Evidence basis. Three supplied records contain sufficient quantitative data for accurate graphs: the Mayo-Tsanaga 2014 outbreak dataset (1050 cases, 98 deaths, population 776,306) with infection-source attribution and R0 under three control intensities ; the V. paracholerae genomic survey (13,206 V. cholerae genomes screened; 222 V. paracholerae retained) ; and the stochastic threshold analysis (R_s^0 = 3.9494, deterministic R0 = 4.1652, extinction threshold R_E^0 = 0.8489) .
Read: Waterborne infection dominated (673/1050 = 64.1%), yet funeral-related transmission (183 cases) was non-trivial β a pathway unique to this model. Strong combined controls (vaccination 0.8, treatment 0.9, sanitation 0.85) push modeled R0 below 1 (0.89), the extinction threshold. These are model outputs calibrated to one outbreak year; underreporting and single-site parameterization limit generalizability .
Read: blaCARB-9-like appears in ~51% of V. paracholerae genomes, mostly embedded in chromosomal integrons β making this species a persistent ARG reservoir. Critically, ~1.8% of genomes labeled V. cholerae were actually V. paracholerae (190 of 13,206 reclassified), and the five-marker locus achieves ~98% sensitivity / >99.99% specificity. Misclassified genomes silently distort cholera surveillance phylogenies .
Read: Adding Ornstein-Uhlenbeck environmental noise lowers the effective threshold from 4.17 (deterministic) to 3.95 (persistence criterion), while a stricter extinction criterion (R_E^0) sits at 0.85. White-noise forcing and stochastic treatment models consistently yield smaller reproduction numbers than deterministic counterparts, implying deterministic models can overestimate outbreak risk . Caveat: neither model is fitted to observed outbreak data; thresholds are sufficient, not necessary, conditions .
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