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1

Kovalčík, Jakub, Martin Straka, Peter Kačmáry, and Tomáš Pavlík. "CATALYST PROCESSING AND RECYCLING." Acta Tecnología 7, no. 3 (September 30, 2021): 99–104. http://dx.doi.org/10.22306/atec.v7i3.118.

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Discussed auto catalysts contain interesting quantities of platinum noble metals, palladium and rhodium according to the type of auto catalyst, thereby becoming a possible source of these metal aims to acquaint themselves with catalysts in general, their history and last but not least the possibilities of processing and obtaining noble metals for further use. The article deals with knowledge at the theoretical level of use of methods in processing depleted catalysts. It is pyrometallurgical and hydrometallurgical methods. The platinum group metals (PGMs) palladium, platinum, and rhodium represent the key materials for automotive exhaust gas treatment. Since there are currently no adequate alternatives, the importance of these metals for the automotive industry is steadily rising. The high value of PGMs in spent catalysts justifies their recycling. The state-of the-art technology is to melt the ceramic carrier and collect the precious fraction in a liquid metal bath. As the feed material has quite high melting points, huge amounts of energy are required for this process. Hydrometallurgical treatments of the spent catalysts offer the possibility to recycle the PGMs with less energy and time demands. Moreover, automotive catalysts contain further valuable materials to improve the exhaust gas treatment. These compounds, like cerium oxide, cannot be recovered in pyrometallurgical processes.
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2

Metzler, Jack, and Thuy Le. "Tritium Recycling (Processing) Facility Design." Fusion Technology 28, no. 3P2 (October 1995): 1359–64. http://dx.doi.org/10.13182/fst95-a30601.

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3

Petrova, A. A., M. A. Zyryanov, S. O. Medvedev, I. A. Voronin, and I. A. Petrova. "Integrated recycling of wood waste using recycling technology." E3S Web of Conferences 420 (2023): 07002. http://dx.doi.org/10.1051/e3sconf/202342007002.

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The activity of the Russian timber processing industry is inextricably linked to the constant generation of wood waste. The paper considers types of wood waste as well as the possibility of their integrated use in the conditions of wood processing plant. We present the results of experiments on the production of wood fibre boards with the addition of prepared wood waste: bark, sawmill waste, format-cutting waste, trapped fibre and hardwood waste, and determine the optimum percentage of the studied waste in the total wood mass.
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4

Wędrychowicz, Maciej. "The Recycling of Secondary Waste in Polish Recycling Companies." Rocznik Ochrona Środowiska 23 (2021): 715–30. http://dx.doi.org/10.54740/ros.2021.050.

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This article analyses the recycling of secondary waste in Polish recycling companies. An innovative method of processing PCBs is presented and trends that should be followed by plants processing non-ferrous metal waste are indicated. In conclusion, it is emphasised that the Polish WEEE recycling market is still at the early development and growth stage and the most important goals that enterprises should set themselves include cost optimisation, improvement of waste management logistics and increases in the level of recycling.
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5

Myhre, Marvin, Sitisaiyidah Saiwari, Wilma Dierkes, and Jacques Noordermeer. "RUBBER RECYCLING: CHEMISTRY, PROCESSING, AND APPLICATIONS." Rubber Chemistry and Technology 85, no. 3 (September 1, 2012): 408–49. http://dx.doi.org/10.5254/rct.12.87973.

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ABSTRACT For both environmental and economic reasons, there is broad interest in recycling rubber and in the continued development of recycling technologies. The use of postindustrial materials is a fairly well-established and documented business. Much effort over the past decade has been put into dealing with of end-of-life tires from landfills and vacant fields. It is only in the last few years that more business opportunities for recycled rubber have come to the forefront. Reclaiming rubber has gained increasing interest, more so in Europe than in North America. In those areas, much work has been done to refine the processes used. The major form of recycled rubber is still ground rubber. This is produced either by cryogenic, ambient, or wet grinding. The material is then used neat with sulfur/curatives, binders, or cements. The binders are normally moisture curable urethanes, liquid polybutadienes, or latex to produce items such as mats, floor tiles, and carpet undercushion. Recycled rubber is still used as tire derived fuel, but less so than 10 years ago. Another outlet is as an additive to asphalt. Recycled rubber can be used in the plastics industry, for which much development is being done. Large particle size ground rubber or chips are used in civil engineering applications, landscaping, or artificial turf. In terms of applications, most use is outside of the conventional rubber industry. Cost factors are still addressed in the tire industry. As of 2012, approximately 8–10% recycled material is used in tires. The biggest obstacles to further adaption are safety factors and property loss. Better methods are needed for treating or modifying the rubber surface and for regenerating the rubber through devulcanization. Devulcanization gives the highest quality recycled material in terms of processing and properties. However, shortcomings to devulcanization are reduced process safety and odorous chemicals that are required at present.
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6

