Table 2.
Stage | Habitat Type | Transect(s) | Tick Encounter Rate*† | Prevalence‡§ | ERI†‖ | ||||||
---|---|---|---|---|---|---|---|---|---|---|---|
Total | Mean (95% CI) | Significance | Total | + | % (95% CI) | Significance | Mean (95% CI) | Significance | |||
Adult | Forest w/invasive | 3, 4 | 764 | 54.6 (45.9, 63.2) | A¶ | 742 | 24 | 3.2 (2.0, 4.5) | A¶ | 1.7 (0.9, 2.5) | A |
Edge | 7, 8 | 544 | 44.1 (34.4, 53.8) | A | 529 | 9 | 1.7 (0.6, 2.8) | AB | 0.7 (0.2, 1.3) | AB | |
Shrub | 1, 2 | 546 | 42.6 (25.4, 59.8) | B | 524 | 6 | 1.1 (0.2, 2.1) | B | 0.5 (0.0, 0.9) | BC | |
Forest w/native | 9, 10 | 137 | 11.8 (8.7, 15.0) | C | 127 | 1 | 0.8 (0.0, 2.3) | AB | 0.1 (0.0, 0.3) | C | |
Field | 5, 6 | 47 | 3.8 (0, 8.8) | D | 42 | 0 | 0 | AB | 0 | C | |
All habitats | – | 2,038 | – | 1,964 | 40 | – | – | – | – | ||
Nymph | Forest w/invasive | 3, 4 | 286 | 20.4 (16.0, 24.9) | A | 230 | 1 | 0.4 (0.0, 1.3) | A | 0.1 (0.0, 0.2) | A |
Edge | 7, 8 | 95 | 7.7 (2.9, 12.5) | C | 78 | 0 | 0 | A | 0 | A | |
Shrub | 1, 2 | 12 | 1.0 (0.3, 1.6) | D | 8 | 0 | 0 | A | 0 | A | |
Forest w/native | 9, 10 | 140 | 12.1 (7.7, 16.5) | B | 103 | 1 | 1.0 (0.0, 2.9) | A | 0.1 (0.0, 0.3) | A | |
Field | 5, 6 | 5 | 0.4 (0, 0.9) | D | 5 | 0 | 0 | A | 0 | A | |
All habitats | – | 538 | – | – | 424 | 2 | – | – | – | – |
DTV = deer tick virus; ERI = entomological risk index; Forest w/invasive = forest with invasive vegetation in the understory; Forest w/native = forest with native vegetation in the understory.
Mean number of ticks collected/hour; n = 20 plots/habitat.
Same letters indicate that values are not statistically different (pairwise Wilcoxon rank sum tests, P <0.05).
Number of DTV-positive ticks/total tested.
Same letters indicate that values are not statistically different (Fisher’s exact test, P <0.05).
Mean number of infected ticks collected/hour; n = 20 plots/habitat.
Mean ticks/hour and DTV prevalence in “forest w/invasive” were marginally greater than those in edge, P = 0.06 and 0.09, respectively.