TABLE 3.
Habitat | Sample no. or type | No of copies of P. stutzeri nirS DNA/μg of community DNAf
|
P. stutzeri nirS DNA (μg/g of community DNA)f
|
||
---|---|---|---|---|---|
Mean | Upper 95% CI | Mean | Upper 95% CI | ||
Soila | |||||
KBS (Mich.) | 0× | 1.0 × 102 | 4.4 × 10−4 | ||
1× | BDLg | BDL | |||
10× | BDL | BDL | |||
100× | BDL | BDL | |||
Groundwater | |||||
Schoolcraft bioremediation site (Mich.)b | M8 | BDL | BDL | ||
M11 | 1.1 × 1011 | 4.8 × 105 | |||
M19 | 2.0 × 107 | 89 | |||
Shiprock UMTRAc site (N. Mex.) | 425 | 1.9 × 103 | 3.7 × 103 | 8.4 × 10−3 | 1.6 × 10−2 |
602 | 3.1 × 105 | 8.8 × 104 | 1.4 | 3.9 × 10−1 | |
603 | 2.2 × 105 | 2.1 × 104 | 9.7 × 10−1 | 9.3 × 10−2 | |
619 | 2.0 × 107 | 9.4 × 105 | 90 | 4.1 | |
813 | 5.0 × 106 | 4.5 × 105 | 22 | 2 | |
826 | 5.0 × 105 | 1.6 × 105 | 2.2 | 6.9 × 10−1 | |
Freshwater sedimentd | |||||
Wintergreen Lake (Mich.) | 2.2 × 106 | 3.1 × 105 | 9.7 | 1.3 | |
Marine sedimente | |||||
Pacific Ocean (Wash.) | 0–0.5 cm | BDL | BDL | ||
0.5–1 cm | BDL | BDL | |||
1–2 cm | 1.0 × 102 | 2.0 × 102 | 4.4 × 10−4 | 8.8 × 10−4 | |
2–3 cm | BDL | BDL | |||
3–5 cm | BDL | BDL | |||
5–10 cm | BDL | BDL | |||
Puget Sound (Wash.) | 1–1.5 cm | BDL | BDL | ||
1.5–2 cm | 2.1 × 104 | 2.4 × 103 | 9.1 × 10−2 | 1.0 × 10−2 | |
6–6.5 cm | 7.0 × 102 | 2.0 × 102 | 3.1 × 10−3 | 8.8 × 10−4 |
Soils were treated with 0, 1, 10, and 100× the normal field rate (1.1 kg ha−1) of the herbicide 2, 4-dichlorophenoxyacetate (1).
Samples were collected 2 m upstream (M8), 1 m downstream (M11), and 2.5 m downstream (M19) from the well where P. stutzeri KC was injected (21).
UMTRA, uranium mill tailings remedial action.
The surface 2 cm containing the active denitrifiers was analyzed.
Depths within the sediment core are reported.
Results are from triplicate samples when 95% confidence interval (CI) is indicated and from single samples, otherwise.
BDL, below detection limit.