SHIBATA, HIROMI. "Recycling and processing of industrial wastes." Shigen-to-Sozai 112, no. 6 (1996): 375–78. http://dx.doi.org/10.2473/shigentosozai.112.375.

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7

SATO, NOBUAKI. "Material processing and recycling by halogenation." RESOURCES PROCESSING 41, no. 2 (1994): 81–84. http://dx.doi.org/10.4144/rpsj1986.41.81.

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8

Zaharescu, Traian, Ludmila I. P. Kayan, Marius Eduard Lungulescu, Declerc F. Parra та Ademar B. Lugão. "EPDM recycling assisted by γ-processing". Iranian Polymer Journal 25, № 8 (16 липня 2016): 725–30. http://dx.doi.org/10.1007/s13726-016-0460-6.

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9

Ertuğ, Burcu. "Processing of Electronic Glass Scrap Recycling." American Chemical Science Journal 4, no. 5 (January 10, 2014): 657–63. http://dx.doi.org/10.9734/acsj/2014/8939.

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10

Wiśniewska, Paulina, Aleksander Hejna, and Mohammad Reza Saeb. "Recycling and Processing of Waste Materials." Materials 16, no. 2 (January 5, 2023): 508. http://dx.doi.org/10.3390/ma16020508.

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11

Liu, Guang Fu, and Tian Yi. "German Textile Waste Recycling Industry Processing and its Implications in China." Applied Mechanics and Materials 651-653 (September 2014): 1345–48. http://dx.doi.org/10.4028/www.scientific.net/amm.651-653.1345.

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Анотація:
Textile recycling can save resource and energy, as well as make huge economic benefits. Under the background of recycling economy, it is imperative to build textile recycling and reuse system in China, as there are many problems in Chinese textile waste recycling market. This paper introduces the background of textile waste recycling and explores the detail of advanced textile recycling mode in Germany as a case study, through which the author points out that we can learn from the German mode and choose Yangtze River Delta as a pilot area to establish the textile waste recycling system.
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12

Dorofeeva, N. L., and A. P. Vikulowa. "Recycling methods." XXI Century. Technosphere Safety 7, no. 1 (March 30, 2022): 21–25. http://dx.doi.org/10.21285/2500-1582-2022-1-21-25.

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Анотація:
The paper addresses the issues of recycling, which contributes to the environment protection. Recycling contributes to the use and circulation of industrial or household waste, or its conversion into energy. Recycling is a labor-intensive and energy-intensive process which can reduce the volume of primary raw materials used, the level of air, water and soil pollution. There are different processing technologies for each type of raw material: metals are melted; waste paper is crushed, dissolved and cleaned; plastic is sorted, foreign objects are removed and crushed. The method of removal and subsequent recycling of waste can have a positive impact on the environment pollution. Safety of the most common methods of waste disposal, such as burning, burial and composting, for humans and the environments was analyzed. It is difficult to select a recycling method, since each one has both advantages and disadvantages. Separate collection of household waste and pre-sorting make it possible to reuse most materials. The development of processing factories and enterprises can reduce the area of landfills.
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13

Goncharova, A. O., and S. D. Burlaka. "ANALYSIS OF THE PROBLEM OF OIL SLUDGE UTILIZATION AND PROCESSING." Chronos 7, no. 9(71) (October 13, 2022): 64–65. http://dx.doi.org/10.52013/2658-7556-71-9-12.

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Анотація:
The problem of recycling and recycling of industrial waste is very relevant at the present time. A large amount of land resources is being alienated for waste storage. Many wastes contain pollutants that are dangerous to the environment and humans. A reasonable approach to the use of modern methods of recycling secondary waste, their combination will bring us closer to solving this complex problem. The article discusses the current problems of recycling and recycling of waste from the petrochemical industry. The main tasks that enterprises need to implement in order to successfully solve the problem of processing the resulting oil sludge are studied.
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14

Pan, Qi, Feng Wang, and Hai Zhen Yang. "Cost-Benefit Analysis and Optimization of Semiconductor Processing Water Recycling Strategy." Applied Mechanics and Materials 71-78 (July 2011): 2772–77. http://dx.doi.org/10.4028/www.scientific.net/amm.71-78.2772.

