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Article

Characteristics and Resource Recovery Strategies of Solid Waste in Sewerage Systems

by
Xiaohui Sun
1,
Junpei He
1,
Wei Lv
2,*,
Silin Wu
3,
Yongshen Peng
1,
Yuansheng Peng
1,
Jianbo Fei
1,* and
Zezhou Wu
1
1
Shenzhen Key Laboratory of Green, High-Efficiency, Intelligent Construction of Underground Metro Station, College of Civil Engineering, Shenzhen University, Shenzhen 518060, China
2
Shenzhen Shenshui Ecological & Environmental Technology Co., Ltd., Shenzhen 518060, China
3
School of Architecture and Civil Engineering, Jiangsu University of Science and Technology, Zhenjiang 212100, China
*
Authors to whom correspondence should be addressed.
Sustainability 2023, 15(2), 1662; https://doi.org/10.3390/su15021662
Submission received: 13 December 2022 / Revised: 9 January 2023 / Accepted: 11 January 2023 / Published: 14 January 2023
(This article belongs to the Special Issue Construction and Demolition Waste Management for Carbon Neutrality)
Browse Figures
Versions Notes

Abstract

:
Sewerage systems-related solid waste accumulates in considerable quantities in urban water systems, including rainwater drainage pipes, pumping stations, grease traps, grit chambers, and septic tanks. Traditional management methods, such as sanitary landfilling, incineration, and composting, not only endanger the environment but also consume a significant amount of land. To address this problem, a variety of waste was collected from a terminal and different facilities in sewerage systems, and the characteristics of solid waste were tested and analyzed. The corresponding appropriate approaches to resource recovery strategies were proposed in detail. The solid waste in the wastewater treatment plant (WWTP) contains low organic matter content and a certain quantity of heavy metals, making recycling difficult. Before the solid waste enters the WWTP, the strategy of pre-sorting, treating, and recycling the solid waste is worth recommending. The waste was divided into three categories based on its nature, and corresponding resource utilization strategies were proposed. A small part of solid waste that is not suitable for pre-recycling can be discharged normally and enter the WWTP for treatment. This paper provides a scientific basis for the green resource utilization of solid waste in the field of sewerage systems in developing countries.

1. Introduction

In recent years, a significant amount of solid waste has accumulated in urban water service pipeline networks and facilities every day [1]. Examples include solid waste from rainwater drainage pipes, pumping stations, grease traps, grit chambers, and septic tanks. It seriously affects the normal operation of facilities in sewerage systems. Daily emptying operations are necessary, which leads to the eventual formation of a large amount of solid waste [2,3]. In developing countries, the solid waste in sewerage systems is basically not used as a resource. The traditional method of disposal of solid waste from facilities in developing countries is to transport it to landfills. Transportation and landfilling of such solid waste may pose an environmental risk due to its complex composition and a certain quantity of pollutants [4,5]. Traditional treatment and disposal methods are no longer viable due to the steady increase in the requirements for environmental protection, and recycling methods suitable for solid waste in developing countries need to be studied.
Research on the disposal and resource utilization of similar solid waste has been extensively conducted, mainly focusing on solid waste generated during the construction process. Table 1 summarizes the treatment purposes and methods of similar solid waste. The treatment purpose of solid waste can be basically divided into three categories, including reduction, resource utilization, and harmless treatment. According to the nature of solid waste and engineering requirements, different methods can be adopted for disposal. For example, when the organic matter content of solid waste is high, thermochemical treatment or anaerobic digestion can be considered to convert it into resources such as natural gas and fertilizer [6,7,8]. If the solid waste has good initial mechanical properties, it can be modified by adding lime, cement, fly ash, and other materials to be used as road construction materials [9,10]. If the solid waste contains certain harmful components, it is necessary to remove or stabilize these substances, usually using methods such as solidification, stabilization, thermal treatment, separation, and extraction [11,12,13].
Since the solid waste generated during the construction process and the solid waste generated from sewerage systems have similar characteristics, these studies and strategies can be used as references. The solid waste from sewerage systems contains a certain amount of organic matter, which has the potential to be converted into useful products such as biogas or other energy-rich compounds [6,7,8]. Solid waste also contains some inorganic components, such as clay, gravel, and fine sand, which can be used as building materials after screening and separating [14,15]. Solid waste contains significant levels of nutrients necessary for plant growth, such as nitrogen, phosphorous, potassium, and organic matter. Therefore, when properly treated, it can be used as a soil conditioner and medium-grade fertilizer [16]. If solid waste from sewerage systems is properly sorted, it can not only solve the problem of its reduction and disposal, but also generate a lot of valuable resources. However, because solid waste lacks systematic management and strict supervision in developing countries, it is difficult to handle properly. The nature of solid waste from different facilities in sewerage systems is complex and variable. This has made the resource utilization of most solid waste in developing countries difficult. To achieve efficient resource utilization, it is critical to investigate the physical and chemical properties of solid waste and to propose potential resource recovery methods for solid waste in developing countries.
Table
Table 1. Overview of the treatment and resource utilization of similar solid waste.
Table 1. Overview of the treatment and resource utilization of similar solid waste.
Purpose of TreatmentProcessing ThoughtsMethods
ReductionReduce the generation of solid wasteUsing green building materials [17,18]
Reduce the volume after solid waste generationFlocculation, sedimentation, and dewatering [19,20,21]
Resource utilizationReuse as road building materialsCrushing, screening, magnetic sorting, and removal of light materials [9,10]
Modified by adding lime, cement, fly ash, silica fume, blast furnace slag, steel slag, rice husk ash, etc. [22,23,24,25,26,27]
Reuse as concrete, brick, and ceramicHeating and compressing [28,29,30]
Converted to materials such as natural gas and fertilizerThermochemical treatment or anaerobic digestion [6,7,8]
Harmless treatmentRemove or stabilize harmful substancesSolidification or stabilization [11]
Thermal treatment [12]
Separation or extraction [13]
Based on the above issues, this paper investigated the solid waste generated from different sources of sewerage systems in Shenzhen, China, including solid waste from a sewerage system terminal and representative sites of various sewerage system facilities. The physical and chemical properties of solid waste from various sources in sewerage systems were tested. The corresponding treatment measures and strategies for solid waste in sewerage systems in developing countries were proposed.

