Benthic bacterial secondary production measured via simultaneous H-3-thymidine and C-14-leucine incorporation, and its implication for the carbon cycle of a shallow macrophyte-dominated backwater system
Akt. Kirschner et B. Velimirov, Benthic bacterial secondary production measured via simultaneous H-3-thymidine and C-14-leucine incorporation, and its implication for the carbon cycle of a shallow macrophyte-dominated backwater system, LIMN OCEAN, 44(8), 1999, pp. 1871-1881
The role of the benthic bacterial community in the carbon cycle of a temper
ate, macrophyte-dominated oxbow was investigated in a 2-yr study from 1994
to 1996. Simultaneous incorporation of H-3-thymidine into DNA and C-14-leuc
ine into proteins was monitored as a tool for the measurement of bacterial
secondary production in the aerobic zone of the sediment along with bacteri
al numbers, morphotype composition, cell volumes, biomass, frequency of div
iding cells (FDC), and abiotic variables. Bacterial numbers ranged from 2.5
x 10(9) to 8.5 x 10(9) cells ml(-1), corresponding to bacterial biomass va
lues of 64 and 288 mu g C ml(-1), respectively. Both bacterial production m
ethods yielded similar and reliable results over the whole investigation pe
riod, varying between 42 and 2,350 mu g C L-1 h(-1) for the thymidine metho
d and between 67 and 2,490 mu g C L-1 h(-1) for the leucine method, and als
o corresponded well with the FDC values. Only during late spring and early
summer was the thymidine uptake uncoupled from leucine incorporation. Tempe
rature was found to be of significant importance for the variation of all b
acterial parameters. In addition carbon inputs from the water column were a
pparently crucial stimulators. of benthic bacterial growth. The spring phyt
oplankton bloom together with higher temperatures led to a strong positive
response of the bacterial community in the sediment. However, the planktoni
c algal production was not sufficient to cover the benthic bacterial C-dema
nd and, as derived from mass-balance calculations, decaying macrophytes of
the previous season seemed to provide the main energy source until the midd
le of spring. From the middle of August to the beginning of October, the pe
riod of maximal biomass of submerged macrophytes, all bacterial parameters
exhibited their annual maximum. The benthic bacterial community was depende
nt on leachates and decay products of the submerged vegetation during this
time. Temperature limitation was most probably the reason for the low bioma
ss and production values observed during autumn and winter.