Abstract:Aichi virus (AiV) that results in gastroenteritis worldwide, is spread through contaminated shellfish and water. The resistance/tolerance of AiV to common inactivation processes along with the absence of commercially available vaccines makes it necessary to study its thermal inactivation kinetics. This research evaluated the heat inactivation of AiV in cell-culture media using 2-ml sterile glass vials by the linear and Weibull models. Heat treatments of AiV titers of 7 log plaque forming units (PFU)/ml were co… Show more
“…In order to determine inactivation parameters, models such as the linear regression model provide standards to estimate D ‐values, that is, time (min) required to cause 1 log PFU/mL reduction of infectious viruses that can predict the treatment conditions (time) required for higher log reductions (Ailavadi et al., 2021; Bozkurt et al., 2013). The calculated D ‐values for FCV‐F9 with D = 0.82 ± 0.01 min and TV of D = 0.96 ± 0.08 min with ~1 ppm ozone treatment within clear sterile water samples (Table 4) demonstrated that the linear D ‐values were close for FCV‐F9 and TV inactivation at RT.…”
Section: Discussionmentioning
confidence: 99%
“…This linear line equation has a "slope of −1/D, where the number of viral survivors in PFU/mL after an exposure time t (min) is described as N(t) that has an initial viral population of N 0 " (Bozkurt et al, 2013;Patwardhan et al, 2020;Ailavadi et al, 2019Ailavadi et al, , 2021. The D (min)-value is then derived from this equation as the time of treatment that is needed to reduce the initial target viral population by 10-fold (Ailavadi et al, 2021).…”
Section: Parameters For Modeling Inactivation Of Fcv-f9 and Tv By ~1 ...mentioning
Ongoing challenges with reproducible human norovirus cultivable assays necessitate the use of surrogates, such as feline calicivirus (FCV‐F9) and Tulane virus (TV), during inactivation studies. Chlorine alternates used as control strategies include aqueous and gaseous ozone. This study aimed at determining the inactivation of FCV‐F9 and TV by a portable ozone‐generating device. FCV‐F9 (∼8 log PFU/mL) or TV (∼6 log PFU/mL) in sterile‐low‐organic matter‐containing‐water was treated for 0–5 min, or in sterile‐water containing newborn calf serum (high‐organic matter/protein) for 0–38 min with ∼1 ppm ozone (pH 7–6). Infectivity was determined from triplicate treatments using plaque assays. FCV‐F9 titers significantly decreased by 6.07 log PFU/mL after 5 min in ozonated low‐organic‐matter‐containing‐water and was non‐detectable (≤2 log PFU/mL) after 36 min treatments in high‐organic‐matter‐containing water (p < 0.05). TV titers decreased by 4.18 log PFU/mL after 4 min in ozonated low‐organic‐matter water (non‐detectable after 4.5 min) and were non‐detectable after 22.5 min treatments of high‐organic‐matter‐containing water (p < 0.05). Overall, ∼1 ppm aqueous ozone significantly decreased FCV‐F9 by >6 log PFU/mL after 5 min, TV to non‐detectable levels (≤2 log PFU/mL) after 4.5 min and required longer treatments (>32 and >20 min, respectively) for ≥4 log reduction in high‐organic‐matter‐containing water (p < 0.05). For ozone treatment of both viruses, the linear and Weibull models were similar for low‐organic‐load water, though the Weibull model was better for the high‐organic load water. Prior filtration or organic load removal is recommended before ozonation for increased viral inactivation with decreased treatment‐time.
“…In order to determine inactivation parameters, models such as the linear regression model provide standards to estimate D ‐values, that is, time (min) required to cause 1 log PFU/mL reduction of infectious viruses that can predict the treatment conditions (time) required for higher log reductions (Ailavadi et al., 2021; Bozkurt et al., 2013). The calculated D ‐values for FCV‐F9 with D = 0.82 ± 0.01 min and TV of D = 0.96 ± 0.08 min with ~1 ppm ozone treatment within clear sterile water samples (Table 4) demonstrated that the linear D ‐values were close for FCV‐F9 and TV inactivation at RT.…”
Section: Discussionmentioning
confidence: 99%
“…This linear line equation has a "slope of −1/D, where the number of viral survivors in PFU/mL after an exposure time t (min) is described as N(t) that has an initial viral population of N 0 " (Bozkurt et al, 2013;Patwardhan et al, 2020;Ailavadi et al, 2019Ailavadi et al, , 2021. The D (min)-value is then derived from this equation as the time of treatment that is needed to reduce the initial target viral population by 10-fold (Ailavadi et al, 2021).…”
Section: Parameters For Modeling Inactivation Of Fcv-f9 and Tv By ~1 ...mentioning
Ongoing challenges with reproducible human norovirus cultivable assays necessitate the use of surrogates, such as feline calicivirus (FCV‐F9) and Tulane virus (TV), during inactivation studies. Chlorine alternates used as control strategies include aqueous and gaseous ozone. This study aimed at determining the inactivation of FCV‐F9 and TV by a portable ozone‐generating device. FCV‐F9 (∼8 log PFU/mL) or TV (∼6 log PFU/mL) in sterile‐low‐organic matter‐containing‐water was treated for 0–5 min, or in sterile‐water containing newborn calf serum (high‐organic matter/protein) for 0–38 min with ∼1 ppm ozone (pH 7–6). Infectivity was determined from triplicate treatments using plaque assays. FCV‐F9 titers significantly decreased by 6.07 log PFU/mL after 5 min in ozonated low‐organic‐matter‐containing‐water and was non‐detectable (≤2 log PFU/mL) after 36 min treatments in high‐organic‐matter‐containing water (p < 0.05). TV titers decreased by 4.18 log PFU/mL after 4 min in ozonated low‐organic‐matter water (non‐detectable after 4.5 min) and were non‐detectable after 22.5 min treatments of high‐organic‐matter‐containing water (p < 0.05). Overall, ∼1 ppm aqueous ozone significantly decreased FCV‐F9 by >6 log PFU/mL after 5 min, TV to non‐detectable levels (≤2 log PFU/mL) after 4.5 min and required longer treatments (>32 and >20 min, respectively) for ≥4 log reduction in high‐organic‐matter‐containing water (p < 0.05). For ozone treatment of both viruses, the linear and Weibull models were similar for low‐organic‐load water, though the Weibull model was better for the high‐organic load water. Prior filtration or organic load removal is recommended before ozonation for increased viral inactivation with decreased treatment‐time.
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