Recycling sustainability of waste paper industry in Beijing City: An analysis based on value chain and GIS model
Introduction
There is a large amount of paper products consumed by the modern society, resulting in enormous paper waste all around the world. Although recycling technologies of waste paper were well-developed due to their advantages of energy & material saving and pollution reduction, comparing to primary paper production (Wang et al., 2012, Bajpai, 2014), a large amount of waste paper was disposed as municipal solid waste (MSW). According to the report by World Bank, total amount of global MSW generated in 2016 was 2.01 billion tons, while the quantity of paper waste accounted for 17%, about 340 million tons per year (Kaza et al., 2018). There are global-, regional- and national- scale studies concerning about waste paper recycling. Van Ewijk et al. (2018) firstly estimated the recovery potential of waste flows in the global paper life cycle, revealing that the recycled input ratio can increase from 38% to 67–73% in an ideal scenario. The European Paper Recycling Council (2018) estimated that 72.3% of paper waste had been recycled in 2017 in Europe. In the Directive 2008/98/EC, EU emphasized to use “recovery potential” as the target for the classification, collection, and recycling of household solid waste (European Parliament, 2008). The recycling rate of waste paper in Japan was around 80% in 2018, according to Japanese Waste Paper Recycling Promotion Center (2019). China led the world in the amount of recycled waste paper during the last ten years, 57.74 million tons of paper pulp were produced from waste paper in China in 2018, in which 8.76 million tons were imported from the developed countries such as the US and Japan (China Paper Associtation, 2019).
In China, the informal sector played an important role for recycling paper waste. Individual waste pickers and small private companies collected and traded paper waste for pursuing profits from the recycling market (Kashyap and Visvanathan, 2014, Souza Lima and Mancini, 2017, Tong and Tao, 2016, Wilson et al., 2006). Steuer et al. (2017) investigated the recycling industry in Beijing and found that the informal recycling system was still the main contributor to MSW recycling. In recent years, the collecting and transporting cost of waste paper, also known as the reverse logistics cost, kept increasing due to the sharply rise of land rent, labor, and fossil fuel prices, thus bringing great challenges to waste paper recycling industry (Steuer et al., 2017, Zhou and Zhou, 2015). As a result, domestic paper waste recycling rate in China was only 47% in 2017 and its growth rate dropped from 20% in 2005 to −13% in 2017, which was much slower than expectation (China Paper Associtation, 2019). Meanwhile, the waste paper recycling industry in China imposed to the challenge due to the new Waste Import Ban, i.e., the unsorted waste paper was not allowed to be imported to China since 2018 (Tan et al., 2018). According to the latest statistics, the amount of pulp produced by imported waste paper decreased by around 30% in 2018, throwing great impact on the global waste paper recycling stream (Qu et al., 2019). Developed countries need to find new target countries or strengthen domestic capacity to dispose their paper waste, on the other hand, China’s paper industry will be more dependent on its domestic recycling. To promote domestically waste recycling, China has been put unprecedented efforts on the source separation of MSW. According to the plan of Chinese government, all of the prefecture-level cities should implement a MSW source separation system and promote material recycling by the end of 2025. Performance of MSW source separation is set as a key indicator for evaluating achievements of local government, while a large sum of financial fund has been invested to promote MSW source separation.
