Table 2.
Lionfish population density (fish per 100 m2) on Okaloosa artificial reefs (ARs), Escambia ARs, and northern Gulf of Mexico (nGOM) natural reefs (NRs) during 2016–2018 estimated via remotely operated vehicle surveys. Changes in mean lionfish population density over time were assessed with generalized linear mixed models (GLMMs) with site incorporated as a random effect. Okaloosa AR and Escambia AR GLMMs were fit with a negative binomial error distribution and the nGOM NR model was fit with a Poisson distribution. GLMM outputs show log-linked parameter estimates for mean lionfish population density, 95% confidence intervals (CI) around mean lionfish density, z-score (z), and p-values (P). Hypothesis testing (z- and p-values) were conducted for each model (Okaloosa ARs, Escambia ARs, and nGOM NRs) to evaluate differences in population density on high-density sites (>25 lionfish per 100 m2 and with no prior lionfish removals) relative to the intercept (initial sampling date) and low-density sites (<15 lionfish per 100 m2 with prior lionfish removals) relative to high-density sites within the same area and sampling date.
| Lionfish density model | Sampling date | Density group | Reef sties | Mean density (100 m−2) | 95% CI | z | P | |
|---|---|---|---|---|---|---|---|---|
| Okaloosa ARs | 2016 | Oct (Intercept) | High | 10 | 27.22 | 17.69–41.88 | 15.03 | <0.001 |
| 2016 | Dec | High | 10 | 23.41 | 16.88–32.94 | −0.87 | 0.383 | |
| 2016 | Feb | High | 10 | 24.23 | 17.42–34.03 | −0.67 | 0.500 | |
| 2017 | Apr | High | 10 | 25.86 | 18.51–36.20 | −0.28 | 0.779 | |
| 2017 | May | High | 10 | 24.77 | 17.69–34.57 | −0.56 | 0.575 | |
| 2017 | Oct | High | 10 | 21.78 | 15.52–30.76 | −1.26 | 0.209 | |
| 2018 | Mar | High | 10 | 13.88 | 09.80–19.87 | −3.78 | <0.001 | |
| 2018 | Jun | High | 10 | 7.35 | 05.17–10.34 | −7.17 | <0.001 | |
| 2018 | Oct | High | 8 | 5.72 | 03.81–08.71 | −7.61 | <0.001 | |
| 2016 | Dec | Low | 8 | 5.17 | 02.72–10.34 | −4.80 | <0.001 | |
| 2017 | Feb | Low | 8 | 3.98 | 02.11–07.96 | −5.07 | <0.001 | |
| 2017 | Apr | Low | 8 | 6.30 | 03.15–12.11 | −4.02 | <0.001 | |
| 2017 | May | Low | 8 | 7.50 | 03.88–14.74 | −3.63 | <0.001 | |
| 2017 | Oct | Low | 8 | 15.61 | 08.17–29.97 | −1.40 | 0.161 | |
| 2018 | Mar | Low | 8 | 18.29 | 09.36–35.28 | −0.53 | 0.599 | |
| 2018 | Jun | Low | 8 | 11.94 | 06.11–23.60 | −0.42 | 0.671 | |
| 2018 | Oct | Low | 8 | 10.44 | 05.22–20.87 | 0.99 | 0.324 | |
| Escambia ARs | 2016 | June (Intercept) | High | 18 | 18.65 | 12.41–28.04 | 14.06 | <0.001 |
| 2017 | Nov | High | 9 | 31.71 | 17.90–56.32 | 1.81 | 0.070 | |
| 2018 | May | High | 18 | 8.39 | 05.22–13.43 | −3.32 | 0.001 | |
| 2018 | Aug | High | 18 | 6.34 | 03.92–10.26 | −4.42 | <0.001 | |
| 2018 | Dec | High | 18 | 7.27 | 04.48–11.56 | −3.92 | <0.001 | |
| 2016 | Jun | Low | 9 | 8.02 | 03.92–16.41 | −2.30 | 0.022 | |
| 2017 | Nov | Low | 9 | 8.56 | 03.80–19.34 | −3.16 | 0.002 | |
| 2018 | May | Low | 9 | 5.87 | 02.85–12.34 | −0.94 | 0.348 | |
| 2018 | Aug | Low | 9 | 3.04 | 01.46–06.53 | −1.89 | 0.058 | |
| 2018 | Dec | Low | 9 | 4.51 | 02.18–09.46 | −1.26 | 0.208 | |
| nGOM NRs | 2016 | Jul (Intercept) | High | 15 | 0.24 | 0.15–0.38 | −6.06 | <0.001 |
| 2017 | Oct | High | 15 | 0.35 | 0.24–0.52 | 1.98 | 0.048 | |
| 2018 | May | High | 7 | 0.29 | 0.15–0.57 | 0.54 | 0.592 | |
| 2018 | Aug | High | 15 | 0.20 | 0.13–0.30 | −0.88 | 0.380 | |
| 2018 | Oct | High | 8 | 0.07 | 0.03–0.15 | −3.11 | 0.002 | |