B. Kilb et al., Community structures of different groundwater habitats investigated using methods of molecular biology, ACT HYDR HY, 26(6), 1998, pp. 349-354
The degradation of pollutants in groundwater and aquifers depends on microb
iological and hydrogeochemical processes. To understand the transport and f
ate of anthropogenic compounds during bank filtration and artificial rechar
ge of groundwater it is necessary to gain more information about the struct
ure of microbial populations in these systems. The population structure of
aerobic, anaerobic groundwater habitats and of water samples during artific
ial groundwater recharge was examined by 16S rDNA based analysis. Water and
sediment samples were collected from a groundwater catchment area with art
ificial groundwater recharge near the river Ruhr in NW-Germany.
16S rRNA genes of mixed bacterial DNA from different samples were amplified
by PCR (polymerase chain reaction) with eubacterial primer sequences. To r
eveal eubacterial population structure amplified PCR-products were separate
d by DGGE (denaturing gradient gel electrophoresis) on the basis of melting
domain structure and nucleotide composition. DGGE patterns of groundwater
enrichment cultures and groundwater samples were compared to demonstrate di
fferences between the use of cultivation dependent and molecularbiological
approaches. The DGGE pattern of groundwater is very complex and differs sig
nificantly from DGGE patterns of groundwater enrichment cultures characteri
zed by a small number of distinct bands. This shows the small quantity of c
ulturable microorganism in groundwater ecosystems. Aerobic and anaerobic gr
oundwater and sediment samples differ markedly in their DGGE profiles. Diff
erent hydrogeochemical zones of this groundwater catchment area are mirrowe
d by distinct DGGE patterns indicating changes in microbial community struc
ture. Analysis of bacterial population structure in the course of artificia
l groundwater recharge shows identical DGGE patterns comparing surface wate
r samples to samples taken before gravel prefiltration and before sand filt
ration. In contrast the DGGE pattern of artificial recharged groundwater di
ffers markedly, indicating significant changes in microbial population duri
ng underground passage.