2. Materials and Methods

2.1. Sampling Location

Sewerage systems are composed of various sewerage facilities and terminals. Terminals refer to wastewater treatment plants (WWTP), while sewerage facilities include rainwater drainage pipes, pumping stations, grease traps, grit chambers, septic tanks, etc. In this study, a variety of solid waste from various sources was collected, including the solid waste from a terminal of sewerage systems and six representative types of solid waste from various facilities in sewerage systems. The sampling location of the terminal of sewerage systems is at the Luofang Water Purification Plant, and the sampling locations of the six different facilities in sewerage systems are at the pipeline network close to the construction site and cuisine street next to the bus stop at the Gangxia Metro Station on Fuhua Road, the pumping station at the Xinzhou Pumping Station, the grease trap and grit chamber close to the Bagualing Refuse Transfer Station, and the septic tank close to Yu Nan Road. The sampling locations shown in Figure 1.
The samples were collected in pre-cleaned plastic drums and transported to the laboratory at a low temperature. The samples were given names based on the sampling locations, such as LWPP (the samples from Luofang Water Purification Plant), RDP-Co (the sample from the rainwater drainage pipes near the construction site), RDP-Cu (the sample from the rainwater drainage pipes near the cuisine street), PS (the sample from the pumping station), GT (the sample from the grease trap), GC (the sample from the grit chamber), and ST (the sample from the septic tank). The samples named LWPP include waste separated at various processes, including coarse aggregates, fine aggregates, grille residue, sewage, and substrate.

2.2. Solid Waste Characterization

In order to better propose strategies for recycling solid waste of sewerage systems, it is necessary to test its physical and chemical properties. As shown in Table 2, different methods have been adopted to examine the relevant properties of solid waste. In Table 2, the grille residue and sewage refer to the samples of LWPP.

2.3. Codes and Standards

In order to propose a recovery strategy for the solid waste from sewerage systems, the following codes and standards were used to analyze and evaluate its basic properties, as shown in Table 3. Since the sampling location and potential utilization are all in China, the codes and standards selected in this paper are from China.

3. Results

3.1. Solid Waste Characterization of the Terminal

In order to improve the resource utilization of the samples from the Luofang Water Purification Plant, the composition and properties of the LWPP were examined. Figure 2 shows the composition of LWPP. The mass content of each substance was quantified as a percentage of the total mass. The main component of the separated waste varied, with the coarse aggregates containing mainly stones (60–73%), and other waste such as construction waste (15–30%), foam (5–8%), and slurry (5.9%). The main component within the fine aggregates is sand (81.6%), with other impurities (5.6%) also interspersed. Within the grille residue, there are dead branches and leaves (20–27%), household waste (8–25%), and other organic impurities (64–75%). There is also sewage and substrate produced during the separation process, which is a mixture of water, slurry, and impurities.
In addition, physical and chemical property tests were carried out on each of the separated waste to determine the pH, water content, heavy metals, and organic matter in order to lay the foundation for the subsequent determination of the approach to resource utilization. The properties of coarse aggregates, fine aggregates, grille residue, sewage, and substrate are shown in Table 4 and Table 5, and Figure 3. The aggregates, grille residue, and substrate all had neutral pH (7–9), no PAHs were found, and the bacteria content was comparable to that of common soil (1 × 106~1 × 107 pcs/ g) [47]. The sewage contains a high level of NH3-N (334 mg/L), which does not meet the minimum requirement (NH3-N ≤ 8 mg/L) of the standard GB 3838-2002 [41].
In addition, it can be seen from Figure 3 that all the separated waste contains a certain quantity of heavy metals, and the prospect of resource utilization may be limited. The coarse aggregates contain a high content of Cd (6.5 mg/kg) and the fine aggregates contain a high level of Hg (5.68 mg/kg) and Cd (9.1 mg/kg), which leads to the content far exceeding the requirements of the Standard CJ/T340-2016 (Cd ≤ 1.5 and Hg ≤ 1.8, unit mg/kg) when considering its direct use as soil for planting fill [43]. Sewage contains a certain quantity of heavy metals, which may potentially lead to environmental pollution. Since the organic matter content of sewage is not high (30%), it is difficult to utilize it as a resource. Sewage needs to be dewatered and subsequently incinerated. The heavy metals would be enriched in the fly ash and slag produced by incineration, which need to be treated in accordance with the requirements of hazardous waste [48].
The grille residue has high organic matter content (76%). In order to better analyze the approach to resource utilization of the grille residue, some properties such as the volatile matter and ash content of the grille residue were determined, as shown in Table 6. Table 6 shows that the volatile substances, ash, and solid carbon indicators are high. This means that it can be processed into RDF rods.
The particle size distribution of coarse aggregates and fine aggregates in LWPP was determined. A 5 mm sieve was used to separate coarse aggregates and fine aggregates, so the particle size of coarse aggregates was greater than 5 mm. The particle size distribution of fine aggregates is shown in Figure 4. The median particle size of fine aggregates is about 0.61 mm, and the content of particles smaller than 0.1 mm is about 10%. Therefore, these materials could be used as a substitute for primary aggregate materials in low specification applications such as road construction and bulk fill.
In summary, a preliminary analysis of resource utilization can be carried out for each waste. The aggregates contain more stones and sand; they can be sieved and cleaned to recover the aggregates for use as road building materials. Due to the high organic content of the grille residue, it can be made into RDF rods for resource utilization.

