Temporal Trends of Phosphorus Cycling in a Tropical Montane Forest in Ecuador During 14 Years

Publikation: Beitrag in FachzeitschriftArtikelForschungPeer-Review

Autoren

  • Wolfgang Wilcke
  • Andre Velescu
  • Sophia Leimer
  • Moritz Bigalke
  • Jens Boy
  • Carlos Valarezo

Organisationseinheiten

Externe Organisationen

  • Karlsruher Institut für Technologie (KIT)
  • University of Bern
  • Universidad Nacional de Loja
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Details

OriginalspracheEnglisch
Seiten (von - bis)1370-1386
Seitenumfang17
FachzeitschriftJournal of Geophysical Research: Biogeosciences
Jahrgang124
Ausgabenummer5
PublikationsstatusVeröffentlicht - 30 Mai 2019

Abstract

Increased bioavailability of P can have a negative impact on plant biodiversity. In an approximately 9-ha catchment under N + P-limited megadiverse tropical montane forest in Ecuador, we budgeted all major P fluxes and determined whether the P fluxes changed from 1999 to 2013. Furthermore, we assessed which external drivers (rainfall, total P and acid deposition) caused this potential change. Mean (±SD) annual P deposition (bulk+dry) was 240 ± 270 mg/m 2, with the SD reflecting the interannual variation. The annual P flux to the soil via throughfall+stemflow+litterfall was 1,400 ± 170 mg/m 2 of which 18 ± 9.2% was leached to below the organic layer. The mineral soil retained 80 ± 12% of the P leached from the organic layer. The mean annual P weathering rate was 79 ± 63 mg/m 2. The sum of P fluxes was approximately 5 times larger above than below the mineral soil surface, illustrating that P was tightly cycled in the biological part of the forest. The mean annual canopy budget was negative (−120 ± 280 mg/m 2); that is, P was leached from the canopy. Throughfall was the largest source of dissolved P. The P catchment budget (total deposition-streamflow) was positive (200 ± 270 mg/m 2); that is, P was retained, mainly in the soil organic layer. From 1999 to 2013, P fluxes with throughfall, stemflow, and streamflow increased significantly. The strongest driver of the P budgets of the canopy and the catchment was total P deposition. Our results demonstrate that mainly biological processes retained deposited P in the vegetation and the organic layer enhancing the internal P cycle.

ASJC Scopus Sachgebiete

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Temporal Trends of Phosphorus Cycling in a Tropical Montane Forest in Ecuador During 14 Years. / Wilcke, Wolfgang; Velescu, Andre; Leimer, Sophia et al.
in: Journal of Geophysical Research: Biogeosciences, Jahrgang 124, Nr. 5, 30.05.2019, S. 1370-1386.

