Summertime Soil-Atmosphere Ammonia Exchange in the Colorado Rocky Mountain Front Range Pine Forest

Understanding the NH<sub>3</sub> exchange between forest ecosystems and the atmosphere is important due to its role in the nitrogen cycle. However, NH<sub>3</sub> exchange is dynamic and difficult to measure. The goal of this study was to characterize this exchange by measuri...

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Main Authors: Amy Hrdina, Alexander Moravek, Heather Schwartz-Narbonne, Jennifer Murphy
Format: Article
Language:English
Published: MDPI AG 2019-02-01
Series:Soil Systems
Subjects:
Online Access:https://www.mdpi.com/2571-8789/3/1/15
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author Amy Hrdina
Alexander Moravek
Heather Schwartz-Narbonne
Jennifer Murphy
author_facet Amy Hrdina
Alexander Moravek
Heather Schwartz-Narbonne
Jennifer Murphy
author_sort Amy Hrdina
collection DOAJ
description Understanding the NH<sub>3</sub> exchange between forest ecosystems and the atmosphere is important due to its role in the nitrogen cycle. However, NH<sub>3</sub> exchange is dynamic and difficult to measure. The goal of this study was to characterize this exchange by measuring the atmosphere, soil, and vegetation. Compensation point modeling was used to evaluate the direction and magnitude of surface-atmosphere exchange. Measurements were performed at the Manitou Experimental Forest Observatory (MEFO) site in the Colorado Front Range by continuous online monitoring of gas and particle phase NH<sub>3</sub>-NH<sub>4</sub><sup>+</sup> with an ambient ion monitoring system coupled with ion chromatographs (AIM-IC), direct measurements of [NH<sub>4</sub><sup>+</sup>] and pH in soil extracts to determine ground emission potential (&#915;<sub>g</sub>), and measurements of [NH<sub>4</sub><sup>+</sup>]<sub>bulk</sub> in pine needles to derive leaf emission potential (&#915;<sub>st</sub>). Two different soil types were measured multiple times throughout the study, in which &#915;<sub>g</sub> ranged from 5 to 2122. &#915;<sub>st</sub> values ranged from 29 to 54. Inferred fluxes (F<sub>g</sub>) from each soil type predicted intervals of emission and deposition. By accounting for the total [NH<sub>4</sub><sup>+</sup>] pool in each compartment, the lifetime of NH<sub>3</sub> with respect to the surface-atmosphere exchange in the soil is on the order of years compared to much faster naturally occurring processes, i.e., mineralization and nitrification.
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spelling doaj.art-8c7563a0cf1d4cd5949f308efc51a3b82022-12-22T01:55:58ZengMDPI AGSoil Systems2571-87892019-02-01311510.3390/soilsystems3010015soilsystems3010015Summertime Soil-Atmosphere Ammonia Exchange in the Colorado Rocky Mountain Front Range Pine ForestAmy Hrdina0Alexander Moravek1Heather Schwartz-Narbonne2Jennifer Murphy3Department of Chemistry, University of Toronto, 80 St. George Street, Toronto, ON M5S 3H6, CanadaDepartment of Chemistry, University of Toronto, 80 St. George Street, Toronto, ON M5S 3H6, CanadaDepartment of Chemistry, University of Toronto, 80 St. George Street, Toronto, ON M5S 3H6, CanadaDepartment of Chemistry, University of Toronto, 80 St. George Street, Toronto, ON M5S 3H6, CanadaUnderstanding the NH<sub>3</sub> exchange between forest ecosystems and the atmosphere is important due to its role in the nitrogen cycle. However, NH<sub>3</sub> exchange is dynamic and difficult to measure. The goal of this study was to characterize this exchange by measuring the atmosphere, soil, and vegetation. Compensation point modeling was used to evaluate the direction and magnitude of surface-atmosphere exchange. Measurements were performed at the Manitou Experimental Forest Observatory (MEFO) site in the Colorado Front Range by continuous online monitoring of gas and particle phase NH<sub>3</sub>-NH<sub>4</sub><sup>+</sup> with an ambient ion monitoring system coupled with ion chromatographs (AIM-IC), direct measurements of [NH<sub>4</sub><sup>+</sup>] and pH in soil extracts to determine ground emission potential (&#915;<sub>g</sub>), and measurements of [NH<sub>4</sub><sup>+</sup>]<sub>bulk</sub> in pine needles to derive leaf emission potential (&#915;<sub>st</sub>). Two different soil types were measured multiple times throughout the study, in which &#915;<sub>g</sub> ranged from 5 to 2122. &#915;<sub>st</sub> values ranged from 29 to 54. Inferred fluxes (F<sub>g</sub>) from each soil type predicted intervals of emission and deposition. By accounting for the total [NH<sub>4</sub><sup>+</sup>] pool in each compartment, the lifetime of NH<sub>3</sub> with respect to the surface-atmosphere exchange in the soil is on the order of years compared to much faster naturally occurring processes, i.e., mineralization and nitrification.https://www.mdpi.com/2571-8789/3/1/15ammoniasoil fluxsoil-atmosphere interactionsammonia lifetime
spellingShingle Amy Hrdina
Alexander Moravek
Heather Schwartz-Narbonne
Jennifer Murphy
Summertime Soil-Atmosphere Ammonia Exchange in the Colorado Rocky Mountain Front Range Pine Forest
Soil Systems
ammonia
soil flux
soil-atmosphere interactions
ammonia lifetime
title Summertime Soil-Atmosphere Ammonia Exchange in the Colorado Rocky Mountain Front Range Pine Forest
title_full Summertime Soil-Atmosphere Ammonia Exchange in the Colorado Rocky Mountain Front Range Pine Forest
title_fullStr Summertime Soil-Atmosphere Ammonia Exchange in the Colorado Rocky Mountain Front Range Pine Forest
title_full_unstemmed Summertime Soil-Atmosphere Ammonia Exchange in the Colorado Rocky Mountain Front Range Pine Forest
title_short Summertime Soil-Atmosphere Ammonia Exchange in the Colorado Rocky Mountain Front Range Pine Forest
title_sort summertime soil atmosphere ammonia exchange in the colorado rocky mountain front range pine forest
topic ammonia
soil flux
soil-atmosphere interactions
ammonia lifetime
url https://www.mdpi.com/2571-8789/3/1/15
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AT heatherschwartznarbonne summertimesoilatmosphereammoniaexchangeinthecoloradorockymountainfrontrangepineforest
AT jennifermurphy summertimesoilatmosphereammoniaexchangeinthecoloradorockymountainfrontrangepineforest