Waste artificial marble pyrolysis and hydrolysis

IF 7.1 2区 环境科学与生态学 Q1 ENGINEERING, ENVIRONMENTAL Waste management Pub Date : 2025-03-01 Epub Date: 2025-02-06 DOI:10.1016/j.wasman.2025.01.032
Jacopo De Tommaso , Federico Galli , Tien Dat Nguyen , Yanfa Zhuang , Jean-Luc Dubois , Gregory S. Patience
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Abstract

Artificial marble, a composite material consisting of 40 % (g g−1) Poly Methyl Methacrylate (PMMA) and 60 % (g g−1) aluminium hydroxide Al(OH)3, combines the durability and aesthetics of real marble with the lightweight and moldability of plastic. It is the most sought-after synthetic stone in the world, with a production volume of over 1 million t in 2021. However, due to a high level of cross-linking, mechanical recycling of the composite is impossible, while chemical recycling is achievable, yet unprofitable. The only economically viable recycling solution is to retain the value of both the organic and inorganic fraction of the composite. We investigated the pyrolysis and hydrolysis of post-consumer end-of-life artificial marble to identify possible valorization routes, examining the effects of temperature, water content, catalyst presence, and heating style. Temperature directly accelerates thermolysis, and indirectly hydrolysis. The water inherently present in Al(OH)3 drives initial hydrolysis, and temperature expedites inorganic fraction dehydration, increasing local water partial pressure near polymer ester sites. Above 350 °C, PMMAeq depolymerizes faster than it hydrolyzes, balancing the effects of temperature on water dehydration with the depletion of available ester sites for hydrolysis. Contrary to intuition, PMMA does not depolymerize to its monomer MMA and then hydrolyze its acid (methacrylic acid); instead, PMMA partially hydrolyzes to poly methacrylic acid (PMAA) while also depolymerizing to MMA. PMAA then dehydrates and degrades, releasing CO and CO2. The optimal method involves a heating ramp that first releases water at 300 °C, minimizing hydrolysis, and then favors MMA production at 400 °C, achieving a 66 % (g g−1) MMA yield. Regardless of the operative conditions, the inorganic fraction transforms from Al(OH)3 to a γ-alumina precursor, boehmite. Additionally, the remaining polymer in the residue, about 9 % (g g−1), has the required heat capacity for an energy-self sufficient calcination to γ-alumina. This dual-phase process not only maximizes MMA recovery but also retains the value of the inorganic fraction, providing a sustainable and economically viable recycling method for artificial marble.
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废弃人造大理石的热解和水解
人造大理石是一种由40% (g g−1)聚甲基丙烯酸甲酯(PMMA)和60% (g g−1)氢氧化铝(OH)3组成的复合材料,它结合了真大理石的耐用性和美观性以及塑料的轻质和可塑性。它是世界上最受欢迎的合成石,2021年的产量超过100万吨。然而,由于交联程度高,复合材料的机械回收是不可能的,而化学回收是可以实现的,但无利可图。唯一经济可行的回收解决方案是保留复合材料的有机和无机部分的价值。我们研究了使用后报废人造大理石的热解和水解,以确定可能的增值途径,并研究了温度、含水量、催化剂存在和加热方式的影响。温度直接加速热解,间接加速水解。存在于Al(OH)3中的水驱动初始水解,温度加速无机部分脱水,增加聚合物酯位附近的局部水分压。在350°C以上,PMMAeq解聚速度快于水解速度,平衡了温度对水脱水的影响和可用酯位水解的消耗。与直觉相反,PMMA不会解聚成其单体MMA,然后水解其酸(甲基丙烯酸);相反,PMMA部分水解成聚甲基丙烯酸(PMAA),同时也解聚成MMA。然后PMAA脱水并降解,释放CO和CO2。最佳方法包括加热斜坡,首先在300°C时释放水,最大限度地减少水解,然后在400°C时有利于MMA的生产,实现66% (g g−1)的MMA产率。无论操作条件如何,无机部分都从Al(OH)3转变为γ-氧化铝前驱体薄水铝石。此外,残渣中剩余的聚合物,约9% (g g−1),具有能量自给烧成γ-氧化铝所需的热容量。这种双相工艺在最大限度地提高MMA回收率的同时,也保留了无机部分的价值,为人造大理石提供了一种可持续的、经济可行的回收方法。
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来源期刊
Waste management
Waste management 环境科学-工程:环境
CiteScore
15.60
自引率
6.20%
发文量
492
审稿时长
39 days
期刊介绍: Waste Management is devoted to the presentation and discussion of information on solid wastes,it covers the entire lifecycle of solid. wastes. Scope: Addresses solid wastes in both industrialized and economically developing countries Covers various types of solid wastes, including: Municipal (e.g., residential, institutional, commercial, light industrial) Agricultural Special (e.g., C and D, healthcare, household hazardous wastes, sewage sludge)
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