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In this study, cost-benefit analyses based on life cycle assessment is applied to optimize the recycling of processing water for semiconductor factories. A representative 8-inch semiconductor wafer manufacturing plant is selected and seven existing or potential processing water-recycling sources were set, reverse osmosis (RO) reject, ultrafilter (UF) reject, multimedia filter (MMF), on-line analyzer drain, cation/anion (C/A) filter and merry-go-round (MGR) filter backwash water (including C/A sensor drain), wafer process organic drain and wafer process inorganic drain, marked as point 1 to 7, respectively. To sort the water-recycling sources in ascending order of the results of life cycle cost analyses, they were point 4, 5, point 2, 3, point 1, 7 and point 6, with life cycle the cost about 100,000$, 350,000$, 1000,000$ and 2000,000$, respectively. The order changed when they were sorted by their unit recycling-water costs; that was point 1, 2, point 5, point 3, 4 and point 7, with the unit recycling-water costs 0.2$/ton, 0.3$/ton, 0.4$/ton and 0.5$/ton, respectively. The analyses also evaluated the water recycling practice for various assumed unit tap water price. The optimal processing water recycling strategies based were proposed and corresponding optimal water-recycling rates were 24%, 64%, 81%, and 85% for water price 0.373$/ton, 0.578$/ton, 0.75$/ton and 0.945$/ton, respectively.
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15

Et. al., Balwant Singh,. "Processing and Recycling of thermoplastic polymers: Current Scenario and Future Challenges." Turkish Journal of Computer and Mathematics Education (TURCOMAT) 12, no. 2 (April 11, 2021): 2744–53. http://dx.doi.org/10.17762/turcomat.v12i2.2303.

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Thermoplastic polymers are extensively utilized in electronics, aerospace, automobile and additive manufacturing industries due to low cost, low temperature processing and reusability. Thermoplastics of different grades and chemical structures arereadily available in the market They can be reusedand reshaped, and also can be manufactured with less weight proportion as compared to the metals and ceramics by providing same strength of material. As a result, the plastics products in the market are getting popular day by day with high demand of customized products due to inception of additive manufacturing technologies. In any case, the issue of recycling these materials is challenge due to enormous energy requirements and varying chemical composition of different polymers. There are both mechanical and financial issues that restrict the advancements in this field. The recycling process of polymers can be done by the four different ways such as primary recycling process, secondary recycling process, tertiary recycling process and quaternary recycling process which can be discussed in this systematic review with practical examples. The modifications and implementation of these polymer waste recycling techniques could help to reduce wastage and save material cost which would directly affect the economy of contemporary industries.
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16

Teipel, Ulrich, and Horst Krause. "PROCESSING OF TRINITROTOLUENE-WATER EMULSIONS FOR RECYCLING." International Journal of Energetic Materials and Chemical Propulsion 4, no. 1-6 (1997): 205–12. http://dx.doi.org/10.1615/intjenergeticmaterialschemprop.v4.i1-6.240.

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17

Hryn, H., O. Miazina, N. Miroshnichenko, and S. Hryn. "Recycling and processing of spent molybdenum catalysts." Ecological Sciences, no. 1(28) (2020): 159–64. http://dx.doi.org/10.32846/2306-9716/2020.eco.1-28.25.

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18

Samoilenko, Nataliia, Vadym Katenin, and Antonina Baranova. "PROCESSING AND RECYCLING OF PHOTOVOLTAIC SOLAR PANELS." Bulletin of the National Technical University «KhPI» Series: New solutions in modern technologies, no. 2(8) (June 15, 2021): 121–26. http://dx.doi.org/10.20998/2413-4295.2021.02.17.

