Abstract
Vehicles are an important source for N deposition that may negatively impact roadside ecosystems. While elevated roadside N deposition has been found in many locations, it is not yet known if vehicle emissions cause measurable increases of N deposition in complex, mountainous terrain adjacent to roads. To address this, this study investigated the effect of vehicle N emissions on throughfall (through trees) and open N deposition in a high traffic corridor in mountainous terrain of Rocky Mountain National Park, Colorado, USA. We measured bulk (wet + dry) atmospheric N deposition in throughfall and open samplers along two transects of 750 (throughfall) and 225 (open) m moving away from the road using ion exchange resin (IER) collectors. Contrary to most studies of roadside N deposition, we found no influence of road proximity on inorganic N deposition in throughfall or open sites, possibly due to terrain complexity. Interactions with vegetation modified regional N deposition; throughfall sites had 69% higher nitrate (NO3−) deposition than open sites and larger trees were associated with higher ammonium (NH4+) deposition as compared to smaller trees. When comparing to regional sites that are part of national monitoring networks, we confirmed that our estimates were unaffected by vehicle emissions as our throughfall IER collectors had similar total inorganic N deposition as wet + dry deposition from regional sites (8.64–13.56 vs 10.72–12.14 g N ha−1 day−1, respectively). These findings do not negate vehicles as a local source of N emissions but suggest elevated N deposition adjacent to busy roads cannot be assumed for complex terrains. Instead, environmental variables may be more important drivers than proximity to roads in topographically complex ecosystems.
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Data Availability
The datasets generated during and/or analyzed during the current study are available in the Environmental Data Initiative repository: https://doi.org/10.6073/pasta/3b9095eb0d80afb6456a61ab37bb6b72
References
Adriaenssens, S., et al. (2011). Foliar nitrogen uptake from wet deposition and the relation with leaf wettability and water storage capacity. Water, Air, & Soil Pollution, 219, 43–57.
Baron, J. S., Rueth, H. M., Wolfe, A. M., Nydick, K. R., Allstott, E. J., Minear, J. T., & Moraska, B. (2000). Ecosystem responses to nitrogen deposition in the Colorado Front Range. Ecosystems, 3, 352–368. https://doi.org/10.1007/s100210000032
Benedict, K., Carrico, C., Kreidenweis, S., Schichtel, B., Malm, W., & Collett, J., Jr. (2013a). A seasonal nitrogen deposition budget for Rocky Mountain National Park. Ecological Applications, 23, 1156–1169.
Benedict, K. B., Day, D., Schwandner, F. M., Kreidenweis, S. M., Schichtel, B., Malm, W. C., & Collett, J. L., Jr. (2013b). Observations of atmospheric reactive nitrogen species in Rocky Mountain National Park and across northern Colorado. Atmospheric Environment, 64, 66–76.
Benedict, K. B., et al. (2018). Impact of front range sources on reactive nitrogen concentrations and deposition in Rocky Mountain National Park. PeerJ, 6, e4759.
Bettez, N. D., Marino, R., Howarth, R. W., & Davidson, E. A. (2013). Roads as nitrogen deposition hot spots. Biogeochemistry, 114, 149–163.
Bignal, K. L., Ashmore, M. R., Headley, A. D., Stewart, K., & Weigert, K. (2007). Ecological impacts of air pollution from road transport on local vegetation. Applied Geochemistry, 22, 1265–1271.
Bishop, G. A., & Stedman, D. H. (2015). Reactive nitrogen species emission trends in three light-/medium-duty United States fleets. Environmental Science & Technology, 49, 11234–11240.
Cape, J. N., Tang, Y. S., Van Dijk, N., Love, L., Sutton, M. A., & Palmer, S. C. F. (2004). Concentrations of ammonia and nitrogen dioxide at roadside verges, and their contribution to nitrogen deposition. Environmental Pollution, 132, 469–478. https://doi.org/10.1016/j.envpol.2004.05.009
Carslaw, D. C., Farren, N. J., Vaughan, A. R., Drysdale, W. S., Young, S., & Lee, J. D. (2019). The diminishing importance of nitrogen dioxide emissions from road vehicle exhaust. Atmospheric Environment. https://doi.org/10.1016/j.aeaoa.2018.100002
Clark, S. C., Barnes, R. T., Oleksy, I. A., Baron, J. S., & Hastings, M. G. (2021). Persistent nitrate in alpine waters with changing atmospheric deposition and warming trends. Environmental Science & Technology, 55, 14946–14956.