3.2. Solid Waste Characterization in Different Sewerage Facilities

The composition and chemical properties of the solid waste from the different facilities in sewerage systems were tested. Figure 5, Figure 6 and Figure 7 show the composition, organic matter, and heavy metals in the solid waste of each facility. The solid waste RDP-Co contains a large quantity of aggregates (coarse and fine aggregates together account for approximately 85% of the total mass) and low organic matter content and heavy metals. This can be attributed to the specificity of the sampling area. The rainwater drainage pipes are near the construction site, and a large amount of cement, gravel, sand, and other building waste have been dumped into the pipe network.
The nature of the solid waste RDP-Cu also has regional characteristics. This type of waste has high organic matter content (83%) and a very low content of aggregates. It can be speculated that some residues of kitchen waste were discharged into the rainwater drainage pipes. Due to the high organic matter content, it is better to mix this solid waste with grille residue to make RDF rods. Solid wastes from RDP-Co and RDP-Cu show strong regional characteristics, which reveals that the degree of management and supervision was insufficient and some wastes were mixed into rainwater drainage pipes.
The waste PS, GT, GC, and ST have a high level of aggregates (coarse and fine aggregates together account for about 35–70% of the total mass). Heavy metals are present in higher concentrations. The complexity of the environment near the sampling area may have contributed to this result. Since organic matter and heavy metals are found in the waste, the aggregates in the waste need to be treated by sand washing before recycling.
In summary, the properties of solid waste from different facilities in sewerage systems are obviously different from those at the terminal, and the properties have regional differences, which can be more convenient for resource treatment according to their characteristics.

4. Discussion

This paper has determined the nature of solid waste from various facilities in sewerage systems and put forward preliminary suggestions for resource utilization. In this section, approaches to resource utilization are further discussed in conjunction with relevant regulations.

4.1. Approach of Resource Utilization for Solid Waste in Terminal

The results have shown that the nature of solid waste from the WWTP is quite complex, which is not conducive to direct resource utilization. In fact, landfilling has been the main means of disposal of the solid waste in developing countries. However, due to the limited capacity of landfills and the tightening of national policies, landfilling will not be sustainable. Therefore, new approaches need to be discussed and proposed.
In developed countries, the reuse of solid waste in the WWTP according to its nature is the main method of treatment. This method avoids many of the disadvantages of landfilling and is the future trend in the treatment of solid waste. However, the results in Table 4, Table 5 and Table 6 and Figure 3 show that the nature of solid waste in the WWTP in developing countries is complex, and all types of solid waste produced after separation contain a certain amount of organic matter and heavy metals. It is necessary to first ensure that the content of organic matter and heavy metals in the waste meets the relevant requirements and adopt corresponding approaches to recycle the waste according to its characteristics.
Through multi-stage separation, the solid waste in the WWTP can be classified into coarse aggregates, fine aggregates, grille residue, sewage, and substrate. The approaches to resource utilization are discussed separately. Despite the presence of some heavy metals in the coarse aggregates, the content of heavy metals met the requirements of the Standard DB4403/T 67-2020 [45] for the first category of construction land soil screening values. Therefore, the hazard of coarse aggregates to human health can be ignored when they are used as building materials. According to the requirements related to fillers and bedding layers in the Code JTG D30-2015 [44], the maximum particle size of fillers should be less than 150 mm. As the coarse aggregates contain large aggregates with particle sizes exceeding 150 mm, they are not suitable for direct use as road base fillers. The coarse aggregates need to be crushed to a particle size below 150 mm and then used as roadbed filler.
Table 4 and Figure 3 show that low concentrations of heavy metals, normal levels of total bacteria, and no PAHs were detected in fine aggregates. Therefore, there is no need to consider the problem of environmental pollution in the process of utilizing fine aggregates. According to the requirements of the Standard JGJ52-2006 [46], the mud content of the sand should not exceed 2% (Class I), 3% (Class II), and 5% (Class III), respectively [45]. Therefore, the fine aggregates need to be cleaned to meet the corresponding requirements for sand.
The main components of the grille residue are dead branches, leaves, and household waste, which contain a large amount of organic matter and has the potential to be used as RDF rods. The general criteria for making RDF rods are as follows: water (<10%), ash (12–25%), volatile matter (55–75%), and solid carbon (7–13%). As can be seen from Table 6, the properties of the grille residue basically meet the requirements, except for the high water content. Therefore, in the subsequent resource utilization of the grille residue, dewatering, crushing, and rod-making processes should be carried out to form the RDF rods. In addition, because of the high organic matter content in the grille residue, the grille residue can also be considered to produce biochar, biocrude, non-condensable flammable gases, and other substances through thermochemical treatment. Alternatively, the grille residue can be mixed with the substrate and fermented through anaerobic digestion to produce biogas and fertilizer.
Figure 3 and Table 5 show that a certain amount of organic matter and heavy metals were detected in the sewage. The organic matter content in sewage is 30%, which is significantly lower than that in developed countries, which is generally about 75% [49]. The particularity of the nature of solid waste in the WWTP in developing countries can be seen. Due to the low content of organic matter in sewage, resource utilization methods used in developed countries are difficult to apply directly. According to Code GB 50335-2002 [42], the sewage from the WWTP cannot be used directly for miscellaneous urban water. Sewage needs to be processed before being used, such as through coagulation, sedimentation, filtration, and disinfection. The treated sewage can also be used in the relevant cleaning process in the WWTP.
In summary, the waste separated at various stages in the WWTP can be used resourcefully after secondary treatment. However, the solid waste in the WWTP contains low organic matter content and a certain quantity of heavy metals. This leads to the need to consider pollutants in the process of recycling, which increases the difficulty and cost of disposal.

