# A Comprehensive Review on Thermal Coconversion of Biomass, Sludge, Coal, and Their Blends Using Thermogravimetric Analysis

Authors: Zeeshan Hameed; Salman Raza Naqvi; Muhammad Naqvi; Imtiaz Ali; Syed Ali Ammar Taqvi; Ningbo Gao; Syed Azfar Hussain; Sadiq Hussain
Journal: Journal of Chemistry
 (2020)

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## Abstract

Lignocellulosic biomass is a vital resource for providing clean future energy with a sustainable environment. Besides lignocellulosic residues, nonlignocellulosic residues such as sewage sludge from industrial and municipal wastes are gained much attention due to its large quantities and ability to produce cheap and clean energy to potentially replace fossil fuels. These cheap and abundantly resources can reduce global warming owing to their less polluting nature. The low-quality biomass and high ash content of sewage sludge-based thermal conversion processes face several disadvantages towards its commercialization. Therefore, it is necessary to utilize these residues in combination with coal for improvement in energy conversion processes. As per author information, no concrete study is available to discuss the synergy and decomposition mechanism of residues blending. The objective of this study is to present the state-of-the-art review based on the thermal coconversion of biomass/sewage sludge, coal/biomass, and coal/sewage sludge blends through thermogravimetric analysis (TGA) to explore the synergistic effects of the composition, thermal conversion, and blending for bioenergy production. This paper will also contribute to detailing the operating conditions (heating rate, temperature, and residence time) of copyrolysis and cocombustion processes, properties, and chemical composition that may affect these processes and will provide a basis to improve the yield of biofuels from biomass/sewage sludge, coal/sewage sludge, and coal/biomass blends in thermal coconversion through thermogravimetric technique. Furthermore, the influencing factors and the possible decomposition mechanism are elaborated and discussed in detail. This study will provide recent development and future prospects for cothermal conversion of biomass, sewage, coal, and their blends.


