Abstract

Abstract. Many alpine areas are experiencing deglaciation, biogeochemical changes driven by temperature rise, and changes in atmospheric deposition. There is mounting evidence that the water quality of alpine streams may be related to these changes, including rising atmospheric deposition of carbon (C) and nutrients. Given that barren alpine soils can be severely C limited, atmospheric deposition sources may be an important source of C and nutrients for these environments. We evaluated the magnitude of atmospheric deposition of C and nutrients to an alpine site, the Green Lake 4 catchment in the Colorado Rocky Mountains. Using a long-term dataset (2002–2010) of weekly atmospheric wet deposition and snowpack chemistry, we found that volume weighted mean dissolved organic carbon (DOC) concentrations were 1.12 ± 0.19 mg l−1, and weekly concentrations reached peaks as high at 6–10 mg l−1 every summer. Total dissolved nitrogen concentration also peaked in the summer, whereas total dissolved phosphorus and calcium concentrations were highest in the spring. To investigate potential sources of C in atmospheric deposition, we evaluated the chemical quality of dissolved organic matter (DOM) and relationships between DOM and other solutes in wet deposition. Relationships between DOC concentration, fluorescence, and nitrate and sulfate concentrations suggest that pollutants from nearby urban and agricultural sources and organic aerosols derived from sub-alpine vegetation may influence high summer DOC wet deposition concentrations. Interestingly, high DOC concentrations were also recorded during "dust-in-snow" events in the spring, which may reflect an association of DOM with dust. Detailed chemical and spectroscopic analyses conducted for samples collected in 2010 revealed that the DOM in many late spring and summer samples was less aromatic and polydisperse and of lower molecular weight than that of winter and fall samples. Our C budget estimates for the Green Lake 4 catchment illustrated that wet deposition (9.9 kg C ha−1 yr−1) and dry deposition (6.9 kg C ha−1 yr−1) were a combined input of approximately 17 kg C ha−1 yr−1, which could be as high as 24 kg C ha−1 yr−1 in high dust years. This atmospheric C input approached the C input from microbial autotrophic production in barren soils. Atmospheric wet and dry deposition also contributed 4.3 kg N ha−1 yr−1, 0.15 kg P ha−1 yr−1, and 2.7 kg Ca2+ ha−1 yr−1 to this alpine catchment.

Highlights

  • In comparison to low elevation ecosystems, alpine environments, often located in remote, high-elevation areas, are sensitive to atmospheric deposition (Psenner, 1999; Ballantyne et al, 2011; Mladenov et al, 2011)

  • Mean dissolved organic carbon (DOC), total dissolved nitrogen (TDN), total dissolved phosphorus (TDP), and Ca2+ concentrations measured at the Soddie collector were nearly identical to those measured at the National Atmospheric Deposition Program (NADP) CO02 collector (Supplement Fig. S3), even though there is an elevational difference of 175 m between the two collectors

  • Our results demonstrated that atmospheric deposition represents a substantial input of C, N, P, and Ca2+ to the Green Lake 4 catchment

Read more

Summary

Introduction

In comparison to low elevation ecosystems, alpine environments, often located in remote, high-elevation areas, are sensitive to atmospheric deposition (Psenner, 1999; Ballantyne et al, 2011; Mladenov et al, 2011). N. Mladenov et al.: Atmospheric deposition as a source of carbon and nutrients is a trend of increasing nitrate export in surface waters that has been observed in many alpine and high-elevation catchments, such as those in the Colorado Rocky Mountains, USA (Williams et al, 2011; Baron et al, 2009), the Alps of northern Italy (Rogora, 2007), and southern Norway (de Wit et al, 2008), for which the process-level controls are just beginning to be explored. Baron et al (2009) suggested that observed increases in nitrate export from the high-elevation Loch Vale catchment in the Colorado Front Range were the result of warmer temperatures that are melting ice in glaciers and rock glaciers. Overall net production (primary production minus respiration) from alpine soils (Blanken et al, 2009) is negative, which means the C loss from microbial respiration probably exceeds the autotrophic C production in these systems

Methods
Results
Discussion
Conclusion
Full Text
Published version (Free)

Talk to us

Join us for a 30 min session where you can share your feedback and ask us any queries you have

Schedule a call