4.2. Approach of Resource Utilization for Solid Waste in Different Sewerage Facilities

From the discussion in Section 4.1, the solid waste in the WWTP can be converted into materials through some means of recycling; however, due to the complexity of the nature of solid waste, the difficulty and cost of recycling have increased. These lead to the fact that in actual operation in developing countries, the solid waste in the WWTP is basically not utilized.
In developing countries, the discharge of solid waste from sewerage systems lacks systematic management and strict supervision, which leads to the complexity of the nature of solid waste in the WWTP. In this case, it is not appropriate to apply the methods of developed countries to the treatment of solid waste related to sewerage systems. Therefore, it is necessary to explore a set of corresponding strategies suitable for the current situation of developing countries.
As can be seen from Figure 5, Figure 6 and Figure 7, unlike the solid waste taken at the WWTP, the waste collected at the various facilities in sewerage systems have not been mixed or contaminated with each other; therefore, they have distinct characteristics. Based on their properties, the waste collected from the different facilities in sewerage systems can be divided into three categories, as shown in Figure 8A–C: Category A is characterized by a very high sand content and low organic matter content and heavy metals (a representative example is the waste RDP-Co); Category B is characterized by a high sand content but also contains a large number of pollutants (representative examples are the waste from pumping stations, grease traps, septic tanks, and grit chambers); Category C is characterized by a low sand content but a high amount of organic matter and pollutants (a representative example is the waste RDP-Cu).
As shown in Figure 8, according to the different nature of various types of waste, different approaches of resource utilization can be designed to improve the efficiency of resource utilization of waste. The waste RDP-Co has low organic matter content and pollution and a high sand content. Therefore, it can be utilized as building materials after being dewatered by pressing and filtering. The waste from the pumping stations, grease traps, septic tanks, and grit chambers has a higher pollution level and sand content but a lower organic content. Therefore, the fine aggregates could be recovered through processes such as de-mixing, screening, and sand washing. The sewage generated during the process can be discharged to the WWTP for treatment. The waste from the RDP-Cu has high organic matter content, a high pollution level, and a low sand content, so it can be mixed with the grille residue and then made into RDF rods through filter press dewatering. In addition, the waste of Category C can be mixed with grille residue and treated thermochemically to produce substances such as biochar, biocrude, and non-condensable flammable gases. Anaerobic digestion can also be considered to produce substances such as natural gas and fertilizer, thereby reusing the resource. In the above process, solid waste that does not have resource potential can be discharged to the WWTP for comprehensive treatment.
In summary, the waste collected from different facilities in sewerage systems has not been mixed and has varied greatly in nature, such as the waste RDP-Co, which only requires simple treatment to achieve building materials. The waste RDP-Cu contains high organic matter content and is more suitable for processing into RDF rods. The solid waste generated by these facilities only needs simple treatment to be recycled. Solid waste that is not suitable for recycling can be discharged normally and enter the WWTP for treatment. Through such a strategy, solid waste is sorted in advance and utilized as a resource, which improves the treatment efficiency of solid waste in the sewerage systems and the efficiency of resource utilization.
Pre-sorting, treatment, and recycling of solid waste from sewerage facilities have achieved sustainable development and reduced the pressure on landfill operations. For developing countries, it is a better strategy before management and supervision can meet the requirements. However, for the early sorting and treatment of solid waste, it is necessary to build corresponding treatment facilities, which increases the cost. In the future, it is necessary to conduct analysis from the life-cycle assessment perspective to explain in which specific situations these strategies should be used.

5. Conclusions

The degree of resource utilization of solid waste generated by the sewerage systems in developing countries is very limited. Based on the idea of sustainable development, it is necessary to expand the methods of resource recovery. In this paper, a variety of waste was collected from a terminal and different facilities in sewerage systems, and the characteristics of solid waste were tested and analyzed. Based on these results, corresponding resource recovery strategies were proposed. The main conclusions are as follows:
(1) The waste separated at various stages in the WWTP can be used resourcefully after secondary treatment. Due to weak management and supervision in developing countries, the solid waste contains low organic matter content and a certain quantity of heavy metals, which increases the difficulty and cost of recycling. Therefore, recycling is not recommended until the management level of sewerage systems has been improved;
(2) The waste collected from different facilities in sewerage systems has not been mixed and has varied greatly in nature. Before these solid wastes enter the WWTP, the strategy of pre-sorting, treating, and recycling these solid wastes is worth recommending. A small part of solid waste that is not suitable for recycling can be discharged normally and enter the WWTP for treatment. There are three types of solid waste in different sewerage facilities that can be classified. The first category is characterized by an extremely high sand content and low organic matter and heavy metal content, which can be directly used as building materials after dewatering treatment. The second category is characterized by high sand content but also contains a large number of polluting substances which need to be cleaned before being considered as building materials. The third category is characterized by low sand content but high organic matter content and large quantities of polluting substances, which can be dewatered to make RDF rods or undergo thermochemical treatment or anaerobic digestion to become relevant valuable products.
Sustainable development could be accomplished through the pre-sorting, treatment, and recycling of solid waste from sewerage facilities. However, it is necessary to build corresponding treatment facilities for the early classification and treatment of solid waste, which increases the cost. In the future, it is necessary to investigate this topic from a life-cycle-evaluation perspective to clarify when these strategies should be applied.

