Plastic waste management addresses the rapid accumulation of non-biodegradable synthetic polymers (such as Polyethylene Terephthalate [PET], High-Density Polyethylene [HDPE], Polyvinyl Chloride [PVC], and Polypropylene [PP]) in municipal solid waste streams. Characterized by high chemical stability and resistance to natural weathering, plastic waste requires specialized material recovery, mechanical reprocessing, and advanced chemical recycling kinetics to prevent long-term environmental accumulation.
The thermal degradation of polymers during thermochemical recycling (such as pyrolysis and gasification) follows non-isothermal reaction kinetics evaluated using the Arrhenius Kinetic Equation:
$$\frac{d\alpha}{dt} = k(T) \cdot f(\alpha) = A \cdot \exp\left(-\frac{E_a}{R \cdot T}\right) \cdot (1 - \alpha)^n$$
Where $\alpha$ is the degree of thermal conversion ($\frac{m_0 - m_t}{m_0 - m_\infty}$), $m_0$ is initial mass, $m_t$ is mass at time $t$, $m_\infty$ is final residual mass, $A$ is the pre-exponential factor ($\text{s}^{-1}$), $E_a$ is the activation energy ($\text{kJ/mol}$), $R$ is the universal gas constant ($8.314\text{ J/mol}\cdot\text{K}$), $T$ is absolute temperature ($\text{K}$), and $n$ is the reaction order.
Mechanical recycling efficiency is quantified through the material recovery mass balance ratio ($\eta_{\text{rec}}$) across sorting and pelletization stages:
$$\eta_{\text{rec}} = \frac{M_{\text{recycled}}}{M_{\text{input}}} = \frac{\sum_{i=1}^{k} \left( m_i \cdot \gamma_i \cdot \xi_i \right)}{M_{\text{input}}}$$
Where $m_i$ is the mass fraction of resin type $i$, $\gamma_i$ is the automated optical sorting purity efficiency, and $\xi_i$ is the extrusion process yield factor. Uncollected microplastics ($d_p < 5\text{ mm}$) exhibit settling and transport behavior in aquatic environments governed by modified non-spherical drag relationships:
$$v_s = \sqrt{\frac{4 \cdot g \cdot (\rho_p - \rho_w) \cdot d_p}{3 \cdot C_D \cdot \rho_w}}$$
Where $v_s$ is particle terminal velocity, $\rho_p$ is polymer density, $\rho_w$ is water density, and $C_D$ is the non-spherical particle drag coefficient.
Historically, plastic waste management across Indian urban centers relied heavily on unorganized informal scrap picking, open dumping, and low-efficiency mechanical downcycling. These practices led to severe drain blockages, urban flooding risks, toxic open burning emissions, and pervasive microplastic contamination in aquatic ecosystems.
Under modern statutory frameworks such as the Plastic Waste Management Rules (enforcing Extended Producer Responsibility - EPR) and the nationwide ban on single-use plastics, Indian environmental engineering practices have undergone rapid structural updates. Municipalities and industrial operators are now establishing mechanized Material Recovery Facilities (MRFs) equipped with Near-Infrared (NIR) optical sorters to automatically segregate polymer types. Furthermore, mixed, non-recyclable multi-layered plastics (MLP) are being diverted to high-temperature thermal processing in cement kilns as alternative fuel and raw material (AFR), pyrolyzed into industrial-grade drop-in liquid fuels, or blended as polymer-modified bitumen (PMB) for constructing long-lasting, water-resistant highway pavements under National Highways Authority of India (NHAI) specifications.
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