Clow, D. W., Roop, H. A., Nanus, L., Fenn, M. E., & Sexstone, G. A. (2015). Spatial patterns of atmospheric deposition of nitrogen and sulfur using ion-exchange resin collectors in Rocky Mountain National Park, USA. Atmospheric Environment, 101, 149–157.
Cook, E. M., Sponseller, R., Grimm, N. B., & Hall, S. J. (2018). Mixed method approach to assess atmospheric nitrogen deposition in arid and semi-arid ecosystems. Environmental Pollution, 239, 617–630.
Creany, N. & Monz, C. (2022). Reservation for Bear Lake at 10am, party of four: A look into the RMNP Timed Entry Permit System from 2020 to 2021 [Conference Presentation].Continental Divide Research Learning Center: Science Behind the Scenery Webinar Series. Estes Park, CO.
Davison, J., et al. (2020). Distance-based emission factors from vehicle emission remote sensing measurements. Science of the Total Environment, 739, 139688.
De Schrijver, A., et al. (2008). Effect of vegetation type on throughfall deposition and seepage flux. Environmental Pollution, 153, 295–303.
Elliott, E. M., et al. (2009). Dual nitrate isotopes in dry deposition: Utility for partitioning NOxsource contributions to landscape nitrogen deposition. Journal of Geophysical Research: Biogeosciences, 114, 1–15. https://doi.org/10.1029/2008JG000889
Environmental Protection agency (EPA). (2020). 2017 National Emissions Inventory Data. Air Emissions Inventories. Available at: https://www.epa.gov/air-emissions-inventories/reports-and-summaries. Accessed Nov 2022.
Environmental Protection Agency (EPA). (2021). 2017 National Emissions Inventory Report. Available at: https://gispub.epa.gov/neireport/2017/. Accessed Nov 2022.
Erisman, J. W., & Draaijers, G. (2003). Deposition to forests in Europe: Most important factors influencing dry deposition and models used for generalization. Environmental Pollution, 124, 379–388.
Evans, C. D., et al. (2008). Does elevated nitrogen deposition or ecosystem recovery from acidification drive increased dissolved organic carbon loss from upland soil? A review of evidence from field nitrogen addition experiments. Biogeochemistry, 91, 13–35.
Fang, Y. T., et al. (2011). Nitrogen deposition and forest nitrogen cycling along an urban-rural transect in southern China. Global Change Biology, 17, 872–885. https://doi.org/10.1111/j.1365-2486.2010.02283.x
Farren, N. J., Davison, J., Rose, R. A., Wagner, R. L., & Carslaw, D. C. (2020). Underestimated ammonia emissions from road vehicles. Environmental Science & Technology, 54, 15689–15697.
Felix, J. D., Berner, A., Wetherbee, G. A., Murphy, S. F., & Heindel, R. C. (2023). Nitrogen isotopes indicate vehicle emissions and biomass burning dominate ambient ammonia across Colorado’s Front Range urban corridor. Environmental Pollution, 316, 120537.
Fenn, M. E., & Bytnerowicz, A. (1993). Dry deposition of nitrogen and sulfur to ponderosa and Jeffrey pine in the San Bernardino National Forest in southern California. Environmental Pollution, 81, 277–285.
Fenn, M. E., & Poth, M. A. (2004). Monitoring nitrogen deposition in throughfall using ion exchange resin columns. Journal of Environmental Quality, 33, 2007–2014.
Fenn, M. E., et al. (2018b). On-road emissions of ammonia: An underappreciated source of atmospheric nitrogen deposition. Science of the Total Environment, 625, 909–919.