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The steady tendency of increasing the installed capacity of solar power plants, which is accompanied by the gradual accumulation of solar panel waste, is analyzed. The main factors of negative impact on the environment and directly on human health from the production of solar photovoltaic panels and waste of these panels are identified. The scenarios of solar photovoltaic panels waste accumulation are analyzed, the specifics of waste generation and accumulation in the present and in the future are characterized. Taking into account the average service life of solar photovoltaic panels in 25 years, it is determined that the amount of waste will increase significantly in the period of 2030…2035, reaching a peak between 2040 and 2050. The type and composition of photovoltaic panels, which determine the essence of waste processing technology, are characterized. It is defined that today most research on waste recycling of solar photovoltaic panels focuses on the first generation of modules, which is associated with the scale of operation of these panels and sales markets. It was found that at present, the production of solar photovoltaic panels, which consumes primary natural materials, is characterized by nature intensity, and direct waste processing cannot meet the needs of the photovoltaic modules production. The objective necessity of carrying out large-scale extraction of minerals and use of precious metals before the period of highly efficient processing of waste solar photovoltaic panels, which would meet the demands of production, is substantiated. Modern tendencies in technological researches and developments of secondary processing of photovoltaic modules are considered. It is determined that as the volume of solar photovoltaic panels production and waste generation increases, the requirements for ensuring the environmental efficiency of waste processing and disposal technologies should be more stringent. This involves increasing the recycling degree of the waste’s main components, starting from 80…90 % and to the highest possible level. It is determined that at the same time with this tendency, it is expedient to develop technologies for recycling of non-recyclable parts of waste at present.
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19

McIntosh, A. F., and J. P. Oden. "Recycling Stacking Velocities for Better Seismic Processing." Exploration Geophysics 24, no. 3-4 (September 1993): 671–78. http://dx.doi.org/10.1071/eg993671.

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20

Vidal de Almeida, B., R. Marinho de Faria, A. Tarcizo de Oliveira Vieira, S. Nascimento Silva, and F. Vernilli. "Recycling of steelworks refractories: processing and properties." Ironmaking & Steelmaking 43, no. 10 (March 18, 2016): 775–79. http://dx.doi.org/10.1080/03019233.2016.1155007.

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21

Nagel, Christopher J., Claire A. Chanenchuk, Esther W. Wong, and Robert D. Bach. "Catalytic Extraction Processing: An Elemental Recycling Technology." Environmental Science & Technology 30, no. 7 (January 1996): 2155–67. http://dx.doi.org/10.1021/es9505457.

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22

Jungbauer, Alois, and Nicole Walch. "Buffer recycling in downstream processing of biologics." Current Opinion in Chemical Engineering 10 (November 2015): 1–7. http://dx.doi.org/10.1016/j.coche.2015.06.001.

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23

Kurta, Sergei A., Alex A. Volinsky, and Mykola S. Kurta. "Environmentally-friendly organochlorine waste processing and recycling." Journal of Cleaner Production 54 (September 2013): 150–56. http://dx.doi.org/10.1016/j.jclepro.2013.05.010.

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24

Valuev, D. V., A. A. Semenok, D. O. Kotova, and A. V. Valueva. "Prospects for of Processing Car Tires." Applied Mechanics and Materials 682 (October 2014): 75–79. http://dx.doi.org/10.4028/www.scientific.net/amm.682.75.

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Анотація:
This article analyzes the problem of recycling of used tires and-retired rubber products, which is of great ecological and economic importance for all developed countries. Nonrenewable natural oil feedstock necessitates the use of secondary resources with maximum efficiency, ie place in the mountains of garbage we could get a new one for our region industry - commercial recycling. This paper presents an overview of methods and technologies for disposal of tires in the world and ways of using waste in the form of dispersed materials.
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25

Popa, Cicerone Laurentiu, Costel Emil Cotet, Diana Popescu, Mihai Florin Solea, Simona Gheorghiţa Şaşcîm (Dumitrescu), and Tiberiu Dobrescu. "Material flow design and simulation for a glass panel recycling installation." Waste Management & Research: The Journal for a Sustainable Circular Economy 36, no. 7 (May 28, 2018): 653–60. http://dx.doi.org/10.1177/0734242x18775487.

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The current paper presents the design of a glass panels recycling flow and the method used for establishing the optimal processing installation architecture. In the solution provided in the current research, a novel approach centred on applying digital twinning in the design of the requested processing architecture is presented. It involves designing the virtual prototype of the diffused processing architecture and modelling the glass waste flow as a hybrid material flow. Dedicated analysis and simulation software is then used for establishing installation architecture and the specific parameters for each processing and transport capacity. The assessment of different processing scenarios by virtual modelling and simulations can also be used for exploring options to increase productivity and profit for other different recycling architectures. The main practical value of the study consists of creating the means to improve the waste recycling of automotive windshields, float glass or construction glass panels with metallic meshes, all representing categories of waste insufficiently recycled in Romania. The simulation results of the study were validated by tests made on the glass panel recycling installation. Also, a recovery glass rate of minimum 85% of the amount of waste loaded into the recycling system was achieved, obtaining a waste recycling quantity three times higher than initially anticipated.
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26

Zhan, Menglin, and Yan Chen. "Vehicle Company’s Decision-Making to Process Waste Batteries: A Game Research under the Influence of Different Government Subsidy Strategies." International Journal of Environmental Research and Public Health 19, no. 21 (October 23, 2022): 13771. http://dx.doi.org/10.3390/ijerph192113771.

