Report from an ICT 2022 workshop on toxicology for Covid19 vaccines: Industry, regulatory and CRO perspectives.

The Covid pandemic took the world by surprise in late 2019 and the need for rapid development of vaccines became paramount. The challenge was how to accelerate standard vaccine development times as much as possible. With knowledge of the genetic code of SARsCOV2, vaccine manufacturers throughout the world have risen to the challenge and several new vaccines were rapidly developed for emergency use. In March 2020, global Regulatory Authorities met to consider how to start early clinical trials and accept rolling submissions. Before use in clinical trials or any mass vaccination campaigns, the safety of the candidate vaccine needs to be evaluated. Non-clinical toxicology studies are required as an important part of vaccine safety evaluation. The extent of the toxicology evaluation prior to the start of clinical trials depended on several factors, including: the type of the candidate vaccine as well as already available supportive information with the candidate vaccine or similar vaccine types. For vaccine candidates with pre-existing data, this would save valuable time whilst a full toxicology evaluation was completed in parallel. For vaccines with more limited data, toxicology data was required before clinical development could start. This workshop examined the nonclinical toxicology studies for new Covid vaccines from the perspectives of: Vaccine manufacturers with different vaccine technologies, managing global regulatory submissions/responses; CROs, managing the urgency of conducting and reporting studies and supporting new players in the vaccine world; and Regulatory Authorities, in supporting the review process, juggling the need for safety and quality with mounting pressure to approve vaccines.

Multidose pharmacokinetics of orally administered florfenicol in the channel catfish (Ictalurus punctatus).

Plasma disposition of florfenicol in channel catfish was investigated after an oral multidose (10 mg/kg for 10 days) administration in freshwater at water temperatures ranging from 24.7 to 25.9 °C. Florfenicol concentrations in plasma were analyzed by means of liquid chromatography with MS/MS detection. After the administration of florfenicol, the mean terminal half-life (t(1/2)), maximum concentration at steady-state (Css (max)), time of Css (max) (T(max)), minimal concentration at steady-state (Css (min)), and Vc /F were 9.0 h, 9.72 µg/mL, 8 h, 2.53 µg/mL, and 0.653 L/kg, respectively. These results suggest that florfenicol administered orally at 10 mg/kg body weight for 10 days could be expected to control catfish bacterial pathogens inhibited in vitro by a minimal inhibitory concentration value of <2.5 µg/mL.

Single intravenous and oral dose pharmacokinetics of florfenicol in the channel catfish (Ictalurus punctatus).

Plasma distribution and elimination of florfenicol in channel catfish were investigated after a single dose (10 mg/kg) of intravenous (i.v.) or oral administration in freshwater at a mean water temperature of 25.4 °C. Florfenicol concentrations in plasma were analyzed by means of liquid chromatography with MS/MS detection. After i.v. florfenicol injection, the terminal half-life (t(1/2)), volume of distribution at steady state (V(ss)), and central volume of distribution (V(c)) were 8.25 h, 0.9 and 0.381 L/kg, respectively. After oral administration of florfenicol, the terminal t(1/2), C(max), T(max), and oral bioavailability (F) were 9.11 h, 7.6 µg/mL, 9.2 h, and 1.09, respectively. There was a lag absorption time of 1.67 h in oral dosing. Results from these studies support that 10 mg florfenicol/kg body weight in channel catfish is an efficacious dosage following oral administration.

Metabolism of 3H/14C-labeled 4''-deoxy-4''-epimethylaminoavermectin B1a benzoate in chickens. Identification of novel fatty acid conjugates of '4'-deoxy-4''-epimethylaminoavermectin B1a.

The metabolism of 3H/14C-labeled 4"-deoxy-4"-epimethylaminoavermectin B1a (MAB1a) benzoate, the major homologue (>/=90%) of the avermectin insecticide emamectin benzoate, was studied in laying chickens. Ten Leghorn hens (Gallus domesticus) were orally dosed once daily for 7 days (1 mg/kg of body weight/day). Eggs and excreta were collected daily, and eggs were subsequently separated into whites and yolks. Chickens were euthanized within 20 hr after the last dose, and liver, kidney, heart, muscle, fat, ovaries, gizzard, gastrointestinal tract and contents, and carcass were collected. Approximately 70 and 6% of the total administered dose were recovered in the excreta plus gastrointestinal tract and contents and in the tissues plus eggs, respectively. Two novel metabolites, i.e. the 24-hydroxymethyl derivative of the parent compound (24-hydroxymethyl-4"-deoxy-4"-epimethylaminoavermectin B1a) and the N-demethylated derivative of 24-hydroxymethyl-4"-deoxy-4"-epimethylaminoavermectin B1a (24-hydroxymethyl-4"-deoxy-4"-epiaminoavermectin B1a), were identified. In addition, eight fatty acid conjugates of each of these two metabolites, comprising 8-75% of total radioactive residues in tissues and eggs, were isolated and identified. Although this represents some of the most extensive in vivo fatty acid conjugation to a xenobiotic reported to date, potential human exposure to MAB1a residues from consumption of chicken would be extremely low, because the dosage level in this study was approximately 1000-fold greater than the MAB1a residue levels seen in crops and because the majority of the applied dose was recovered in the excreta. Based on these findings, the avian biotransformation of MAB1a differs substantially from the mammalian biotransformation.

Dermal penetration of 4"-(epi-methylamino)-4"-deoxyavermectin B1a benzoate in the rhesus monkey.

The dermal absorption of the experimental avermectin insecticide emamectin benzoate was studied in the Rhesus monkey. Dermal absorption was calculated by comparing radioactivity levels in excreta following dermal application of the compound with those following administration of an equivalent intravenous dose. After i.v. administration of 300 micrograms [3H]MAB1a (prepared as a 1:1 solution of propylene glycol:saline) to three monkeys, plasma levels decreased biphasically with a rapid decline in radioactivity during the first 15 min followed by a slower decline to background. By 7 days post-dose, approximately 90% and 5% of the administered radioactivity was recovered in the faeces and urine, respectively. After a washout period, 300 micrograms [3H]MAB1a (dissolved in emulsifiable concentrate) was applied topically to the shaved forearm of the same monkeys. Following a 10-hr exposure period, approximately 90% of the radioactivity was recovered in a soap and water wash of the exposed forearms. Although plasma radioactivity levels generally remained below background levels, approximately 1.5% of the applied dose was recovered in the excreta. Dermal absorption of [3H]emamectin benzoate was calculated as 1.6%. The low dermal penetration of emamectin benzoate indicates that minimal actual exposure of agricultural workers to this compound will occur.