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. 2001 Feb;67(2):760–768. doi: 10.1128/AEM.67.2.760-768.2001

TABLE 3.

P. stutzeri nirS gene abundance in various habitats as measured by real-time PCR

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.) 1.0 × 102 4.4 × 10−4
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
a

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). 

b

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). 

c

UMTRA, uranium mill tailings remedial action. 

d

The surface 2 cm containing the active denitrifiers was analyzed. 

e

Depths within the sediment core are reported. 

f

Results are from triplicate samples when 95% confidence interval (CI) is indicated and from single samples, otherwise. 

g

BDL, below detection limit.