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Анотація:
With the increase in the number of waste power batteries and the occurrence of related environmental problems, battery recycling is receiving extensive attention. Driven by economic benefits, many companies have begun to deploy the waste battery processing market and government subsidies also play an essential role in battery recycling. Considering the vehicle company outsources processing tasks or invests in research and development (R&D), this paper studies the optimal decision-making problem of the supply chain under government subsidy to the battery manufacturer or the battery manufacturer. The research finds that: (1) For the government, when the vehicle company outsources processing tasks, compared with subsidizing the vehicle company, the total recycling volume when subsidizing the battery manufacturer is higher. When the vehicle company invests in R&D, the total recycling volume under different government subsidy strategies is equal. (2) The vehicle company’s decision is only related to its processing costs; when the unit processing cost is low, the vehicle company’s profit under the strategy of investing in R&D is higher. However, when the unit processing cost is high, the profit of outsourcing processing tasks is higher. (3) With increase in unit subsidy and decrease in unit processing cost, the total recycling volume will increase. These findings can provide decision-making help for the government in formulating subsidy policies and the vehicle company in determining processing strategies in the future.
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27

Voloshina, І. V. "PROCESSING GARBAGE CONTAINING PLASTICS (REVIEW)." Thermophysics and Thermal Power Engineering 41, no. 3 (April 10, 2019): 90–98. http://dx.doi.org/10.31472/ttpe.3.2019.13.

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28

Zhou, Jian Mei. "Recycling Lanolin from Tannery Wastewater by Mixed Flocculation and Extraction Processing." Advanced Materials Research 347-353 (October 2011): 1113–16. http://dx.doi.org/10.4028/www.scientific.net/amr.347-353.1113.

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Анотація:
Using mixed flocculation and extraction method to recover the lanolin from Tannery Wastewater, and studied the process research. The result indicated that the recovery rate of lanolin can reached 92% by using aluminium sulfate (AS) and the polyacrylamide (PAM) mixed flocculation, hexane and cyclohexane mixed extraction. Comparing the main indexes and the infrared spectra of recycling lanolin with the industry level lanolin, the results indicated the main indexes of the recycling lanolin achieved the industry level standard, and both similar spectrogram showed the component and the structure of recycling lanolin are almost similar with industry level lanolin. Therefore the method used to deal with tannery wastewater recycling lanolin is practicable and effective.
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Druzhinina, Anastasiia, Antonina Golubeva, Eleonora Zhuravleva, Ekaterina Makarenko, and Anastasiia Nedomovnaya. "Project of Gasification plant for mechanized processing of household waste." E3S Web of Conferences 247 (2021): 01043. http://dx.doi.org/10.1051/e3sconf/202124701043.

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Humanity knows three ways to deal with waste: incineration, burial (landfills) and recycling. All the methods, except reuse and recycle, destroy nature and are dangerous for ecology and human health exactly. Each year Russians produce about 50 million tons solid waste, the most part of which goes to the landfills. National green projects are aimed to create visible eco-friendly system by awarding greenwashing projects with grants: landfills with sorting system, sorting centres without recycling facilities. Therefore, this study is aimed to discover recycling practices execute in Russia and suggest the project of gasification waste plant.
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30

Rudoy, Dmitry, Mary Odabashyan, Anastasiya Olshevskaya, Alexander Rybak, Daniil Kovalchuk, Natalya Kulikova, Alexey Prutskov, and Dzhuletta Sarkisian. "Methods for ensuring the processing and disposal of agricultural waste." BIO Web of Conferences 113 (2024): 05011. http://dx.doi.org/10.1051/bioconf/202411305011.