Fenn ME, Blubaugh T, Alexander D, & Jones D. (2016). Second Gen IER methods. USDA Forest Service. Available at: https://www.fs.usda.gov/psw/topics/air_quality/resin_collectors/fenn_iermethods.pdf. Accessed Nov 2022.
Fenn ME, Bytnerowicz A, & Schilling SL. (2018a). Passive monitoring techniques for evaluating atmospheric ozone and nitrogen exposure and deposition to california ecosystems. USDA Forest Service. Available at: https://permanent.access.gpo.gov/gpo92863/psw_gtr257.pdf. Accessed Nov 2022.
Gadsdon, S. R., & Power, S. A. (2009). Quantifying local traffic contributions to NO2 and NH3 concentrations in natural habitats. Environmental Pollution, 157, 2845–2852.
Galloway, J. N., Aber, J. D., Erisman, J. W., Seitzinger, S. P., Howarth, R. W., Cowling, E. B., & Cosby, B. J. (2003). The nitrogen cascade. BioScience, 53, 341–341. https://doi.org/10.1641/0006-3568(2003)053[0341:TNC]2.0.CO;2
García-Gomez, H., et al. (2016). Atmospheric deposition of inorganic nitrogen in Spanish forests of Quercus ilex measured with ion-exchange resins and conventional collectors. Environmental Pollution, 216, 653–661.
Guerrieri, R., Vanguelova, E. I., Michalski, G., Heaton, T. H., & Mencuccini, M. (2015). Isotopic evidence for the occurrence of biological nitrification and nitrogen deposition processing in forest canopies. Global Change Biology, 21, 4613–4626.
Guerrieri, R., et al. (2020). Partitioning between atmospheric deposition and canopy microbial nitrification into throughfall nitrate fluxes in a Mediterranean forest. Journal of Ecology, 108, 626–640.
Hanawalt, R. B. (1969). Environmental factors influencing the sorption of atmospheric ammonia by soils. Soil Science Society of America Journal, 33, 231–234.
Harrison A, Schulze E-D, Gebauer G, & Bruckner G. (2000). Canopy uptake and utilization of atmospheric pollutant nitrogen. In E. D. Schulze (Ed.), Carbon and nitrogen cycling in European forest ecosystems. Ecological Studies (vol. 142). Berlin, Heidelberg: Springer. https://doi.org/10.1007/978-3-642-57219-7_8
Hasselrot, B., & Grennfelt, P. (1987). Deposition of air pollutants in a wind-exposed forest edge. Water, Air, and Soil Pollution, 34, 135–143.
Heindel RC, Murphy SF, Repert DA, Wetherbee GA, Liethen AE, Clow DW, & Halamka TA. (2022). Elevated Nitrogen Deposition to Fire‐Prone Forests Adjacent to Urban and Agricultural Areas, Colorado Front Range, USA. Earth's Future: e2021EF002373.
Hoffman, A. S., Albeke, S. E., McMurray, J. A., Evans, R. D., & Williams, D. G. (2019). Nitrogen deposition sources and patterns in the Greater Yellowstone Ecosystem determined from ion exchange resin collectors, lichens, and isotopes. Science of the Total Environment, 683, 709–718.
Huang, J., Zhang, W., Zhu, X., Gilliam, F. S., Chen, H., Lu, X., & Mo, J. (2015). Urbanization in China changes the composition and main sources of wet inorganic nitrogen deposition. Environmental Science and Pollution Research, 22, 6526–6534.
Huber, C., Oberhauser, A., & Kreutzer, K. (2002). Deposition of ammonia to the forest floor under spruce and beech at the Höglwald site. Plant and Soil, 240, 3–11.
IRMA. (2022). NPS Stats: National Park Service Visitor Use Statistics. Available at: https://irma.nps.gov/STATS/Reports/Park/ROMO. Accessed Nov 2022.
Jacob, D. J. (1999). Introduction to atmospheric chemistry. Princeton University Press.
Jovan, S., et al. (2021). Challenges characterizing N deposition to high elevation protected areas: A case study integrating instrument, simulated, and lichen inventory datasets for the Devils Postpile National Monument and surrounding region, USA. Ecological Indicators, 122, 107311.