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## Body

## 1. Introduction

Fossil fuels have been extensively used for the last two centuries to meet the energy demand of the growing population for global development [1–3]. The increase in the environmental and sustainability summons due to the greenhouse emissions that are related to fossil fuel usage and the unceremonious distribution of fossil fuel resources has increased the global energy [4, 5]. It is the need of the time to introduce an alternate energy approach to meet current and future energy demands [6]. The replacement of conventional fossil fuels with sewage sludge, coal, and lignocellulosic biomass fuels as renewable energy resources is considered promising as these have already contributed to around 10% of the global energy supply [7–12]. Soncini et al. stated that from the past thirty years, lignocellulosic biomass was a focal point of research for renewable energy because 56% of energy is provided by biomass, 26% by solar, 11% by wind power, 5% by geothermal energy, and 2% by hydropower [13]. In the future, utilization of renewable sources and biofuels will increase from 2 to 27% [14]. The abundance of biomass and sewage sludge coupled with lower environmental concern and technical ease is the main reason for intensive research and utilization of these sources as feedstocks [15].Coal is the largest source of energy in the United States (fulfilling to about 42% of net energy demand) [16]. Global coal demand dropped during 2014–2016 despite the economic growth during these two years. The growth in the energy demand in China, the US, and Europe has been met partly by renewables and natural gas switch in power generation from coal. However, coal demand grew in India and South East Asia Region due to the increased power demand for their social development and growing economies. Still, in the 21st century, coal is a major source of world energy due to lower cost and a higher energy density [17]. It is expected that coal will contribute to future energy demands in many fast-developing countries, such as China and India [18]. The conversion of biomass to fuels and chemicals by thermal conversion has a substantial value in the petrochemical industry (Figure 1). The major downside of coal is that it is responsible for the emission of ecologically damaging compounds such as sulfur (S), nitrogen (N), and heavy metals, so its utilization with biomass and sewage sludge can mitigate the impact [21].Figure 1
Biomass conversion processes [19, 20].Lignocellulosic biomass, a clean and alternative energy source, has been the point of focus for its abundance and the lower tendency of greenhouse gas emissions [22]. CO2 exhausted from the burning of biomass is absorbed through photosynthesis, thereby controlling global warming [23, 24]. Sewage sludge is another important energy source to produce biofuels through thermochemical conversion, which also solves the disposal problem of waste sludge. The dried sewage sludge is reasonably rich in volatile matters and high in calorific value [25]. Cellulose, hemicellulose, lignin, and extractives are the main constituents of lignocellulosic biomass. Lignocellulosic biomass can be crudely categorized as woody, nonwoody, and wastes. These can be converted into bio-oils, gases, and chemicals through different thermochemical processes such as pyrolysis, gasification, liquefaction, and high-pressure supercritical extraction [26, 27]. Lignocellulosic biomass is considered as the largest sustainable energy source and approximately 220 billion tons of dry biomass is produced annually. It is also called the sole source of obtaining energy because it provides around 14% of the world’s energy supply. According to the UN Food and Agriculture Organization, the world biomass production has increased from 19 million tons to 25 million tons in between 2012 and 2017 [28]. The coconversion of lignocellulosic biomass and sludge by using copyrolysis process can improve the quality of bio-oils and other gaseous products. The use of copyrolysis processes is gaining attention due to its simple and efficient operation to produce liquid [29]. Copyrolysis of lignocellulosic biomass and coal blends can offer several advantages such as reduction in CO2, SOx, and NOx emissions and improve economy and efficiency [30]. A thermogravimetric analyser (TGA) can study the behavior and characteristics of coconversion through copyrolysis. TGA is an important tool to study thermal degradation behavior and synergic effect of many copyrolysis samples [31, 32]. TGA measures the percentage of mass loss of a sample with respect to temperature and time from these data; thermal decomposition behavior during pyrolysis is examined [33]. Moreover, kinetics of degradation of organic material during the pyrolysis process can also be investigated. Thermal degradation is an important factor in designing pyrolysis and copyrolysis processes. TGA is also useful in studying the synergy of different feedstock such as coal, lignocellulosic biomass, and sludge. The synergetic effects depend on the different types of feedstock mix, the intensity of sample contact, type of reactor, experimental conditions, and characteristics of the sample [34]. The effect of mixing ratio and temperature on the product distribution can also be studied by TGA. The most important advantage of thermal coconversion of coal, lignocellulosic biomass, and sewage sludge blends is the reduction in the harmful emissions. Thermal coconversion of biomass and sludge with coal is a relatively profound, cost-effective, and efficient process [35]. Thermal conversion of lignocellulosic biomass can reduce the landfill methane emission and coconversion can reduce the N2O emission as compared to the conversion of coal alone [36]. Thermal coconversion of coal and lignocellulosic biomass offers a better way to utilize coal and wastes/biomass in an inexpensive, harmless, and environmentally acceptable manner [37].Previously published work on the thermal conversion of the different types of lignocellulosic biomass, sewage sludge, and coal is summarized in many review articles (Figure2). Some review articles have focused on the advancement of conversion techniques to improve the oil quality (Figure 3). However, blending ratio is an important factor in thermal coconversion biomass and sludge/coal, and to the best of authors’ knowledge, there is no comprehensive review on the thermal coconversion of different blends using TGA. The compiled data and related discussions in this review will be beneficial in designing and developing efficient cothermal processes.Figure 2
Annual scientific publication on the cothermal conversion of coal/sludge or coal/biomass appeared in the Web of Science database.Figure 3
Sankey three-field plot of countries/keywords/affiliations.Thermal coconversion is getting much attention recently from the researcher due to its economic as well as environmental benefits. Especially during the past ten years, an exponential increase has been seen in the published literature at Web of Science related to thermal coconversion of coal/sludge or coal/biomass.The work has been mostly published by the authors from the developing and developed nations. China is by far leading the rest of the world. Compared to sludge, the copyrolysis of coal/biomass is found in more instances. Most of the related literature appeared in Bioresource Technology, Energy and Fuels, Fuel, and Journal of Analytical and Applied Pyrolysis (Figure4). From 2010 onwards, a sharp increase in the number of published papers is quite evident.Figure 4
(a) Most relevant sources and (b) source growth rate.
(a)(b)The aim of this paper is to comprehensively review the thermal coconversion of the different types of lignocellulosic biomass, sewage sludge, and coal to reveal the synergistic effect of their composition, conversion processes, and blending impact. Previously, there are no concrete and unique studies coupled with thermal coconversion (pyrolysis or combustion) of biomass, sludge, coal, and their blends and discussed their challenges. In addition, some comprehensive discussion is provided emphasizing the behavior of lignocellulosic biomass and blending ratio with coal and sewage sludge focusing on the relevant properties and technical issues that may influence the yield of bio-oils during thermal coconversion. In result, the effect of the properties and chemical composition of blending mixtures of sewage sludge, coal, and lignocellulosic biomass blends on the behavior of these processes will provide pinpoints to increase the efficiency and yield of biofuels obtained from biomass/sewage sludge, coal/sewage sludge, and coal/biomass blends by improving the operating conditions of TGA technique.


