Impact of Plastics on Fate and Transport of Organic Contaminants in Landfills

Factors controlling organic contaminant sorption to common plastics in municipal solid waste were identified Consumer plastics [drinking water container, prescription drug bottle, soda bottle, disposable cold cup, computer casing, furniture foam, carpet, vinyl flooring, formica sheet] and model polymers [high-density polyethylene (HDPE), medium-density polyethylene, low-density polyethylene, poly(vinyl chloride) (PVC)] were characterized by X-ray diffractometry, differential scanning calorimetry, and elemental analysis The material characterization was used to interpret batch isotherm and kinetic data K(p) values describing toluene sorption to rubbery or soft polymers could be normalized by the amorphous polymer fraction (f(amorphous)) but not by the organic carbon fraction (f(oc)). Diffusion coefficients ID) describing the uptake rate of toluene by rubbery plastics (HOPE, drinking water container, prescription drug bottle) were similar (D approximate to 10(-10) cm(2)/s), indicating that pure HDPE can be used as a model for rubbery plastics Toluene diffusivity was similar among glassy or hard plastics (PVC, soda bottle, computer casing, disposable cold cup, D approximate to 10(-12) cm(2)/s) but lower than for rubbery plastics Plastics in landfills are potential sinks of hydrophobic organic contaminants (HOCs) because of their higher affinity for HOCs compared to lignocellulosic materials and the slow desorption of HOCs from glassy plastics