Author Contributions

Conceptualization, X.S.; methodology, X.S. and J.F.; formal analysis, S.W. and J.F.; investigation, Y.P. (Yongshen Peng); data curation, Y.P. (Yuansheng Peng); writing—original draft preparation, X.S. and J.H.; writing—review and editing, S.W.; visualization, Z.W.; project administration, W.L. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by the National Natural Science Foundation of China: (52179108), and Shenzhen Science and Technology Program (KCXFZ2021102016401302).

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Not applicable.

Conflicts of Interest

The authors declare no conflict of interest.

Abbreviations

AsArsenicPbLead
CdCadmiumPAHsPolycyclic aromatic hydrocarbons
CODChemical oxygen demandPSThe sample from pumping station
CrChromiumRDFRefuse derived fuel
CuCuprumRDP-CoThe sample from rainwater drainage pipes near the construction site
GCThe sample from grit chamberRDP-CuThe sample from rainwater drainage pipes near the cuisine street
GTThe sample from grease trapSTThe sample from septic tank
HgHydrargyrumTNTotal nitrogen
LWPPThe samples from Luofang Water Purification PlantTPTotal phosphorus
NH3-NAmmonia nitrogenTPHTotal petroleum hydrocarbon
NiNickelWWTPWastewater treatment plant
ZnZinc