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Nowadays, the issue of processing and disposal of agricultural waste is becoming increasingly relevant. Agriculture has a serious impact on the environment, and pollution from waste from poultry and livestock farms is often associated with imperfect technologies and equipment used, as well as non-compliance with environmental standards. The purpose of this article is to explore effective ways to process and dispose of agricultural waste. We will look at different methods of recycling and recycling agricultural waste, and also offer recommendations for optimizing this process. Keywords. Agricultural waste, recycling technologies, waste processing, livestock waste, crop waste, pesticide disposal.
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31

Baptista-Neto, Álvaro, Juliana Conceição Teodoro, Luiz Claudio Macedo Cassiano Filho, Alberto Colli Badino, and Carlos Osamu Hokka. "Comparisons between continuous and batch processing to produce clavulanic acid by Streptomyces clavuligerus." Brazilian Archives of Biology and Technology 48, spe (June 2005): 97–104. http://dx.doi.org/10.1590/s1516-89132005000400012.

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The aim of the present work was to compare CA production in continuous culture with and without cell recycling and in batch process by Streptomyces clavuligerus. Continuous cultivations with high cell concentration using cell recycling were performed utilizing a hollow fiber ultrafiltration module to separate cells from the filtrate broth. The continuous cultures without cell recycling and the batch cultivations were performed conventionally. The highest productivity was attained in the continuous cultivation with cell recycling (22.2 mg.L-1.h-1). The highest CA concentration was obtained in the batch process (470 mg.L-1.h-1).
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32

Suwarno, Istiqomah Farah Novita Devi, Rusmiati, and Rachmaniyah. "PENGARUH GAS HIDROGEN SULFIDA (H2S) TERHADAP KELUHAN SUBYEKTIF PETUGAS PENGOLAHAN SAMPAH DI PUSAT DAUR ULANG JAMBANGAN SURABAYA." Gema Lingkungan Kesehatan 20, no. 2 (July 31, 2022): 117–23. http://dx.doi.org/10.36568/gelinkes.v20i2.14.

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The Jambangan Recycling Center (PDU) in Surabaya is a waste management site that applies the 3R principles, namely Reuse, Reduce, Recycle. The amount of waste that comes in every day is 5-6 tons. The waste processing officer complained of subjective complaints in the form of influenza, cough, sore throat and chest pain. The purpose of the study was to determine the effect of H2S gas on subjective complaints of waste processing officers at the Jambangan Recycling Center Surabaya. This research is an analytic observational research with a cross sectional approach. This research was conducted at the Jambangan Recycling Center. Sampling of respondents and ambient air was carried out by saturated sampling with a total population and sample of 27 people. Data collection techniques in this study used measurements, observations, and interviews. Data analysis using SPSS application with Spearman Correlation Test. The results showed that the average level of Hydrogen Sulfide (H2S) in the Jambangan Recycling Center Surabaya was 0.00054 ppm which was included in the eligible category according to the East Java Governor Regulation Number 10 of 2009. This study also showed that 27 waste processing officers who 2 people experienced severe complaints, 25 people had mild complaints, and there were no waste processing officers who had no complaints. The conclusion of the study is that there is no effect between levels of Hydrogen Sulfide on subjective complaints of waste processing officers at the Jambangan Recycling Center Surabaya (P = 0.336) so it is recommended to the relevant agencies to monitor air quality regularly. Waste processing officers are also advised to use personal protective equipment when in the Surabaya Jambangan Recycling Center environment.
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33

HINO, Junzo. "Recycling. Thermal Processing Technology of Shredder Residue. Incineration." Shigen-to-Sozai 113, no. 12 (1997): 1032–35. http://dx.doi.org/10.2473/shigentosozai.113.1032.

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34

Doriomedov, M. S., A. V. Petrov, М. I. Daskovskiy, and S. Yu Skripachev. "Processing reinforcing filler from PCM for recycling purposes." Proceedings of VIAM, no. 8 (2016): 12. http://dx.doi.org/10.18577/2307-6046-2016-0-8-12-12.

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35

Friedrich, Bernd. "Sustainable Utilization of Metals-Processing, Recovery and Recycling." Metals 9, no. 7 (July 10, 2019): 769. http://dx.doi.org/10.3390/met9070769.

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36

Henderson, Brooke. "POLICY AND SCIENCE IN POULTRY PROCESSING RESIDUALS RECYCLING." Proceedings of the Water Environment Federation 2000, no. 1 (January 1, 2000): 731–42. http://dx.doi.org/10.2175/193864700785378202.