Economic sustainability assessment of recyclables, e.g., waste paper, is fundamental for designing incentive policies, promoting source separation, and establishing a sustainable MSW management system (Wang et al., 2015). Value chain model (VCM) has been widely applied for assessing the economic sustainability of waste recycling. Mueller (2005) applied VCM to examine the cardboard recycling in Durban, South Africa, by constructing analyzing model involving informal sectors and other stakeholders. It showed that local policies should support the cardboard collectors due to the value they created. Pati et al. (2008) established a model for analyzing the reverse logistics distribution networks of paper recycling in India and examined the cost reduction effect in such networks. Fei et al. (2016) applied VCM for analyzing the formal and informal recycling systems in Suzhou city. Pishvaee et al. (2010) used VCM to illustrate plastic recycling in Northern Europe, indicating that the main obstacle was the collecting and transporting costs. Beretta et al. (2017) discussed the environmental impacts in different stages of the food value chain in Switzerland and found that 60% of the total climate impacts was caused in the end of food value chain. Geographic factors are vital to determine the economic sustainability of recycling, such as waste generation density, transport distance, and logistic structure, etc. in different urban areas. For instance, spatial layout of sorting and recycling sites is one of the key factors to affect the transport cost of waste paper recycling. Previous VCM studies generally viewed the city as a “black box”, the geographic factors inside the city were rarely discussed. Geographic information system (GIS) was adopted for analyzing waste recycling and MSW management. López Alvarez et al. (2008) applied GIS tool to optimize the waste paper and cardboard collection process for small businesses. Based on GIS analysis on population density and territorial, 59% of the shops, which generate 82% of the waste paper, were selected to cover recycling services, thus improving the recycling efficiency and obtaining high quality paper waste. Karadimas and Loumos (2008) established a GIS-based model to estimate the amount of MSW generation and estimate of the optimal number of waste bins and their allocation. Rada et al. (2013) used a Web-GIS tool to improve MSW management system in Italy and China. Nevertheless, very few of those GIS-based researches discussed how spatial distribution of recycling facilities influences the economic sustainability of waste paper recycling.
This work aims at revealing the economic mechanism and filling the data gap in waste paper recycling for mega cities. A methodology integrated VCM and GIS is developed to examine the value flows along with the waste paper recycling stream in Beijing city. Multiple stakeholders were investigated to obtain data from both formal and informal recycling sectors. Recycling sustainability of waste paper is analyzed with a resolution of 1 km2 grid in 2015 and 2018, the recycling cost and benefit, as well as the index of recycling sustainability (IRS) of waste paper in each grid is estimated herein. Scenarios concerning the increase of recycling cost are analyzed, to examine the possible changes in the future. Based on the results, policy recommendations are put forward for promoting a more sustainable paper waste recycling system.
Section snippets
Studied case
Beijing, the capital of China, with an area of 16,421 km2 and population of 21.54 million, is selected as the studied case. In 2017, the average quantity of MSW generation in Beijing was 24,700 tons per day (Ministry of Ecology and Environment, 2018). According to the estimation by Linzner and Salhofer (2014), the amount of recycables collected by the informal sector accounted for 21–42% of total MSW generation in Beijing. Although the informal sector diverted a considerable sum of recyclables
Stakeholders in waste paper recycling
The recycling process of waste paper is not only material flow processes, but also value flow processes among different stakeholders. According to the fieldwork, stakeholders in waste paper recycling in Beijing include: (1) waste paper generators, e.g., residents, enterprises, public institutions, etc.; (2) individual waste pickers, cleaners of communities, and workers of MSW transfer station, etc.; (3) middle recyclers (or middle men), who normally locate at the community or commercial space,
Recycling sustainability of waste paper and its influential factors
The VCM has been widely applied for analyzing the waste recycling system (Fei et al., 2018, Steuer et al., 2017, Van Ewijk et al., 2018), however, previous studies always took the whole city as a basic analyzing unit, while the reverse logistic networks and their cost inside city were largely ignored (Goldstein, 2017, Tong and Tao, 2016). In this work, the “black box” of waste paper recycling inside the city is opened to some extent, for the first time, and the IRS of waste paper for each
Conclusions
A methodology for assessing city-level recycling sustainability and its spatial distribution is applied in this work, paper recycling sustainability of Beijing, China, in 2015 and 2018 are examined, and the future trend of waste paper recycling is analyzed herein. In the past three years, the value chain of waste paper recycling in Beijing was demonstrated to be economically sustainable, due to a well balance between the costs and benefits of the recycling industry, with a dominated
Declaration of Competing Interest
The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.
Acknowledgements
This research was supported by grants from the Beijing Natural Science Foundation (9182018), National Key R&D Program of China (2018YFC1903601), National Natural Science Foundation of China (Grant No. 41871206), and Youth Innovation Promotion Association CAS (2017061). We thank all the interviewees for sharing their ideas and experiences with us during our field studies and all the anonymous reviewers who help us to improve the paper.
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