References

  1. Trotti, F.; Caldognetto, E.; Forte, M.; Nuccetelli, C.; Risica, S.; Rusconi, R. Estonian waterworks treatment plants: Clearance of residues, discharge of effluents and efficiency of removal of radium from drinking water. J. Radiol. Prot. 2013, 33, 809–822. [Google Scholar] [CrossRef] [PubMed]
  2. Mokonyama, S.; Schalkwyk, M.; Rajagopaul, R. Guidelines and good practices for water treatment residues handling, disposal and reuse in South Africa. Water Res. Comm. Gezina S. Afr. 2017, 140. Available online: https://wrc.org.za/wp-content/uploads/mdocs/TT738.pdf (accessed on 13 January 2023).
  3. Anyakora, N.V.; Ajinomoh, C.S.; Ahmed, A.S.; Mohammed-Dabo, I.A.; Ejeh, S.P.; Okuofu, C.A.; Abba, H. Phase and Micro-Chemical Characterization of Water Works Sludge Minerals and their Thermally-Decomposed Products. J. Eng. Res. 2016, 21, 9–20. [Google Scholar]
  4. Titshall, L.W.; Hughes, J.C. Characterisation of some South African water treatment residues and implications for land application. Water SA 2005, 31, 299–308. [Google Scholar] [CrossRef] [Green Version]
  5. Bugajski, P.; Operacz, A.; Młyński, D.; Wałęga, A.; Kurek, K. Optimizing treatment of cesspool wastewater at an activated sludge plant. Sustainability 2020, 12, 10196. [Google Scholar] [CrossRef]
  6. Nandhini, R.; Berslin, D.; Sivaprakash, B.; Rajamohan, N.; Vo, D.N. Thermochemical conversion of municipal solid waste into energy and hydrogen: A review. Environ. Chem. Lett. 2022, 20, 1645–1669. [Google Scholar] [CrossRef]
  7. Hartmann, H.; Ahring, B.K. Strategies for the anaerobic digestion of the organic fraction of municipal solid waste: An overview. Water Sci. Technol. 2006, 53, 7–22. [Google Scholar] [CrossRef]
  8. Khan, A.H.; Sharholy, M.; Alam, P.; Al-Mansour, A.I.; Ahmad, K.; Kamal, M.A.; Alam, S.; Pervez, M.N.; Naddeo, V. Evaluation of cost benefit analysis of municipal solid waste management systems. J. King Saud Univ. 2022, 34, 101997. [Google Scholar] [CrossRef]
  9. Cai, X.; Wu, K.; Huang, W.; Yu, J.; Yu, H. Application of recycled concrete aggregates and crushed bricks on permeable concrete road base. Road Mater. Pavement Des. 2021, 22, 2181–2196. [Google Scholar] [CrossRef]
  10. Asokan, P.; Saxena, M.; Asolekar, S.R. Coal combustion residues—Environmental implications and recycling potentials. Resour. Conserv. Recycl. 2005, 43, 239–262. [Google Scholar] [CrossRef]
  11. Ma, W.; Chen, D.; Pan, M.; Gu, T.; Zhong, L.; Chen, G.; Yan, B.; Cheng, Z. Performance of chemical chelating agent stabilization and cement solidification on heavy metals in MSWI fly ash: A comparative study. J. Environ. Manag. 2019, 247, 169–177. [Google Scholar] [CrossRef] [PubMed]
  12. Lindberg, D.; Molin, C.; Hupa, M. Thermal treatment of solid residues from WtE units: A review. Waste Manag. 2015, 37, 82–94. [Google Scholar] [CrossRef] [PubMed]
  13. Luo, H.; Cheng, Y.; He, D.; Yang, E. Review of leaching behavior of municipal solid waste incineration (MSWI) ash. Sci. Total Environ. 2019, 668, 90–103. [Google Scholar] [CrossRef]
  14. Yang, Y.; Liew, R.K.; Tamothran, A.M.; Foong, S.Y.; Yek, P.N.Y.; Chia, P.W.; Van Tran, T.; Peng, W.; Lam, S.S. Gasification of refuse-derived fuel from municipal solid waste for energy production: A review. Environ. Chem. Lett. 2021, 19, 2127–2140. [Google Scholar] [CrossRef]
  15. Hoppe, E.J.; Lane, D.S.; Fitch, G.M.; Shetty, S. Feasibility of Reclaimed Asphalt Pavement (RAP) Use as Road Base and Subbase Material. Available online: https://rosap.ntl.bts.gov/view/dot/28518 (accessed on 13 January 2023).
  16. Moawad, H.; Zohdy, L.I.; Badr El-Din, S.; Khalafallah, M.A.; Abdel-Maksoud, H.K. Assessment of anaerobically digested slurry as a fertilizer and soil conditioner. In Biogas Technology, Transfer and Diffusion; Springer: Berlin/Heidelberg, Germany, 1986; pp. 499–519. [Google Scholar]
  17. Saghafi, M.D.; Teshnizi, Z.S.H. Recycling value of building materials in building assessment systems. Energy Build. 2011, 43, 3181–3188. [Google Scholar] [CrossRef]
  18. Aye, L.; Hes, D. Green building rating system scores for building reuse. J. Green Build. 2012, 7, 105–112. [Google Scholar] [CrossRef]
  19. Ding, A.; Qu, F.; Liang, H.; Guo, S.; Ren, Y.; Xu, G.; Li, G. Effect of adding wood chips on sewage sludge dewatering in a pilot-scale plate-and-frame filter press process. RSC Adv. 2014, 4, 24762–24768. [Google Scholar] [CrossRef]
  20. Cui, Y.; Zhu, W.; Wu, S.; Liu, J.; Hou, H.; Lin, N. The role of lime in dredged mud dewatered by a plate and frame filter press and potential substitutes. Environ. Sci. Pollut. Res. 2021, 28, 17331–17342. [Google Scholar] [CrossRef]
  21. Verma, S.; Klima, M.S. Evaluation of a pilot-scale, plate-and-frame filter press for dewatering thickener underflow slurries from bituminous coal-cleaning plants. Int. J. Coal Prep. Util. 2010, 30, 1–19. [Google Scholar] [CrossRef]
  22. Oggeri, C.; Fenoglio, T.M.; Vinai, R. Tunnel spoil classification and applicability of lime addition in weak formations for muck reuse. Tunn. Undergr. Space Techcol. 2014, 44, 97–107. [Google Scholar] [CrossRef]
  23. Zhang, H.; Liu, W.; Lin, X.; Su, S.; Zhao, B. To ameliorate the performance of recycled aggregate concrete (RAC) by pre-treating aggregate in sulfoaluminate cement slurry and water glass solution. J. Build. Eng. 2021, 44, 103364. [Google Scholar] [CrossRef]
  24. Dave, S.; Raj, D.; Raval, J. To Study the Characteristics of Recycled Concrete Aggregates upon Their Treatment with a Weak Acid and Geopolymer Slurry. Available online: http://ir.pdpu.ac.in:8080/jspui/handle/123456789/173 (accessed on 13 January 2023).
  25. Li, H.; Tong, Y.; Zhang, H.; Zhang, X.; Duan, J. Study on road performance of cement fly ash stabilized steel slag—Concrete recycled macadam. Materials 2021, 14, 7530. [Google Scholar] [CrossRef]
  26. Yan, K.; Lan, H.; Li, Q.; Ge, D.; Li, Y. Optimum utilization of recycled aggregate and rice husk ash stabilized base material. Constr. Build. Mater. 2022, 348, 128627. [Google Scholar] [CrossRef]
  27. Mistri, A.; Bhattacharyya, S.K.; Dhami, N.; Mukherjee, A.; Barai, S.V. A review on different treatment methods for enhancing the properties of recycled aggregates for sustainable construction materials. Constr. Build. Mater. 2020, 233, 117894. [Google Scholar] [CrossRef]