Publikation: Beitrag in FachzeitschriftArtikelForschungPeer-Review

Wilcke W, Velescu A, Leimer S, Bigalke M, Boy J, Valarezo C. Temporal Trends of Phosphorus Cycling in a Tropical Montane Forest in Ecuador During 14 Years. Journal of Geophysical Research: Biogeosciences. 2019 Mai 30;124(5):1370-1386. doi: 10.1029/2018jg004942
Wilcke, Wolfgang ; Velescu, Andre ; Leimer, Sophia et al. / Temporal Trends of Phosphorus Cycling in a Tropical Montane Forest in Ecuador During 14 Years. in: Journal of Geophysical Research: Biogeosciences. 2019 ; Jahrgang 124, Nr. 5. S. 1370-1386.
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title = "Temporal Trends of Phosphorus Cycling in a Tropical Montane Forest in Ecuador During 14 Years",
abstract = "Increased bioavailability of P can have a negative impact on plant biodiversity. In an approximately 9-ha catchment under N + P-limited megadiverse tropical montane forest in Ecuador, we budgeted all major P fluxes and determined whether the P fluxes changed from 1999 to 2013. Furthermore, we assessed which external drivers (rainfall, total P and acid deposition) caused this potential change. Mean (±SD) annual P deposition (bulk+dry) was 240 ± 270 mg/m 2, with the SD reflecting the interannual variation. The annual P flux to the soil via throughfall+stemflow+litterfall was 1,400 ± 170 mg/m 2 of which 18 ± 9.2% was leached to below the organic layer. The mineral soil retained 80 ± 12% of the P leached from the organic layer. The mean annual P weathering rate was 79 ± 63 mg/m 2. The sum of P fluxes was approximately 5 times larger above than below the mineral soil surface, illustrating that P was tightly cycled in the biological part of the forest. The mean annual canopy budget was negative (−120 ± 280 mg/m 2); that is, P was leached from the canopy. Throughfall was the largest source of dissolved P. The P catchment budget (total deposition-streamflow) was positive (200 ± 270 mg/m 2); that is, P was retained, mainly in the soil organic layer. From 1999 to 2013, P fluxes with throughfall, stemflow, and streamflow increased significantly. The strongest driver of the P budgets of the canopy and the catchment was total P deposition. Our results demonstrate that mainly biological processes retained deposited P in the vegetation and the organic layer enhancing the internal P cycle. ",
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author = "Wolfgang Wilcke and Andre Velescu and Sophia Leimer and Moritz Bigalke and Jens Boy and Carlos Valarezo",
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T1 - Temporal Trends of Phosphorus Cycling in a Tropical Montane Forest in Ecuador During 14 Years

AU - Wilcke, Wolfgang

AU - Velescu, Andre

AU - Leimer, Sophia

AU - Bigalke, Moritz

AU - Boy, Jens

AU - Valarezo, Carlos

N1 - Funding information: We thank E. Beck, K. Müller? Hohenstein, M. Richter, and W. Zech for coinitiating the long?term study; K. Fleischbein, R. Goller, M. Meyer? Grünefeldt, M. Sequeira, H. Wullaert, S. Yasin, and numerous undergraduate students for data acquisition during parts of the observation period; W. Schädler for providing RFA data of rock macro element concentrations; the Ecuadorian Environmental Ministry for the research permits; and Naturaleza y Cultura Internacional (NCI) in Loja for providing the study area and the research station and the Deutsche Forschungsgemeinschaft (DFG) for funding (FOR402 and FOR816). The original data are included in the supporting information.

PY - 2019/5/30

Y1 - 2019/5/30

N2 - Increased bioavailability of P can have a negative impact on plant biodiversity. In an approximately 9-ha catchment under N + P-limited megadiverse tropical montane forest in Ecuador, we budgeted all major P fluxes and determined whether the P fluxes changed from 1999 to 2013. Furthermore, we assessed which external drivers (rainfall, total P and acid deposition) caused this potential change. Mean (±SD) annual P deposition (bulk+dry) was 240 ± 270 mg/m 2, with the SD reflecting the interannual variation. The annual P flux to the soil via throughfall+stemflow+litterfall was 1,400 ± 170 mg/m 2 of which 18 ± 9.2% was leached to below the organic layer. The mineral soil retained 80 ± 12% of the P leached from the organic layer. The mean annual P weathering rate was 79 ± 63 mg/m 2. The sum of P fluxes was approximately 5 times larger above than below the mineral soil surface, illustrating that P was tightly cycled in the biological part of the forest. The mean annual canopy budget was negative (−120 ± 280 mg/m 2); that is, P was leached from the canopy. Throughfall was the largest source of dissolved P. The P catchment budget (total deposition-streamflow) was positive (200 ± 270 mg/m 2); that is, P was retained, mainly in the soil organic layer. From 1999 to 2013, P fluxes with throughfall, stemflow, and streamflow increased significantly. The strongest driver of the P budgets of the canopy and the catchment was total P deposition. Our results demonstrate that mainly biological processes retained deposited P in the vegetation and the organic layer enhancing the internal P cycle.

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