actual wastewater or biosolid amendments. Those that have been conducted are
largely from HICs even though the use of these wastewater products is used
extensively in LMICs.
Significant knowledge gaps relating to the exposure and risks of pharmaceuticals
to crops, terrestrial organisms and humans and livestock consuming these crops in
LMICs clearly exist. These knowledge gaps include the classes and concentrations
of pharmaceuticals in wastewater (either directly or indirectly) that are used to
irrigate crops, the sources of wastewater used for irrigation (to inform mitigation
strategies), the crops irrigated by pharmaceutical-contaminated wastewater
(to determine exposure pathways and risks to crops and consumers of crops) and
the stability of pharmaceuticals or uptake of pharmaceuticals in crops under different
agricultural scenarios and climatic conditions that occur in LMICs. Figure 1 highlights this disparity showing the widespread geographical usage of wastewater for
irrigation and the relatively few studies that have been conducted and their focus in
HICs. This is not trivial, in that the majority of the global population lives in LMICs
and relies on agriculture that abstracts the majority of the world’s water, increasingly
through wastewater reuse, for production.
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