Abstract

Abstract. Atmospheric sulfur deposition above certain limits can represent a threat to tropical forests, causing nutrient imbalances and mobilizing toxic elements that impact biodiversity and forest productivity. Atmospheric sources of sulfur deposited by precipitation have been roughly identified in only a few lowland tropical forests. Even scarcer are studies of this type in tropical mountain forests, many of them mega-diversity hotspots and especially vulnerable to acidic deposition. In these places, the topographic complexity and related streamflow conditions affect the origin, type, and intensity of deposition. Furthermore, in regions with a variety of natural and anthropogenic sulfur sources, like active volcanoes and biomass burning, no source emission data has been used for determining the contribution of each source to the deposition. The main goal of the current study is to evaluate sulfate (SO4- deposition by rain and occult precipitation at two topographic locations in a tropical mountain forest of southern Ecuador, and to trace back the deposition to possible emission sources applying back-trajectory modeling. To link upwind natural (volcanic) and anthropogenic (urban/industrial and biomass-burning) sulfur emissions and observed sulfate deposition, we employed state-of-the-art inventory and satellite data, including volcanic passive degassing as well. We conclude that biomass-burning sources generally dominate sulfate deposition at the evaluated sites. Minor sulfate transport occurs during the shifting of the predominant winds to the north and west. Occult precipitation sulfate deposition and likely rain sulfate deposition are mainly linked to biomass-burning emissions from the Amazon lowlands. Volcanic and anthropogenic emissions from the north and west contribute to occult precipitation sulfate deposition at the mountain crest Cerro del Consuelo meteorological station and to rain-deposited sulfate at the upriver mountain pass El Tiro meteorological station.

Highlights

  • Sulfur enters the atmosphere principally as sulfur dioxide (SO2), an air pollutant with a lifetime of about 1 to 2 days, before it is normally deposited or oxidized into sulfate (SO−4 )

  • Conductivity is a proxy of ion concentrations in water and high conductivity values coincide with episodes of rain and Occult precipitation (OP) water droplets with high ion loads

  • We concerned ourselves with the identification of important natural and anthropogenic sources contributing to atmospheric sulfate deposition in the tropical mountain forests of southeastern Ecuador

Read more

Summary

Introduction

Sulfur enters the atmosphere principally as sulfur dioxide (SO2), an air pollutant with a lifetime of about 1 to 2 days, before it is normally deposited or oxidized into sulfate (SO−4 ). Sulfate decreases the pH of precipitation to levels that represent a threat to health and ecosystems. This phenomenon called “acid rain” has been discussed in the past, in the industrialized countries of Europe and North America where adverse effects were found to be more serious for health than for ecosystems (Menz and Seip, 2004). Acidification of soil due to persistent increases in sulfate inputs could lead to nutrient imbalances and changes in ecosystem diversity and productivity (Greaver et al, 2012; Phoenix et al, 2006). It can mobilize many potentially toxic elements that promote soil degradation and erosion

Objectives
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