Abstract
Environmentally mediated infectious disease transmission models provide a mechanistic approach to examining environmental interventions for outbreaks, such as water treatment or surface decontamination. The shift from the classical SIR framework to one incorporating the environment requires codifying the relationship between exposure to environmental pathogens and infection, i.e. the dose–response relationship. Much of the work characterizing the functional forms of dose–response relationships has used statistical fit to experimental data. However, there has been little research examining the consequences of the choice of functional form in the context of transmission dynamics. To this end, we identify four properties of dose–response functions that should be considered when selecting a functional form: low-dose linearity, scalability, concavity, and whether it is a single-hit model. We find that i) middle- and high-dose data do not constrain the low-dose response, and different dose–response forms that are equally plausible given the data can lead to significant differences in simulated outbreak dynamics; ii) the choice of how to aggregate continuous exposure into discrete doses can impact the modeled force of infection; iii) low-dose linear, concave functions allow the basic reproduction number to control global dynamics; and iv) identifiability analysis offers a way to manage multiple sources of uncertainty and leverage environmental monitoring to make inference about infectivity. By applying an environmentally mediated infectious disease model to the 1993 Milwaukee Cryptosporidium outbreak, we demonstrate that environmental monitoring allows for inference regarding the infectivity of the pathogen and thus improves our ability to identify outbreak characteristics such as pathogen strain.
Highlights
Modeling infectious disease transmission by person-to-person contact has a long history in the scientific community
We present a number of examples to highlight the impact the choice of a dose–response function has on model dynamics
There is good agreement, qualitatively, among the seven functions (Fig 2a); in particular, the exact and approximate beta–Poisson models are indistinguishable. These seven functions are used as the dose– response relationship f in the model given in Eq (3), parameterized to reasonably approximate Cryptosporidium
Summary
Modeling infectious disease transmission by person-to-person contact has a long history in the scientific community. Explicit modeling of pathogens in the environment can generate additional insight into how environmental processes affect infectious disease dynamics and allow modelers to incorporate knowledge from experimental studies into their models It allows for consideration of pathogen fate and transport [20] and the functional relationship, called the dose– response relationship, between the amount of pathogen a person is exposed to (dose) and the probability of infection, illness, or death (response). Empirical models, which come from the field of chemical toxicology and are based on the theory of tolerance distributions [24], have been used, for foodborne diseases [25, 26] Those seeking to develop a dose–response relationship for QMRA must find data for an appropriate host organism that aligns with the exposure route and desired endpoint (e.g. symptoms or clinical infection) [27]. Once appropriate data are found, the choice of functional form from among a plausible set is usually a statistical one (goodness-of-fit or best-fit)
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