  28. Raut, S.P.; Ralegaonkar, R.V.; Mandavgane, S.A. Development of sustainable construction material using industrial and agricultural solid waste: A review of waste-create bricks. Constr. Build. Mater. 2011, 25, 4037–4042. [Google Scholar] [CrossRef]
  29. Boarder, R.; Owens, P.L.; Khatib, J.M. The sustainability of lightweight aggregates manufactured from clay wastes for reducing the carbon footprint of structural and foundation concrete. In Sustainability of Construction Materials; Elsevier: Amsterdam, The Netherlands, 2016; pp. 209–244. [Google Scholar]
  30. Hossain, S.S.; Roy, P.K. Sustainable ceramics derived from solid wastes: A review. J. Asian Ceram. Soc. 2020, 8, 984–1009. [Google Scholar] [CrossRef]
  31. Ministry of Agriculture of the PRC. Method for Determination of Soil Organic Matter. China Agriculture Press: Beijing, China, 2010. Available online: https://www.doc88.com/p-4921296827978.html (accessed on 14 November 2022).
  32. Ministry of Environmental Protection of the People’s Republic of China. Solid Waste—Determination of Mercury, Arsenic, Selenium, Bismuth, Antimony—Microwave Dissolution/Atomic Fluorescence Spectrometry. China Environmental Press: Beijing, China, 2014. Available online: https://www.doc88.com/p-68939064249582.html (accessed on 14 November 2022).
  33. Ministry of Environmental Protection of the People’s Republic of China. Solid Waste—Determination of Lead, Zinc and Cadmium-Flame atomic absorption spectrometry. China Environmental Press: Beijing, China, 2016. Available online: https://www.doc88.com/p-9922568892068.html (accessed on 14 November 2022).
  34. Ministry of Environmental Protection of the People’s Republic of China. Solid Waste—Determination of Metals—Inductively Coupled Plasma Mass Spectrometry (ICP-MS). China Environmental Press: Beijing, China, 2015. Available online: https://www.doc88.com/p-9048715200664.html (accessed on 14 November 2022).
  35. Ministry of Ecology and Environment of the People’s Republic of China. Soil and Sediment—Determination of Petroleum Hydrocarbons (C10-C40)—Gas Chromatography. China Environment Publishing Group: Beijing, China, 2019. Available online: https://www.doc88.com/p-60529008112529.html (accessed on 14 November 2022).
  36. Ministry of Construction of the People’s Republic of China. Determination Method for Municipal Sludge in Wastewater Treatment Plant. Standards Press of China: Beijing, China, 2005. Available online: https://www.doc88.com/p-1186038269.html (accessed on 14 November 2022).
  37. Ministry of Environmental Protection of the People’s Republic of China. Solid Waste—Determination of Polycyclic Aromatic Hydrocarbons—High Performance Liquid Chromatography. China Environmental Press: Beijing, China, 2017. Available online: https://www.doc88.com/p-9099672501868.html (accessed on 14 November 2022).
  38. General Administration of Quality Supervision, Inspection and Quarantine of the People’s Republic of China; Standardization Administration of the People’s Republic of China. Proximate Analysis of Coal. Standards Press of China: Beijing, China, 2009. Available online: https://www.doc88.com/p-1933807965091.html (accessed on 14 November 2022).
  39. Ministry of Environmental Protection of the People’s Republic of China. Water Quality—Determination of pH—Electrode Method. China Environmental Press: Beijing, China, 2020. Available online: https://www.doc88.com/p-99599060330118.html (accessed on 14 November 2022).
  40. Ministry of Environmental Protection of the People’s Republic of China. Water Quality—Determination of the Chemical Oxygen Demand—Dichromate Method. China Environmental Press: Beijing, China, 2017. Available online: https://www.doc88.com/p-7794991208370.html (accessed on 14 November 2022).
  41. State Environmental Protection Administration; General Administration of Quality Supervision, Inspection and Quarantine of the People’s Republic of China. Environmental Quality Standards for Surface Water. China Environmental Press: Beijing, China, 2002. Available online: https://www.doc88.com/p-7763822545075.html (accessed on 14 November 2022).
  42. Ministry of Construction of the People’s Republic of China; General Administration of Quality Supervision, Inspection and Quarantine of the People’s Republic of China. Code for Design of Municipal Wastewater Reclamation and Reuse. China Environmental Press: Beijing, China, 2016. Available online: https://www.doc88.com/p-6488418465814.html (accessed on 14 November 2022).
  43. Ministry of Housing and Urban-Rural Development of the People’s Republic of China. Planting Soil for Greening. Standards Press of China: Beijing, China, 2016. Available online: https://www.doc88.com/p-34087139088771.html (accessed on 15 November 2022).
  44. Ministry of Transport of the People’s Republic of China. Specifications for Design of Highway Subgrades. China Communications Press: Beijing, China, 2004. Available online: https://www.doc88.com/p-3874248635707.html (accessed on 14 November 2022).
  45. Shenzhen Administration for Market Regulation. Risk Screening Values and Intervention Values for Soil Contamination of Development Land. Shenzhen Publishing Group: Shenzhen, China, 2020. Available online: https://www.doc88.com/p-24359487432786.html (accessed on 14 November 2022).
  46. Ministry of Construction of the People’s Republic of China. Standard for Technical Requirements and Test Method of Sand and Crushed Stone (or Gravel) for Ordinary Concrete. China Architecture & Building Press: Beijing, China, 2006. Available online: https://www.doc88.com/p-135711922595.html (accessed on 14 November 2022).
  47. Oelkers, E.H.; Benning, L.G.; Lutz, S.; Mavromatis, V.; Pearce, C.R.; Plümper, O. The efficient long-term inhibition of forsterite dissolution by common soil bacteria and fungi at Earth surface conditions. Geochim. Cosmochim. Acta 2015, 168, 222–235. [Google Scholar] [CrossRef] [Green Version]
  48. Khan, A.H.; López-Maldonado, E.A.; Khan, N.A.; Villarreal-Gómez, L.J.; Munshi, F.M.; Alsabhan, A.H.; Perveen, K. Current solid waste management strategies and energy recovery in developing countries—State of art review. Chemosphere 2022, 291, 133088. [Google Scholar] [CrossRef]
