TABLE 5 |.
Outcome | Factor | Change in Odds | 95% CIb | P-value |
---|---|---|---|---|
eaeA-stx Codetection | ||||
Bottom Substrate, Cobble or Larger (Absent = Reference) | 0.50 | 0.24, 1.05 | 0.068 | |
Developed Non-Open Space, IDW c % of Flood Plain | 0.92 | 0.85, 0.99 | 0.012 | |
Developed Non-Open Space, IDW % of Stream Corridor | 0.93 | 0.86, 1.00 | 0.036 | |
Developed Non-Open Space, IDW % of Total Watershed | 0.95 | 0.90, 1.00 | 0.034 | |
Developed Open Space, IDW % of Flood Plain | 0.95 | 0.91, 0.99 | 0.012 | |
Developed Open Space, IDW % of Stream Corridor | 0.95 | 0.91, 0.99 | 0.010 | |
Developed Open Space, IDW % of Total Watershed | 0.93 | 0.88, 0.99 | 0.018 | |
Ditch, Present Immediately Upstream of Site (Absent = Reference) | 2.17 | 1.02, 4.62 | 0.044 | |
Forest Wetland, IDW % of Flood Plain | 1.02 | 1.00, 1.04 | 0.022 | |
Forest Wetland, IDW % of Stream Corridor | 1.02 | 1.00, 1.05 | 0.038 | |
Open Water, IDW % of Flood Plain | 0.98 | 0.95, 1.00 | 0.043 | |
Open Water, IDW % of Stream Corridor | 0.90 | 0.81, 0.99 | 0.033 | |
Open Water, IDW % of Total Watershed | 0.83 | 0.69, 0.99 | 0.033 | |
Wastewater Discharge Sites, Upstream Density (per 10 km2) | 0.23 | 0.04, 1.30 | 0.096 | |
In-stream Waterbodies, Flow Path Distance to Nearest (km) | 1.10 | 1.01, 1.19 | 0.032 | |
In-stream Waterbodies, Present Upstream (Absent = Reference) | 2.04 | 0.96, 4.35 | 0.065 | |
Listeria species excluding L. monocytogenes | ||||
Bottom Substrate, Coarse Gravel (Absent = Reference) | 2.29 | 0.97, 5.41 | 0.059 | |
Bottom Substrate, Fine Gravel (Absent = Reference) | 2.12 | 0.87, 5.16 | 0.097 | |
Bottom Substrate, Organic Matter (Absent = Reference) | 0.42 | 0.16, 1.10 | 0.077 | |
Bottom Substrate, Sand (Absent = Reference) | 0.45 | 0.19, 1.04 | 0.062 | |
Campgrounds, Present Upstream (Absent = Reference) | 0.37 | 0.13, 1.11 | 0.076 | |
Dairy Operations, Flow Path Distance to Nearest (km) | 0.84 | 0.03. 0.73 | 0.027 | |
Dairy Operations, Present Upstream (Absent = Reference) | 0.26 | 0.75, 0.98 | 0.028 | |
Ditch, Present Immediately Upstream of Site (Absent = Reference) | 0.41 | 0.16, 1.05 | 0.064 | |
In-stream Waterbodies, Flow Path Distance to Nearest (km) | 0.86 | 0.75, 0.98 | 0.028 | |
Livestock Operation, Present Upstream (Absent = Reference) | 0.27 | 0.08, 0.93 | 0.039 | |
Pasture, IDW % of Flood Plain | 1.03 | 1.00, 1.07 | 0.070 | |
Pig Farms, Present Upstream (Absent = Reference) | 0.16 | 0.04, 0.69 | 0.014 | |
Pig Farms, Upstream Density (per 10 km2) | 0.00d | 0.00, 5.17 | 0.077 | |
Stables, Present Upstream (Absent = Reference) | 0.32 | 1.06, 1.67 | 0.018 | |
L. monocytogenes Isolation | ||||
Campgrounds, Upstream Density (per 10 km2) | 565.4e | 0.91, 3.50*105 | 0.053 | |
Developed Non-Open Space, 0–100m Upstream of Site (%) | 0.96 | 0.91, 1.01 | 0.086 | |
Salmonella Isolation | ||||
Bottom Substrate, Cobble or Larger (Absent = Reference) | 0.55 | 0.30, 1.01 | 0.054 | |
Campground, Flow Path Distance to Nearest (km) | 0.94 | 0.88, 1.01 | 0.068 | |
Dairy Operations, Upstream Density (per 10 km2) | 0.47 | 0.28, 0.81 | 0.007 | |
Pasture, 0–100m Upstream of Site (%) | 0.99 | 0.97, 1.00 | 0.053 | |
Developed Open Space, IDW % of Stream Corridor | 1.03 | 1.00, 1.06 | 0.096 | |
Ditch, Stormwater Outfalls Present Upstream (Absent = Reference) | 2.04 | 1.03, 4.05 | 0.042 | |
Poultry Operations, Flow Path Distance to Nearest (km) | 0.93 | 0.86, 1.00 | 0.060 |
Since this was a hypothesis-generating study, two thresholds were used for interpreting the results of the GLMMs. Specifically, P< 0.05 indicated that likelihood of microbial target detection and the factor were significantly associated, while a 0.05 ≤P<0.10 indicated the presence of a potential relationship that warrants investigation in future studies.
CI, Confidence interval.
IDW, Inverse distance weighted.
The odds ratio was >0.000 but <0.001.
This confidence interval is wide due to sparse data bias, which is a product of the low prevalence of L. monocytogenes (10%; 20/196) and of watersheds with campgrounds upstream of the sampling site (22%; 16/71); 54% of L. monocytogenes-positive samples were collected from watersheds with campgrounds upstream.