Kenkel, J. A., Sisk, T. D., Hultine, K. R., Sesnie, S. E., Bowker, M. A., & Johnson, N. C. (2016). Indicators of vehicular emission inputs into semi-arid roadside ecosystems. Journal of Arid Environments, 134, 150–159.
Langford, A., & Fehsenfeld, F. (1992). Natural vegetation as a source or sink for atmospheric ammonia: A case study. Science, 255, 581–583.
Lenth, R. (2020). emmeans: Estimated Marginal Means, aka Least-Squares Means. R package version 1.5.1. https://CRAN.R-project.org/package=emmeans. Accessed Nov 2022.
Li, X., et al. (2021). Canopy and understory nitrogen addition have different effects on fine root dynamics in a temperate forest: Implications for soil carbon storage. New Phytologist, 231, 4.
Liu, X.-Y., et al. (2017). Stable isotope analyses of precipitation nitrogen sources in Guiyang, southwestern China. Environmental Pollution, 230, 486–494.
Lu, M., Zhou, X., Luo, Y., Yang, Y., Fang, C., Chen, J., & Li, B. (2011). Minor stimulation of soil carbon storage by nitrogen addition: A meta-analysis. Agriculture, Ecosystems and Environment., 140, 234–244. https://doi.org/10.1016/j.agee.2010.12.010
Mast, M. A., Clow, D. W., Baron, J. S., & Wetherbee, G. A. (2014). Links between N deposition and nitrate export from a high-elevation watershed in the Colorado Front Range. Environmental Science & Technology, 48, 14258–14265.
McDonald BC, Dallmann TR, Martin EW, & Harley RA. (2012). Long‐term trends in nitrogen oxide emissions from motor vehicles at national, state, and air basin scales. Journal of Geophysical Research: Atmospheres, 117, D21. https://doi.org/10.1029/2012JD018304
Nanus, L., Campbell, D. H., Lehmann, C. M., & Mast, M. A. (2018). Spatial and temporal variation in sources of atmospheric nitrogen deposition in the Rocky Mountains using nitrogen isotopes. Atmospheric Environment, 176, 110–119.
National Atmospheric Deposition Program (NADP). (1987) NADP/NTN Annual Data Summary: Precipitation Chemistry in the United States. 1986. Natural Resource Ecology Laboratory, Colorado State University, Fort Collins, CO.
National Park Service (NPS). (2022). Most famous national parks set visitation records in 2021. Available at: https://www.nps.gov/orgs/1207/most-famous-national-parks-set-visitation-records-in-2021.htm. Accessed Nov 2022.
Papen, H., Geβler, A., Zumbusch, E., & Rennenberg, H. (2002). Chemolithoautotrophic nitrifiers in the phyllosphere of a spruce ecosystem receiving high atmospheric nitrogen input. Current Microbiology, 44, 56–60.
Patterson, K. (2019). Record Visitation At Rocky Mountain National Park In 2018. National Park Service.
R Core Team. (2019). R: A language and environment for statistical computing. R Foundation for Statistical Computing. https://www.R-project.org/
Redling, K., Elliott, E., Bain, D., & Sherwell, J. (2013). Highway contributions to reactive nitrogen deposition: Tracing the fate of vehicular NOxusing stable isotopes and plant biomonitors. Biogeochemistry, 116, 261–274. https://doi.org/10.1007/s10533-013-9857-x
Rocci, K. S., Fonte, S. J., von Fischer, J. C., & Cotrufo, M. F. (2019). Nitrogen dynamics in an established alfalfa field under low biochar application rates. Soil Systems, 3, 77.
Rueth, H. M., & Baron, J. S. (2002). Differences in Englemann spruce forest biogeochemistry east and west of the Continental Divide in Colorado, USA. Ecosystems, 5, 45–57.
Schwede, D. B., & Lear, G. G. (2014). A novel hybrid approach for estimating total deposition in the United States. Atmospheric Environment, 92, 207–220.