  49. Świerczek, L.; Cieślik, B.M.; Konieczka, P. The potential of raw sewage sludge in construction industry—A review. J. Clean. Prod. 2018, 200, 342–356. [Google Scholar] [CrossRef]
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Figure 1. Sampling location: A: Luofang Water Purification Plant; B: rainwater drainage pipes (near the construction site); C: rainwater drainage pipes (near the cuisine street); D: pumping station; E: grease trap; F: grit chamber; G: septic tank.
Figure 1. Sampling location: A: Luofang Water Purification Plant; B: rainwater drainage pipes (near the construction site); C: rainwater drainage pipes (near the cuisine street); D: pumping station; E: grease trap; F: grit chamber; G: septic tank.
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Figure 2. Composition of solid waste separated at various stages of the terminal.
Figure 2. Composition of solid waste separated at various stages of the terminal.
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Figure 3. Heavy metal content of solid waste separated at various stages of terminal.
Figure 3. Heavy metal content of solid waste separated at various stages of terminal.
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Figure 4. Particle size distribution of fine aggregates.
Figure 4. Particle size distribution of fine aggregates.
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Figure 5. Inorganic content in solid waste at each facility.
Figure 5. Inorganic content in solid waste at each facility.
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Figure 6. Organic content in solid waste at each facility.
Figure 6. Organic content in solid waste at each facility.
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Figure 7. Heavy metal content in solid waste at each facility.
Figure 7. Heavy metal content in solid waste at each facility.
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Figure 8. Approaches of resource utilization for solid waste in sewerage systems. (A) Category A. (B) Category B. (C) Category C.
Figure 8. Approaches of resource utilization for solid waste in sewerage systems. (A) Category A. (B) Category B. (C) Category C.
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Table
Table 2. Testing items and reference standards for the nature of solid waste.
Table 2. Testing items and reference standards for the nature of solid waste.
Sample TypeTest ItemsReference Standards
All solid wasteOrganic matterMethod for determination of soil organic matter (GB 9834-88) [31]
AsSolid Waste—Determination of Mercury, Arsenic, Selenium, Bismuth, Antimony—Microwave Dissolution/Atomic Fluorescence Spectrometry (HJ 702-2014) [32]
Solid waste—Determination of Lead, Zinc and Cadmium- Flame atomic absorption spectrometry (HJ 786-2016) [33]
Solid waste—Determination of metals- Inductively Coupled Plasma Mass Spectrometry (ICP- MS) (HJ766-2015) [34]
Hg
Zn
Pb
Cd
Cr
Ni
Cu
TPHSoil and sediment—Determination of petroleum hydrocarbons (C10- C40)—gas chromatography (HJ 1021-2019) [35]
BacteriaDetermination method for municipal sludge in wastewater treatment plant (CJ/T 221-2005) [36]
PAHsSolid waste—Determination of polycyclic aromatic hydrocarbons—High performance liquid chromatography (HJ 892-2017) [37]
Grille residueVolatile substances, Ash, and Solid carbonProximate analysis of coal (GB/T 212-2008) [38]
SewagepHWater quality—Determination of pH—Electrode method (HJ 1147-2020) [39]
CODWater quality—Determination of the Chemical Oxygen Demand—Dichromate Method (HJ 828-2017) [40]
TNEnvironmental quality standards for surface water (GB3838-2002) [41]
TP
NH3-N
Table
Table 3. Codes and standards for evaluating the nature of solid waste.
Table 3. Codes and standards for evaluating the nature of solid waste.
Sample TypeRelated Codes and Standards
SewageEnvironmental quality standards for surface water (GB 3838-2002) [41]
Code for design of municipal wastewater reclamation and reuse (GB50335-2016) [42]
Coarse aggregatesPlanting soil for greening (CJ/T340-2016) [43]
Specifications for Design of Highway Subgrades (JTG D30-2004) [44]
Risk screening values and intervention values for soil contamination of development land (DB4430/T 67-2020) [45]
Fine aggregatesStandard for technical requirements and test method of sand and crushed stone (or gravel) for ordinary concrete (JGJ 52-2006) [46]
Table
Table 4. Basic properties of solid waste separated at various stages of terminal.
Table 4. Basic properties of solid waste separated at various stages of terminal.
Test ItemsCoarse AggregatesFine AggregatesGrille ResidueSubstrate
pH8.58.36.86.9
Water content (%)812.84092
Organic matter (%)1.7787634.8
PAHs (µg/L)ND *NDNDND
Bacteria (pcs/g)2.1 × 1071.7 × 1061.7 × 1083.6 × 108
* ND means that the corresponding substance was not detected in the sample.
Table
Table 5. Properties of the sewage.
Table 5. Properties of the sewage.
pHOrganic Matter (%)COD (mg/L)TN (mg/L)NH3-N (mg/L)TP (mg/L)TPH (mg/L)
6.1308.45 × 10345733457.72.13
Table
Table 6. Properties of the grille residue from the separation process.
Table 6. Properties of the grille residue from the separation process.
Volatile Substances (%)Ash (%)Solid Carbon (%)
73.7115.8010.49
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Sun, X.; He, J.; Lv, W.; Wu, S.; Peng, Y.; Peng, Y.; Fei, J.; Wu, Z. Characteristics and Resource Recovery Strategies of Solid Waste in Sewerage Systems. Sustainability 2023, 15, 1662. https://doi.org/10.3390/su15021662

AMA Style

Sun X, He J, Lv W, Wu S, Peng Y, Peng Y, Fei J, Wu Z. Characteristics and Resource Recovery Strategies of Solid Waste in Sewerage Systems. Sustainability. 2023; 15(2):1662. https://doi.org/10.3390/su15021662

Chicago/Turabian Style

Sun, Xiaohui, Junpei He, Wei Lv, Silin Wu, Yongshen Peng, Yuansheng Peng, Jianbo Fei, and Zezhou Wu. 2023. "Characteristics and Resource Recovery Strategies of Solid Waste in Sewerage Systems" Sustainability 15, no. 2: 1662. https://doi.org/10.3390/su15021662

APA Style

Sun, X., He, J., Lv, W., Wu, S., Peng, Y., Peng, Y., Fei, J., & Wu, Z. (2023). Characteristics and Resource Recovery Strategies of Solid Waste in Sewerage Systems. Sustainability, 15(2), 1662. https://doi.org/10.3390/su15021662

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