Spatial distribution and pollution evaluation of heavy metals in soils surrounding a typical municipal solid waste incineration plant in Hang-Jia-Hu plain

Author(s):  
Cheng Zhang ◽  
Hongfeng Su ◽  
Hui Gao ◽  
Lishan Zhang ◽  
Shan Zhong
2021 ◽  
Vol 1203 (3) ◽  
pp. 032087
Author(s):  
Nikolina Poranek ◽  
Beata Łaźniewska-Piekarczyk ◽  
Adrian Czajkowski ◽  
Krzysztof Pikoń

Abstract To improve the condition of the environment and prevent its degradation, global trends have moved from linear to the circular economy. Closing the loop is to protect natural resources, minimize waste, emissions, and pollution. The circular economy assumptions are based mainly on the 3-R: Reduce (minimum use of raw materials); Reuse (maximum reuse of products and components); Recycle (high-quality reuse of raw materials). In the waste management hierarchy, the last place in the circular economy is energy recovery. In the process of incinerating municipal waste, secondary waste is generated. Some of them, like fly ash, are hazardous waste. It includes, among others heavy metals, chlorine, sulphur, and other pollutions, hence it is currently not used as a raw material. The management of fly ash from municipal solid waste incineration plant in the construction industry is a part of sustainable development and the circular economy. Fly ash is a hazardous and heterogeneous waste, therefore it is important to know its physicochemical and construction properties, which are presented in the article. Fly ash has pozzolanic properties, therefore it can be a good binding and building material. For fly ash to be a component of the construction mixture, it is necessary to immobilize pollutants, heavy metals, and some elements so that they do not leach into the environment. For this purpose, the concrete structure and the C-S-H matrix should be compacted. Currently, fly ash is stabilized and stored in underground landfills. They are storage in closed salt, manganese, and potassium mines. However, the volume of post-mining voids is limited, and storage is not part of the circular economy. In addition, some countries do not have their fly ash storage facilities and it has to be exported across borders. This increases the carbon footprint and shortens the product life cycle.


2021 ◽  
Vol 121 ◽  
pp. 33-41
Author(s):  
Yanjun Hu ◽  
Lingqin Zhao ◽  
Yonghao Zhu ◽  
Bennong Zhang ◽  
Guixiang Hu ◽  
...  

2021 ◽  
Vol 13 (2) ◽  
pp. 535
Author(s):  
Jing Gao ◽  
Tao Wang ◽  
Jie Zhao ◽  
Xiaoying Hu ◽  
Changqing Dong

Melting solidification experiments of municipal solid waste incineration (MSWI) fly ash were carried out in a high-temperature tube furnace device. An ash fusion temperature (AFT) test, atomic absorption spectroscopy (AAS), scanning electron microscope (SEM), and X-ray diffraction (XRD) were applied in order to gain insight into the ash fusibility, the transformation during the melting process, and the leaching behavior of heavy metals in slag. The results showed that oxide minerals transformed into gehlenite as temperature increased. When the temperature increased to 1300 °C, 89 °C higher than the flow temperature (FT), all of the crystals transformed into molten slag. When the heating temperatures were higher than the FT, the volatilization of the Pb, Cd, Zn, and Cu decreased, which may have been influenced by the formation of liquid slag. In addition, the formation of liquid slag at a high temperature also improved the stability of heavy metals in heated slag.


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