The nitrogen and sulfur status and isotopes of soils within the vicinity of a coal-fired power station in South Africa
Date
2013-05-02
Authors
Angelova, Mia
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Abstract
Amplified loads of sulfate and nitrate have caused increased stress on soil systems in many areas
of the world, as both are dominant components of acid rain. This is a critical environmental stress due
to the damage caused to soil, water quality and ecosystem functioning. Issues concerning the rising
emissions of these elements from local industries have begun to attract increasing attention in South
Africa, as the rates of deposition in the Mpumalanga Highveld region alone is comparable to those
experienced in First World countries. This study sought to investigate the use of natural stable isotopes
of sulfur and nitrogen to identify the process transformations that these species undergo in
environmental cycles. Total δ34S, δ15N and δ13C isotope signature of soils in the Mpumalanga region
were combined with total elemental concentrations to determine the effect of deposition on the soil
system. Soil samples from two soil depths (0 – 10 cm and 20 – 40 cm) were taken along a distance
gradient from an identified pollution source, the Majuba power station. Long-term air quality data
from the study area were also obtained from Eskom’s air quality monitoring stations, as well as sulfur
and nitrogen deposition data from selected literature.
Elemental concentrations decreased with soil depth as expected, while sites located
approximately 25 km downwind of the power station were seen to contain higher concentrations of
both soil sulfur and nitrogen. The mean per site soil sulfur concentration across all depths ranged from
0.009 % to 0.048 %, while the mean per site nitrogen concentration across all depths ranged
from 0.056 % to 0.346 %. The mean soil carbon concentration in the top-soils ranged from 0.97 % to
7.93 %, and decreased in the sub-soils to 0.490 % to 3.270 %.The mean δ34S value for the top-soils
was found to be 8.28 ‰ and increased to 10.78 ‰ in the sub-soils. Soil δ15N also increased with soil
depth from 6.55 ‰ to 8.28 ‰. Soil δ13C values were seen to increase from -12.83 ‰ in the top-soils to
-11.90 ‰ in the sub-soils. Lighter δ34S values at the surface may be due to anthropogenic deposition.
The positive δ34S shift was attributed to a two-source mixing model (atmospheric deposition and
bedrock) and isotopic fractionation processes that occur within the soil profile. The δ15N values of the
top-soil were higher than what is expected if all nitrogen was derived from atmospheric nitrogen gas
fixation. The increase in δ15N with depth suggested that isotope fractionation occurred during nitrogen
export due to the faster reaction rate of 14N compared to 15N. The soil δ13C values indicated a typical
C4 grassland system. New carbon at the top-soil depths was enriched in 13C due to the slower decay of
13C-depleted lignin; whereas in the sub-soils microbial recycling of carbon dominates and explained
the higher 13C content of the older carbon. The conceptual framework presented for this project
involves simultaneous processes of deposition and export in the soil system. This was particularly true
for sulfur, where sites with lower isotope values had lower soil sulfur concentrations and vice versa.
This indicates that high levels of deposition correspond to high net export. The sulfur and nitrogen
isotopic signatures could not be used to as a direct means of source identification; however, the
effectiveness of isotopes in elucidating transfer of these nutrients in the soil system was illustrated.
Description
A dissertation submitted to the Faculty of Science, University of Witwatersrand, in
fulfilment of the requirements for the degree of Masters of Science
Johannesburg, 2012.