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PNNL-13501 - Pacific Northwest National Laboratory

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triangular configuration. Once the tubes and shield are in<br />

place, liquid nitrogen is injected into the tubes for<br />

approximately 20 to 30 minutes (Figure 1, top).<br />

Immediately after the liquid is injected, a chain hoist is<br />

used to lift the frozen tear-drop-shaped core (Figure 1,<br />

bottom) from the bed of the river. This method is capable<br />

of extracting 70 cm cores that weigh, on average, about<br />

24 kg. Once the core is extracted, it is photographed,<br />

bagged, and placed on dry ice in a sample transport box<br />

for further processing and analysis at the laboratory.<br />

Figure 1. Filling hollow tubes with liquid N 2 to freeze river<br />

sediments in situ (top). Intact frozen core obtained from the<br />

Columbia River using the freeze core technique (bottom).<br />

Although the focus of this project is on the development<br />

and evaluation of approaches for collecting samples from<br />

the hyporheic zone, select microbiological and<br />

geochemical analyses were applied to the collected<br />

samples to assess the effectiveness of the methods<br />

described above and to gain preliminary insights into the<br />

characteristics of this environment. Frozen and unfrozen<br />

samples were analyzed using microbiological cultivation<br />

techniques and direct extraction and characterization of<br />

nucleic acids using methods that have been developed and<br />

employed by our <strong>Laboratory</strong> for analyses of microbial<br />

communities in subsurface sediments and soil. Pore<br />

waters were extracted from sediments by centrifugation<br />

and analyzed for total cations and anions, dissolved<br />

organic and inorganic carbon, and trace metals.<br />

Results and Accomplishments<br />

Freeze-Core Sampling<br />

Intact frozen cores of Columbia River sediment were<br />

successfully collected from near the 100 H area of the<br />

Hanford Site in March and again in May 2000. Three<br />

intact frozen blocks of sediment were removed on each<br />

occasion and treated as replicates. Unfrozen sediment<br />

was collected adjacent to the freeze core location and<br />

used as controls to assess the impact of freezing on viable<br />

microbial populations, metabolic activity, and on pore<br />

water geochemistry. Collected samples were returned to<br />

laboratories in the 331 Building. Freeze-cores remained<br />

frozen during transport and subsequent sampling.<br />

Microbiological Analyses<br />

Microbial characterization of Columbia River sediments<br />

revealed an unexpectedly large and diverse microbial<br />

community, whereas, previous experience with saturated<br />

subsurface sediments from the Hanford confined aquifer<br />

suggested the opposite. Direct community diversity<br />

analysis based on terminal restriction fragment<br />

polymorphism analyses of 16S ribosomal RNA genes<br />

showed between 10 and 15 major ribotypes, indicative of<br />

significant microbial diversity. Populations of viable<br />

aerobic heterotrophic bacteria in unfrozen sediment<br />

ranged from 10 6 to 10 7 colony-forming units per gram; in<br />

the frozen sediments, the populations were lower,<br />

between 10 5 to 10 6 colony-forming units g -1 (Figure 2).<br />

These results suggest that freezing does have an impact<br />

on bacterial cell viability, reducing populations by<br />

approximately 10-fold or less. Although the results<br />

shown in Figure 2 are from the May sampling, identical<br />

trends were also observed in the March samples.<br />

Log CFU g -1 dry sediment<br />

7<br />

6<br />

5<br />

4<br />

3<br />

2<br />

1<br />

0<br />

HA1 HA2 HA3 FC1 FC2 FC3<br />

Sample<br />

Medium<br />

10% PTYG<br />

FS R2A<br />

Dilute R2A<br />

Figure 2. Populations of viable aerobic heterotrophic<br />

bacteria in hyporheic ambient (HA) and freeze-core (FC)<br />

Columbia River sediments<br />

Earth System Science 201

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