Table 2. One-Sided Paired t-Test Comparing Indoor and Outdoor PAH Air Concentrations before, during, and after Wildfires by Ring Sizea.
LMW PAHs |
HMW PAHs |
||||||
---|---|---|---|---|---|---|---|
location | 2-ring | 3-ring | 4-ring | 5-ring | 6-ring | wildfire average AQI | |
before wildfires indoorb | Alturas, CA | 0.99 | 0.90 | 0.10 | 0.10 | 0.10 | 70 |
Newport, OR | 0.34 | 0.99 | 0.83 | N/A (n = 0) | N/A (n = 0) | 90 | |
St. Helena, CA | <0.00010b | 0.0069b | 0.00020b | N/A (n = 0) | N/A (n = 0) | 93 | |
Sandpoint, ID | 0.24 | 0.58 | 0.57 | N/A (n = 0) | N/A (n = 0) | 116 | |
Richland, WA | 0.0088 | 0.25 | <0.00010b | 0.012 | N/A (n = 1) | 135 | |
Lake Oswego, OR | 0.019 | 0.22 | 0.014 | 0.038 | N/A (n = 1) | 189 | |
after wildfires indoorc | Carson, WA | <0.00010c | 0.88 | 0.16 | N/A (n = 0) | N/A (n = 0) | 21 |
McCall, ID | 0.36 | 0.26 | 0.044 | N/A (n = 0) | N/A (n = 0) | 73 | |
Prineville, OR | 0.59 | 0.92 | 0.090 | N/A (n = 1) | N/A (n = 0) | 95 | |
Sandpoint, ID | 0.096 | 0.24 | 0.74 | N/A (n = 0) | N/A (n = 0) | 116 | |
Richland, WA | 0.018 | 0.54 | <0.0001c | 0.012 | N/A (n = 1) | 135 | |
Seattle, WA 2 | 0.85 | 0.91 | 0.011 | N/A (n = 0) | N/A (n = 1) | 142 | |
Sunriver, OR | 0.14 | 0.98 | 0.0050c | N/A (n = 1) | N/A (n = 0) | 184 | |
Lake Oswego, OR | 0.085 | 0.0030c | 0.00030c | 0.015 | N/A (n = 1) | 189 | |
Corvallis, OR 2 | 0.10 | 0.93 | 0.0086 | 0.032 | 0.041 | 220 | |
before wildfires outdoorb | Alturas, CA | 0.92 | 0.95 | 1.0 | 1.0 | 1.0 | 70 |
Newport, OR | 0.79 | 0.16 | 0.00050b | N/A (n = 0) | N/A (n = 1) | 90 | |
St. Helena, CA | 0.033 | 0.025 | <0.00010b | 0.016 | N/A (n = 1) | 93 | |
Sandpoint, ID | 0.50 | 0.053 | <0.00010b | 0.0032b | 0.0049b | 116 | |
Richland, WA | 0.061 | 0.033 | <0.00010b | 0.0002b | N/A (n = 1) | 135 | |
Lake Oswego, OR | 0.14 | 0.0054b | <0.00010b | <0.00010b | <0.00010b | 189 | |
after wildfires outdoorc | Carson, WA | 0.99 | 0.80 | 0.99 | 0.99 | N/A (n = 0) | 21 |
McCall, ID | 0.00020c | 0.012 | <0.00010c | N/A (n = 0) | N/A (n = 0) | 73 | |
Prineville, OR | 0.0099 | 0.051 | <0.00010c | 0.00080c | 0.044 | 95 | |
Sandpoint, ID | 0.94 | 0.016 | <0.00010c | 0.00010c | <0.00010c | 116 | |
Richland, WA | 0.99 | 0.011 | <0.00010c | 0.00030c | N/A (n = 1) | 135 | |
Seattle, WA 2 | <0.0001c | 0.0020c | <0.00010c | 0.016 | 0.049 | 142 | |
Sunriver, OR | 0.19 | 0.92 | 1.0 | 1.0 | 0.97 | 184 | |
Lake Oswego, OR | 0.48 | 0.011 | <0.00010c | <0.00010c | <0.00010c | 189 | |
Corvallis, OR 2 | 0.61 | 0.00020c | <0.00010c | <0.00010c | <0.00010c | 220 |
Significant p-values indicate that vapor-phase PAH air concentrations during wildfires are significantly greater than before or after. α values are Bonferroni-corrected for each sampling event.
Significant when probability >t at α′ = 0.0083.
Significant when probability >t at α′ = 0.0056.