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37

OWADA, Shuji. "Mineral Processing Technology Applied to the Resources Recycling." Journal of the Society of Powder Technology, Japan 32, no. 6 (1995): 401–7. http://dx.doi.org/10.4164/sptj.32.401.

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38

Casella, George, and Christian P. Robert. "Post-Processing Accept-Reject Samples: Recycling and Rescaling." Journal of Computational and Graphical Statistics 7, no. 2 (June 1998): 139. http://dx.doi.org/10.2307/1390810.

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39

Nikolaeva, V. M., and A. I. Borisov. "The technology of processing and recycling organic waste." IOP Conference Series: Earth and Environmental Science 548 (September 2, 2020): 052035. http://dx.doi.org/10.1088/1755-1315/548/5/052035.

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40

Medina, Eduardo, Pedro García, Concepción Romero, and Manuel Brenes. "Recycling preservation solutions in black ripe olive processing." International Journal of Food Science & Technology 46, no. 8 (June 6, 2011): 1685–90. http://dx.doi.org/10.1111/j.1365-2621.2011.02671.x.

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41

Dąbrowska, Ewa. "Recycling utterances: A speaker's guide to sentence processing." Cognitive Linguistics 25, no. 4 (November 1, 2014): 617–53. http://dx.doi.org/10.1515/cog-2014-0057.

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AbstractIn recent years, there has been a growing consensus that speakers store large numbers of preconstructed phrases and low-level patterns, even when these can be derived from more abstract constructions, and that ordinary language use relies heavily on such relatively concrete, lexically specific units rather than abstract rules or schemas that apply “across the board”. One of the advantages of such an approach is that it provides a straightforward explanation of how grammar can be learned from the input; and in fact, previous work (e.g. Dąbrowska and Lieven 2005) has demonstrated that the utterances children produce can be derived by superimposing and juxtaposing lexically specific units derived directly from utterances that they had previously experienced. This paper argues that such a “recycling” account can also explain adults' ability to produce complex fluent speech in real time, and explores the implications of such a view for theories of language representation and processing.
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42

Casella, George, and Christian P. Robert. "Post-Processing Accept-Reject Samples: Recycling and Rescaling." Journal of Computational and Graphical Statistics 7, no. 2 (June 1998): 139–57. http://dx.doi.org/10.1080/10618600.1998.10474767.

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43

Buchan, R., and B. Yarar. "Recovering plastics for recycling by mineral processing techniques." JOM 47, no. 2 (February 1995): 52–55. http://dx.doi.org/10.1007/bf03221410.

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44

Veit, Hugo M., Carolina C. de Pereira, and Andréa M. Bernardes. "Using mechanical processing in recycling printed wiring boards." JOM 54, no. 6 (June 2002): 45–47. http://dx.doi.org/10.1007/bf02701850.

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45

Zaharescu, Traian, Ludmila I. P. Kyan, Marius Eduard Lungulescu, Duclerc F. Parra та Ademar B. Lugao. "Erratum to: EPDM recycling assisted by γ-processing". Iranian Polymer Journal 26, № 1 (23 грудня 2016): 91. http://dx.doi.org/10.1007/s13726-016-0494-9.

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46

Helling, Christoph, and Jochen Strube. "Future Processing and Recycling Strategies for Rare Earths." Chemie Ingenieur Technik 85, no. 8 (June 10, 2013): 1272–81. http://dx.doi.org/10.1002/cite.201200214.

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47

Shofiyah, Rohimatush, and Irawati Irawati. "Pengolahan Sampah Polimer Termoplastik dan Termoset di Lingkungan Bank Sampah Induk Kabupaten Jember." Jurnal Komunitas : Jurnal Pengabdian kepada Masyarakat 6, no. 2 (January 18, 2024): 180–90. http://dx.doi.org/10.31334/jks.v6i2.3548.

