Abstract

Storage and flux of nitrogen were studied in several contrasting lodgepole pine (Pinus contorta spp.latifolia) forests in southeastern Wyoming. The mineral soil contained most of the N in these ecosystems (range of 315–860 g · m−2), with aboveground detritus (37.5–48.8g · m−2) and living biomass (19.5–24.0 g · m−2) storing much smaller amounts. About 60–70% of the total N in vegetation was aboveground, and N concentrations in plant tissues were unusually low (foliage = 0.7% N), as were N input via wet precipitation (0.25 g · m−2 · yr−1), and biological fixation of atmospheric N (<0.03 g · m−2 · yr−1, except locally in some stands at low elevations where symbiotic fixation by the leguminous herbLupinus argenteus probably exceeded 0.1 g · m−2 · yr−1). Because of low concentrations in litterfall and limited opportunity for leaching, N accumulated in decaying leaves for 6–7 yr following leaf fall. This process represented an annual flux of about 0.5g · m−2 to the 01 horizon. Only 20% of this flux was provided by throughfall, with the remaining 0.4g · m−2 · yr−1 apparently added from layers below. Low mineralization and small amounts of N uptake from the 02 are likely because of minimal rooting in the forest floor (as defined herein) and negligible mineral N (< 0.05 mg · L−1) in 02 leachate. A critical transport process was solubilization of organic N, mostly ‘fulvic acids’. Most of the organic N from the forest floor was retained within the major tree rooting zone (0–40 cm), and mineralization of soil organic N provided NH4 for tree uptake. Nitrate was at trace levels in soil solutions, and a long lag in nitrification was always observed under disturbed conditions. Total root nitrogen uptake was calculated to be 1.25 gN · m−2 · yr−1 with estimated root turnover of 0.37-gN · m−2 · yr−1, and the soil horizons appeared to be nearly in balance with respect to N. The high demand for mineralized N and the precipitation of fulvic acid in the mineral soil resulted in minimal deep leaching in most stands (< 0.02 g · m−2 · yr−1). These forests provide an extreme example of nitrogen behavior in dry, infertile forests.

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