Abstract:Waste plastic gasification for hydrogen production combined with carbon capture and storage is one technology option to address the plastic waste challenge. Here, we conducted a techno-economic analysis and life cycle assessment to assess this option. The minimum hydrogen selling price of a 2000 oven-dry metric ton/day mixed plastic waste plant with carbon capture and storage is US$2.26–2.94 kg−1 hydrogen, which can compete with fossil fuel hydrogen with carbon capture and storage (US$1.21–2.62 kg−1 hydrogen) … Show more
“…The cost of post‐consumer HDPE was considered in the techno‐economic analysis. An estimated overhead cost of capital expenses and operating expenses was based on averages of work done by Lan and Yao for 2000 tons of plastic processed per day basis factory ($1.20 per kg H 2 ), [ 12 ] as well as work done by the National Renewable Energy Labs for 500 tons of biomass processed per day basis factory ($3.10 per kg H 2 ). [ 49 ] Overhead costs could be accurately modeled using software such as Aspen Plus, but this was deemed beyond the scope of this current work.…”
Hydrogen gas (H2) is the primary storable fuel for pollution‐free energy production, with over 90 million tonnes used globally per year. More than 95% of H2 is synthesized through metal‐catalyzed steam methane reforming that produces 11 tonnes of CO2 per tonne H2. “Green H2” from water electrolysis using renewable energy evolves no CO2, but costs 2–3x more, making it presently economically unviable. Here we report catalyst‐free conversion of waste plastic into clean H2 along with high purity graphene. The scalable procedure evolves no CO2 when deconstructing polyolefins and produces H2 in purities up to 94% at high mass yields. Sale of graphene byproduct at just 5% of its current value yields H2 production at negative cost. Life‐cycle assessment demonstrates a 39–84% reduction in emissions compared to other H2 production methods, suggesting the flash H2 process to be an economically viable, clean H2 production route.This article is protected by copyright. All rights reserved
“…The cost of post‐consumer HDPE was considered in the techno‐economic analysis. An estimated overhead cost of capital expenses and operating expenses was based on averages of work done by Lan and Yao for 2000 tons of plastic processed per day basis factory ($1.20 per kg H 2 ), [ 12 ] as well as work done by the National Renewable Energy Labs for 500 tons of biomass processed per day basis factory ($3.10 per kg H 2 ). [ 49 ] Overhead costs could be accurately modeled using software such as Aspen Plus, but this was deemed beyond the scope of this current work.…”
Hydrogen gas (H2) is the primary storable fuel for pollution‐free energy production, with over 90 million tonnes used globally per year. More than 95% of H2 is synthesized through metal‐catalyzed steam methane reforming that produces 11 tonnes of CO2 per tonne H2. “Green H2” from water electrolysis using renewable energy evolves no CO2, but costs 2–3x more, making it presently economically unviable. Here we report catalyst‐free conversion of waste plastic into clean H2 along with high purity graphene. The scalable procedure evolves no CO2 when deconstructing polyolefins and produces H2 in purities up to 94% at high mass yields. Sale of graphene byproduct at just 5% of its current value yields H2 production at negative cost. Life‐cycle assessment demonstrates a 39–84% reduction in emissions compared to other H2 production methods, suggesting the flash H2 process to be an economically viable, clean H2 production route.This article is protected by copyright. All rights reserved
“…26 On the economic side, Lan and Yao recently discussed that producing H 2 via wP gasification in the US could yield competitive costs with blue H 2 in the local market. 27 LCA has become the preferred approach for evaluating the environmental impact of technologies. 28 However, standard LCAs are mostly applied to compare alternatives as they lack thresholds beyond which a system should be deemed unsustainable, making the interpretation phase challenging.…”
Section: ■ Introductionmentioning
confidence: 99%
“…Moreover, Bhandari et al found that the electricity source heavily influences the environmental performance of electrolytic routes at the mid- and end point impact levels . On the economic side, Lan and Yao recently discussed that producing H 2 via wP gasification in the US could yield competitive costs with blue H 2 in the local market …”
Section: Introductionmentioning
confidence: 99%
“… 26 On the economic side, Lan and Yao recently discussed that producing H 2 via wP gasification in the US could yield competitive costs with blue H 2 in the local market. 27 …”
The rising demand
for single-use polymers calls for alternative
waste treatment pathways to ensure a circular economy. Here, we explore
hydrogen production from waste polymer gasification (wPG) to reduce
the environmental impacts of plastic incineration and landfilling
while generating a valuable product. We assess the carbon footprint
of 13 H2 production routes and their environmental sustainability
relative to the planetary boundaries (PBs) defined for seven Earth-system
processes, covering H2 from waste polymers (wP; polyethylene,
polypropylene, and polystyrene), and a set of benchmark technologies
including H2 from natural gas, biomass, and water splitting.
Our results show that wPG coupled with carbon capture and storage
(CCS) could reduce the climate change impact of fossil-based and most
electrolytic routes. Moreover, due to the high price of wP, wPG would
be more expensive than its fossil- and biomass-based analogs but cheaper
than the electrolytic routes. The absolute environmental sustainability
assessment (AESA) revealed that all pathways would transgress at least
one downscaled PB, yet a portfolio was identified where the current
global H2 demand could be met without transgressing any
of the studied PBs, which indicates that H2 from plastics
could play a role until chemical recycling technologies reach a sufficient
maturity level.
“…13 Consequently, there has been an unprecedented surge of multi-disciplinary research aimed at reducing plastic waste, limiting the production of virgin polymers, and improving pathways for PCPW to re-enter the value chain. [14][15][16][17][18][19][20][21][22][23][24][25][26][27] The development of automated optical sorting technologies for implementation at MRFs is one of these active research thrusts in the plastics recycling community. 28,29 This is because MRFs currently rely on air jets, magnetic separators, mechanical pistons, and human intervention to sort PCPW, all of which are methods that have been deemed insufficient to meet growing recycling demands.…”
Materials recovery facilities (MRFs) require new automated technologies if growing recycling demands are to be met. Current optical screening devices use visible (VIS) and near-infrared (NIR) wavelengths, frequency ranges that...
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