The isotopic composition of nitrate produced from nitrification in a hardwood forest floor

Dual isotopic analysis of nitrate (¹⁵N/¹⁴N and ¹⁸O/¹⁶O) is increasingly used to investigate the environmental impacts of human-induced elevated atmospheric nitrate deposition. In forested ecosystems, the nitrate found in surface water and groundwater can originate from two sources: (1) atmospheric deposition, and (2) nitrate produced from nitrification in forest soils (microbial nitrate). Application of the dual nitrate isotope technique for determining the relative importance of nitrate sources in forested catchments requires knowledge of the isotopic composition of microbial nitrate. We excluded precipitation inputs to three zero-tension lysimeters installed below the F-horizon (Oe) at the Turkey Lakes Watershed (TLW) in order to measure the isotopic composition of microbial nitrate produced in situ. To our knowledge, this is the first in situ study of the isotopic composition of microbial nitrate in forest soils. Over a 2-week period, nitrate produced by nitrification was periodically flushed to the lysimeters by watering the area with a nitrogen-free solution. Nitrate produced in the forest floor had δ¹⁸O values ranging from +3.1‰ to +10.1‰ with a mean of +5.2‰. These values were only slightly higher than from the expected value of +1.0‰ calculated for chemolithoautotrophic nitrification, which depends on the δ¹⁸O of available O₂ and H₂O. In addition to nitrate, we also collected soil gas to determine if soil respiration and O₂ diffusion affected soil gas δ¹⁸O-O₂, which is typically assumed to be identical to atmospheric O₂ (+23.5‰) when calculating microbial nitrate δ¹⁸O values. No significant difference in δ¹⁸O-O₂ from atmospheric O₂ was found in forest soils to a depth of 55 cm, and therefore ¹⁸O-enrichment of soil gas O₂ could not explain the modest enrichment of nitrate ¹⁸O. Evaporative ¹⁸O-enrichment of soil water available to nitrifiers in the forest floor is a plausible mechanism for slightly elevated nitrate δ¹⁸O values. However, the observed nitrate δ¹⁸O values could also be explained by a minor contribution of nitrate from heterotrophic nitrifiers. The δ¹⁵N of nitrate produced ranged from −10.4 to −7.3‰ and, as expected, was depleted in ¹⁵N relative to soil organic nitrogen. Microbial nitrate produced in the forest floor was also significantly depleted in ¹⁵N relative to microbial nitrate exported in groundwater and headwater streams at the TLW. We hypothesize that ¹⁵N-depleted forest floor nitrate is not detected in groundwaters largely because of: (1) the immobilization of forest floor nitrate in the mineral soil and (2) the mixing of the remaining forest floor nitrate with nitrate generated in the mineral soil, which is expected to have higher δ¹⁵N values. This study demonstrates that current methods of calculating a priori the δ¹⁸O of microbial nitrate provide a reasonable value for nitrate produced by nitrification at the TLW.