Find research datasets worth reusing

opencc-by-4.0Mar 2024View details →

Figure 2 in The problem of taxonomic uncertainty in biosecurity: South African mite interceptions as an example

Figure 2 Images of slide-mounted specimens, showing features which could clearly distinguish the intercepted unknownBrevipalpus species,

opencc-by-4.0Mar 2024View details →

Figure 1 in The problem of taxonomic uncertainty in biosecurity: South African mite interceptions as an example

Figure 1 South African biosecurity personnel inspecting imported kiwifruit for insects and mites. Images have been edited to remove sensitive information, including identity of personnel.

opencc-by-4.0Nov 2021View details →

Figure 1 in Developing biosecurity plans for non-native species in marine dependent areas: the role of legislation, risk management and stakeholder engagement

Figure 1. Five-stage approach for risk assessment management of NNS in Shetland, adapted from the ecosystem-based risk management framework (Cormier et al. 2013).

Figure 6 in In for the kill: novel biosecurity approaches for invasive and medically important mosquito species

Figure 6. Mean (+ SE) proportioned mortality rates of Culex quinquefasciatus larvae following exposure to submersion treatments with Virkon® Aquatic disinfectant at different exposure concentrations and durations (n = 3 per experimental group).

Figure 4 in In for the kill: novel biosecurity approaches for invasive and medically important mosquito species

Figure 4. Mean (+ SE) proportioned hatchability rates of Aedes albopictus following exposure to submersion treatments with (a) 1% and (b) 4% Virkon® Aquatic disinfectant (n = 3 per experimental group).

Figure 2 in In for the kill: novel biosecurity approaches for invasive and medically important mosquito species

Figure 2. Mean (+ SE) proportioned hatchability rates of Culex quinquefasciatus egg rafts following different exposure durations to direct steam jet (n = 3 per experimental group).

Figure 3 in In for the kill: novel biosecurity approaches for invasive and medically important mosquito species

Figure 3. Mean (+ SE) proportioned hatchability rates of Aedes albopictus following exposure to spray treatments with 1% (a) and 4% (b) Virkon® Aquatic disinfectant (n = 3 per experimental group).

Figure 1 in In for the kill: novel biosecurity approaches for invasive and medically important mosquito species

Figure 1. Mean (+ SE) proportioned hatchability rates of Aedes albopictus following different exposure durations to direct steam jet (n = 3 per experimental group).

Figure 5 in In for the kill: novel biosecurity approaches for invasive and medically important mosquito species

Figure 5. Mean (+ SE) proportioned mortality rates of larval Aedes albopictus following different exposure durations to direct steam jet (n = 3 per experimental group).

Figure 6 in Better biosecurity: spread-prevention of the invasive Asian clam, Corbicula fluminea (Müller, 1774)

Figure 6. Mean mortality (± SE) of adult Corbicula fluminea specimens (SH = 15–26 mm) 24 hrs post-exposure to a direct steam application, at a distance of 2–3 cm from the source, for 10 sec, 30 sec, 1, 2, 5 and 10 minutes (n = 5, with 70 clams per n).

Figure 4 in Better biosecurity: spread-prevention of the invasive Asian clam, Corbicula fluminea (Müller, 1774)

Figure 4. Mean mortality (± SE) for groups of ten adult Corbicula fluminea specimens (SH = 15–26 mm) 24 hrs post-exposure to 35 (35 g L-1) or 70% (70 g L-1) aerated salt solutions (regular table salt) for 1, 6, 24, 48 and 72 hrs (n = 5, with 150 clams per n).

Figure 2 in Better biosecurity: spread-prevention of the invasive Asian clam, Corbicula fluminea (Müller, 1774)

Figure 2. Mean mortality (± SE) of adult Corbicula fluminea specimens (SH = 15–26 mm) 24 hrs post-exposure to warm water (30 °C) solutions of aquatic disinfectants Virasure® Aquatic and Virkon® Aquatic, at both 2% (20 g L-1) and 4% (40 g L-1) concentrations. Experimental groups, each consisting of ten adult clams, were immersed in solutions of either chemical for 10, 20, 40 and 80 minutes (n = 3, with 200 clams per n).

Figure 5 in Better biosecurity: spread-prevention of the invasive Asian clam, Corbicula fluminea (Müller, 1774)

Figure 5. Mean mortality (± SE) for groups of ten medium (A: SH = 15–20.9 mm) and ten large (B: SH = 21–36 mm) adult Corbicula fluminea specimens 24 hrs post-exposure to hot water temperatures of 35, 40 and 45 °C for 5, 10 and 20 minutes (n = 5, with 120 clams per n).

Figure 3 in Better biosecurity: spread-prevention of the invasive Asian clam, Corbicula fluminea (Müller, 1774)

Figure 3. Mean mortality (± SE) of adult Corbicula fluminea specimens (SH = 15–26 mm) 24 hrs post-exposure to 5 (50 ml L-1), 10 (100 ml L-1) or 20% (200 ml L-1) bleach solutions. Experimental groups, each consisting of ten clams, were immersed in solutions of either chemical for 10, 20, 40 and 80 minutes (n = 3, with 160 clams per n).

Figure 1 in Better biosecurity: spread-prevention of the invasive Asian clam, Corbicula fluminea (Müller, 1774)

Figure 1. Mean mortality (± SE) of medium (A: SH = 15–20.9 mm) and large (B: SH = 21–36 mm) adult Corbicula fluminea specimens 24 hrs post-exposure to aquatic disinfectants Virasure® Aquatic and Virkon® Aquatic, at both 2% (20 g L-1) and 4 % (40 g L-1) concentrations. Experimental groups, each consisting of ten clams, were immersed in solutions (dechlorinated tap water) of either chemical for 10, 20, 40 and 80 minutes (n = 5, with 400 clams per n).