| 5. MICROBIOLOGY AND BIOTECHNOLOGY
5.3
IMPACT OF AIRBORNE METAL POLLUTION ON MICROBIAL COMMUNITY STRUCTURE
IN CONIFEROUS SOIL
R. Maarit Niemi, Jukka Ahtiainen, Tarja Sarjakoski, Eija Schultz and
Pekka Vanhala
Finnish Environment Institute, Helsinki
The impact of airborne pollution on microorganisms and their activity
in boreal coniferous soil was measured in two areas in Southern Finland.
The Harjavalta site is characterized by pollution from a copper and nickel
smeltery emitting SO2, Cu, Ni, and Cd. The Koverhar area is contaminated
by an iron smeltery emitting SO2, NOx, Cd, Pb, Zn, Fe, As and chalc.
ATP content and soil respiration decreased towards the pollution source
in the Harjavalta gradient but were either not affected or increased in
the exposed site at Koverhar. The semiquantitative API Zym test kit was
used to assess enzyme activities. The activities were low in all samples
but tended to decrease due to the pollution in Harjavalta. Quantitative
enzyme activity measurements showed decreases in the activities in invertase,
xylanase, arylsulphatase and acid phoshatase when progressing
towards the pollution source in Harjavalta. When enzyme activities were
quatitatively measured in Koverhar area, dublicate composite samples showed
no differences in soil respiration between the exposed site and the control
site. ATP content was slightly decreased in the exposed site, but replicate
samles showed remarkable variation. Alkaline phosphatase and xylanase were
decreased but invertase and arylsulphatase were increased in the exposed
site compared with the control site. The levels of acid phosphatase were
similar in both sites.
In Harjavalta heavy metal pollution gradient, relative numbers of colony-forming
bacteria and fungi decreased as a function of pollution. However, in the
most heavily polluted site adaptation of bacterial and
fungal flora to heavy metals was demonstrated by cultivating heterotrophic
bacteria and fungi on agar media supplemented with heavy metals (Cu, Pb,
Zn, Ni) and by cultivating soil samples from different
sites in liquid R2A medium containing Cu, Ni and Zn in different combinations.
DNA was isolated from different sites in the Harjavalta gradient and
its 16S rDNA fragments amplified using Y1 (modified with GC-clamp) and
Y2 primers. Metal-resistant bacteria were isolated from the same sites
and their isolated DNA was amplified using the same primers. Amplicons
were separated with DGGE. DGGE revealed more bands of 16S rDNA fragments
in the control soil samples than in the exposed sites. Three clusters were
observed of nine heavy metal resistant bacterial isolates on the basis
of DGGE. However, these were not dominant among soil bacteria in exposed
area.

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