enzymes using a colorimetric microplate assay (Tecan Infinite 200 Pro, Switzerland) with L-3,4-dihydroxyphenylalanine linked substrates according to Saiya-Cork et al., 2002.
Saiya-Cork KR, Sinsabaugh RL, Zak DR (2002) The effects of long term nitrogen deposition on extracellular enzyme activity in an Acer saccharum forest soil. Soil Biology and Biochemistry, 34, 1309–1315. DOI: 10.1016/S0038-0717(02)00074-3.
See protocol: https://allison.bio.uci.edu/protocols/fluorimetricenzymeprotocol.pdf