The chemical recycling of chlorinated plastics is industrially challenging due to the release of corrosive HCl and char formation. In this work, a novel upcycling route for chlorinated plastics, including polyvinyl chloride (PVC), polyvinylidene chloride (PVDC), and chlorinated polyethylene (CPE), is developed. When ZnCl2-catalyzed dehydrochlorination (DHC) is combined with tandem DHC-hydrogenation, using a homogeneous Ru hydrogenation catalyst and metal oxides as a HCl trap, each plastic type can be selectively converted into an unsaturated polyolefin (UPO), which can be chemically split via metathesis. By rational design of reaction conditions, CPE (25 or 35 m% Cl) as a model substrate, a PVDC–PVC copolymer (66 m% Cl) and PVC (57 m% Cl) were consecutively converted into partially and fully dechlorinated UPOs. Both of these UPO products contained −CH2–CH2–sequences and up to 11 double bonds per 100 carbons. They were chemically split into α,ω-dienes using a second-generation Grubbs catalyst. Via this procedure, chlorinated plastics can be converted into valuable chemical building blocks, while the released HCl is sequestered.
Washing and thermal treatment are among the most promising technologies for managing municipal solid waste incineration fly ash (FA). However, the fate of residual ash after treatment remains uncertain and requires further investigation to achieve full resource utilization. In this study, the feasibility of using raw fly ash (RFA), washed fly ash (WFA), and thermally activated fly ash (TFA) as partial replacements for cement in composite cementitious materials was investigated. The macroscopic properties, strength development, environmental safety, and hydration mechanisms of FA-based composites were systematically examined. After the removal of hazardous substances, the physicochemical properties of WFA and TFA became closer to those of ordinary Portland cement (OPC). The mechanical performance of the composites followed the order TFA > WFA > RFA. At a 30% replacement level, the compressive strength of TFA reached 64.2 MPa, slightly higher than that of pure OPC and 103% greater than that of RFA. The corresponding carbon emission calibrated by strength is 29.5% lower than that of pure OPC, reaching 672.5 kgCO2e/t. In terms of environmental performance, heavy-metal leaching from all FA-based composites met the relevant standards, and the chloride immobilization efficiency exceeded 90%. The crystalline phases of hydration products included ettringite (AFt), calcium silicate hydrate [C-(A)-S-H], and Friedel’s salt. During hydration, the formation of portlandite, precipitation of AFt, and deposition of C-(A)-S-H led to an interlaced microstructure in the TFA-derived composites, effectively refining the microstructure and thereby enhancing the macroscopic performance. These findings provide a reference pathway for the utilization of FA and contribute to the sustainable management of FA.