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The Jember Regency Main Garbage Bank has the role of fostering and coordinating the Unit Garbage Bank in the Jember Regency area. BSI had several problems in terms of how to sort polymer waste and the need for technological tools for processing plastic polymer waste. The purpose of the PKM activity is to convey knowledge, information and technology for processing plastic polymer waste. The socialization that has been delivered is related to thermoplastic and thermoset polymer waste processing technology based on physical, chemical, technological and mechanical properties, as well as management and marketing strategy for waste bank products. After interviews with BSI and BSU management, discussions with participants, mentoring, and evaluation with partners; The PKM team presented that a Garbage Bank in the city of Jember really needs a plastic polymer waste counting tool to realize the Zero Waste program, increase economic value, usability and aesthetic value. Processing of plastic polymer waste has several methods, namely; recycling plastic waste into handicraft products, turning plastic waste into pellets, processing plastic waste into; fuel oil, brick mixture, and asphalt, recycling process, namely; Hydrogenation, Glycolysis, Methanolysis, Hydrolysis, Gasification, Pyrolysis and Catalytic Conversion, Recycling methods, namely (primary, secondary, tertiary and quarter) recycling.
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48

Chernyi, S. A. "Secondary Resources of Rare Еarth Мetals". Ecology and Industry of Russia 24, № 9 (1 вересня 2020): 44–50. http://dx.doi.org/10.18412/1816-0395-2020-9-44-50.

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The article provides an overview of the main existing methods for recycling rare earth metals from various types of waste. It was noted that the demand for rare-earth metals is increasing annually due to the growth of advanced technologies, mainly in the sectors of electronics, power engineering and photonics. It has been established that in countries producing final products of high processing, the chemical-technological processes of processing goods that have worked out their life cycle, and, first of all, fluorescent lamps, NdFeB magnets from electronic devices, and nickel-metal hydride (NiMeH) batteries containing rare earths are most quickly created. The most profitable and recycling option is the reuse of products containing rare-earth metals, however, such technologies are applicable for a narrow range of waste. Another important area of REM recycling is the processing of industrial waste. For countries with developed mining and chemical industries, mining processing technologies are attractive. It is shown that for Russia, more appropriate are schemes for the disposal of industrial waste, primarily waste from the production of apatite concentrate. The main problems of the development of REM recycling are identified: low content and dispersion of rare earths in waste; the presence of impurities that impede the extraction of valuable components and the toxicity of the used recycling schemes.
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49

Perez Bay, Andres E., Devon Faulkner, John O. DaSilva, Tara M. Young, Katie Yang, Jason T. Giurleo, Dangshe Ma, et al. "A Bispecific METxMET Antibody–Drug Conjugate with Cleavable Linker Is Processed in Recycling and Late Endosomes." Molecular Cancer Therapeutics 22, no. 3 (January 11, 2023): 357–70. http://dx.doi.org/10.1158/1535-7163.mct-22-0414.

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Abstract Most antibody–drug conjugates (ADC) approved for the treatment of cancer contain protease-cleavable linkers. ADCs that traffic to lysosomes traverse highly acidic late endosomes, while ADCs that recycle to the plasma membrane traffic through mildly acidic sorting and recycling endosomes. Although endosomes have been proposed to process cleavable ADCs, the precise identity of the relevant compartments and their relative contributions to ADC processing remain undefined. Here we show that a METxMET biparatopic antibody internalizes into sorting endosomes, rapidly traffics to recycling endosomes, and slowly reaches late endosomes. In agreement with the current model of ADC trafficking, late endosomes are the primary processing site of MET, EGFR, and prolactin receptor ADCs. Interestingly, recycling endosomes contribute up to 35% processing of the MET and EGFR ADCs in different cancer cells, mediated by cathepsin-L, which localizes to this compartment. Taken together, our findings provide insight into the relationship between transendosomal trafficking and ADC processing and suggest that receptors that traffic through recycling endosomes might be suitable targets for cleavable ADCs.
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50

Yakovleva, E., and E. Titova. "Recycling of forestry waste." IOP Conference Series: Earth and Environmental Science 875, no. 1 (October 1, 2021): 012045. http://dx.doi.org/10.1088/1755-1315/875/1/012045.

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Abstract The article examines the current state of wood waste recycling in the interests of ensuring sustainable development and minimizing the impact on climate change. Classification of wood waste based on the stage of the life cycle of a wood product has been carried out. The problem of organization of wood waste disposal and processing is relevant both directly in the forest industry and in the process of using wood since this leads to the preservation of primary wood material and significantly reduces the volume of deforestation. During the study methods of wood waste recycling and options for complex recycling have been identified. A wood waste recycling scheme which includes such stages as collecting wood waste, deep wood processing and involvement in secondary circulation has been developed. An econometric analysis of correlation between current environmental costs and indicators of economic activity associated with the use of wood waste on innovative basis has been carried out. It has been concluded that there is a tight relationship between the costs of environmental protection and the selected factors. The research results can be used in the development of wood waste recycling schemes by various economic entities of timber and woodworking sectors.
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