Paper No. 87-12
Presentation Time: 11:00 AM
NITROGEN SOURCES AND SIGNATURES IN SULFURIC ACID CAVES
BEST, Mackenzie1, WANKEL, Scott D.2, GREEN, Katelyn3, GRAHAM, Heather V.4, STERN, Jennifer4, MACALADY, Jennifer, Ph.D.5 and JONES, Daniel6, (1)Department of Earth and Evironmental Sciences, New Mexico Institute of Mining and Technology, 801 Leroy Place, Socorro, NM 87801, (2)Department of Chemistry and Geochemistry, Woods Hole Oceanographic Institution, Woods Hole, MA 02543, (3)Department of Biology, New Mexico Institute of Mining and Technology, 801 Leroy Place, Socorro, NM 87801, (4)NASA Goddard Space Flight Center, Astrobiology Analytical Laboratory, Code 691, Bldg 34, Room S139, Greenbelt, MD 20771, (5)Geosciences, Pennsylvania State University, University Park, PA 16802, (6)Earth and Environmental Science, New Mexico Institute of Mining and Technology, Socorro, NM 87801
“Sulfidic” caves contain robust, chemosynthetic ecosystems where reduced, H
2S-rich groundwaters are exposed to oxygen at the cave water table. Cave streams host white mats created by sulfide-oxidizing microorganisms. Above the water table, viscous biofilms-forming sulfide oxidizers live on H
2S(
g) vapors that degas from turbulent springs and streams. The chemoautotrophic nature of these cave ecosystems was recognized because d
13C and d
15N values of organic matter from the sulfidic water table are distinct from surface sources. In particular, d
15N of organic material above the water table can be very low, with d
15N values below -25‰, indicating that there are unusual sources or cycling of nitrogen in these areas. We are using molecular, metagenomic, and isotopic tools to evaluate different sources and key nitrogen cycling populations in this subaerial cave environment.
Previous authors have hypothesized that the extremely negative d15N values result from strong fractionation during NH3(g) volatilization (Jones et al., 2008; Stern et al., 2003). By this hypothesis, trace NH3(g) flux from circumneutral streams is trapped in acidic biofilms and water on the walls; however, the isotopic composition of NH3/NH4+ in the streams and air have not been measured, and other N sources have not been accounted for. We deployed passive NH3(g) samplers for 2 and 9 months in the sulfidic Frasassi cave, in areas that are close to and far from the degassing streams. NH4+ in the stream was consistently δ15N = -1‰, and preliminary results from passive samplers show a much lighter values between -13 and 27‰, consistent with a much lighter source in the cave atmosphere. We will validate these results with additional samplers, and are now testing an active sampling strategy.
Heavier organic d15N values further from the streams suggest that wall communities rely on N2 fixation or another source. However, nifH amplification and high-throughput nifH amplicon sequencing shows that potential N2-fixers are not abundant or diverse on cave walls, so these subaerial communities may rely on other N sources carried by air currents or waters. We will discuss N biogeochemistry in different cave zones, and compare microbial N cycling in Frasassi wall biofilms to those from other sulfidic caves with different groundwater geochemistry and surface connections.