Sparks, J. P. (2009). Ecological ramifications of the direct foliar uptake of nitrogen. Oecologia, 159, 1–13.
Thompson, T. M., et al. (2015). Rocky Mountain National Park reduced nitrogen source apportionment. Journal of Geophysical Research: Atmospheres, 120, 4370–4384.
Tulloss, E. M., & Cadenasso, M. L. (2015). Nitrogen deposition across scales: Hotspots and gradients in a California savanna landscape. Ecosphere, 6, 1–12.
United States Department of Agriculture (USDA) (2022). Bear Lake SNOTEL site. Available at: https://wcc.sc.egov.usda.gov/nwcc/site?sitenum=322. Accessed Nov 2022.
Vogt JT, & Smith WB. (2017). Forest Inventory and Analysis Fiscal Year 2016 Business Report. United States Forest Service. Available at: https://www.fs.usda.gov/sites/default/files/fs_media/fs_document/publication-15817-usda-forest-service-fia-annual-report-508.pdf. Accessed Nov 2022.
Weathers, K. C., Lovett, G., Likens, G., & Lathrop, R. (2000). The effect of landscape features on deposition to Hunter Mountain, Catskill Mountains, New York. Ecological Applications, 10, 528–540.
Weathers, K. C., Simkin, S. M., Lovett, G. M., & Lindberg, S. E. (2006). Empirical modeling of atmospheric deposition in mountainous landscapes. Ecological Applications, 16, 1590–1607.
Wetherbee, G. A., Benedict, K. B., Murphy, S. F., & Elliott, E. M. (2019). Inorganic nitrogen wet deposition gradients in the Denver-Boulder metropolitan area and Colorado Front Range-Preliminary implications for Rocky Mountain National Park and interpolated deposition maps. Science of the Total Environment, 691, 1027–1042.
Wickham, H. (2016). ggplot2: Elegant Graphics for Data Analysis. Springer-Verlag.
Xu, S., Chen, M., Feng, T., Zhan, L., Zhou, L., & Yu, G. (2021). Use ggbreak to effectively utilize plotting space to deal with large datasets and outliers. Frontiers in Genetics, 12, 774846. https://doi.org/10.3389/fgene.2021.774846
Yue, K., Peng, Y., Peng, C., Yang, W., Peng, X., & Wu, F. (2016). Stimulation of terrestrial ecosystem carbon storage by nitrogen addition: A meta-analysis. Scientific Reports, 6, 19895. https://doi.org/10.1038/srep19895
Zhang, Q., et al. (2021). Atmospheric nitrogen deposition: A review of quantification methods and its spatial pattern derived from the global monitoring networks. Ecotoxicology and Environmental Safety, 216, 112180.
Zuur, A. F., Ieno, E. N., & Elphick, C. S. (2010). A protocol for data exploration to avoid common statistical problems. Methods in Ecology and Evolution, 1, 3–14.
Acknowledgements
We thank Rebecca Even, Kaydee Barker, Leland Dorchester, Amy Rocci, Tim Weinmann, and Caitlin Charlton for their assistance in the field. We also thank Scott Esser and Lisa Baron at Rocky Mountain National Park for their assistance in facilitating this research. This research was conducted under permit numbers: ROMO-2021-SCI-0013 & ROMO-2021-SCI-0019. This material is based upon work supported by the National Science Foundation Graduate Research Fellowship Program and a small grant from the Colorado State University Graduate Degree Program in Ecology, both awarded to K. S. Rocci.
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All authors contributed to the study conception and design. Material preparation, data collection and analysis were performed by Katherine Rocci. The first draft of the manuscript was written by Katherine Rocci and all authors commented on previous versions of the manuscript. All authors read and approved the final manuscript.
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Rocci, K.S., Cotrufo, M.F. & Baron, J.S. Proximity to Roads Does Not Modify Inorganic Nitrogen Deposition in a Topographically Complex, High Traffic, Subalpine Forest. Water Air Soil Pollut 234, 761 (2023). https://doi.org/10.1007/s11270-023-06762-2
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DOI: https://doi.org/10.1007/s11270-023-06762-2