## 2. Feedstock and Thermal Coconversion

The selection of feedstock mainly depends on two factors: availability and the property of the material. The feedstock is divided into three main categories. One is lignocellulosic biomass other is coal, and the third is municipal waste.


### 2.1. Lignocellulosic Biomass

The most abundant feedstock is lignocellulosic biomass. Any organic material that can be burned and used as a fuel is called lignocellulosic biomass. Lignocellulosic biomass is the most convenient energy asset that can be used to obtain different liquid fuels and bio-oils. All types of lignocellulosic biomass are classified into primary, secondary, and tertiary biomass based on their resource. Primary biomass can be formed directly by using solar energy and is grown from the land such as woody crops, oilseeds, rice husk, corn comb, rice straw, and bark from trees [38]. An energy research indicated that biomass has the capability to fulfil 10% of the energy supply globally [39]. Secondary biomass can be generated from chemical, physical, and biological processing of primary biomass resources. The bulging substitute as a raw material for bio-oil production for industrial corporations is usually plant-derived biomass, such as corn, sweet sorghum, sugarcane bagasse, wheat, and crop residue, and the feedstock prices are very practical, for example, 7.40 US$/ton in which transportation cost is also included. Accordingly, commercialization of this second-generation biomass turned is being considered as very auspicious and valuable [40]. Tertiary biomass consists of animal fats, used vegetable oil, packaging wastes, and construction wastes. Hossain et al. indicated that microalgae wedged the awareness of presence as third-generation source of biofuel, raw material, nutriment, and collections of extremely treasured products in medicinal and agricultural industries [41]. She also suggested microalgae fuel could be applied for electricity generation by using static diesel engines. They all are composed of cellulose, hemicellulose, lignin, and extractives. Lignocellulosic biomass has the tendency to be transformed into bio-oils, gases, and chemicals [42, 43].


### 2.2. Coal

The other feedstock is coal, which is the second largest source used for energy and can be classified into bituminous, subbituminous, and lignite according to property and origin. Coal is a natural and abundant source to be used. The United States has approximately 260 billion short tons of recoverable reserves, that is, 27% of total reserves around the world. There are many studies which prove the potential of different types of coal in the usage of thermochemical conversion process under different operating conditions.


### 2.3. Sewage Sludge

The next important feedstock is sewage sludge, which is obtained from the municipal and industrial wastewater treatment plants. Sludge is collected as lumps, so it is necessary to reduce particle size and remove the excess moisture content (<10%) to upgrade the quality of the feedstock. To improve the quality of the products, the feedstocks of different properties are mixed in desired blending ratios. Sewage sludge can provide energy and fuel by thermochemical conversion, so this is considered as the most promising alternate technology to reduce the amount of waste and harmful environmental impact. The amount of sewage sludge production is largely depending upon the level and method of treatment applied to wastewater, population growth, and volume of wastewater stream [44]. As indicated by Fytili et al., dried sewage has unpredictable substance of 30–88% and calorific esteem normally 11–25.5 MJ/kg [45]. The utilization of sewage sludge as sustainable power source assets is taken as a healthier choice since this source can give around 10% of worldwide vitality stock [30].


### 2.4. Thermal Coconversion

The conversion of individual coal through thermochemical conversation has environmental challenges in terms of harmful emission which can be minimized by using thermal coconversion of different raw materials, biomass, coal, and sewage sludge bends in different ratios [46]. The thermal coconversion depends upon how feedstock interacts under a specific condition with the specified ratio. Zhang et al. studied the synergy effect of lignite coal and biomass by grinding and sieving at a particle size range of 0.3–0.45 mm with 1 : 1 and dried it in an oven at 105°C for 24 h to improve the yield of the products [47]. Biomass and sewage sludge fuels usually contain a lower amount of fixed carbon and a higher percentage of volatile matter as compared to coal. Usually, thermal coconversion of coal and biomass or sewage sludge produces less carbon-containing compounds such as CO2, CO, CH4, and other light hydrocarbons as compared to the conversion of coal alone [48, 49]. Increasing biomass content in the blend can increase carbon-containing compounds like CO2, CO, and light hydrocarbon gases while hydrogen content decreases. Kumabe et al. used biomass with the higher hydrogen content to increase the proportion of the hydrogen in the product, but the contrary resulted in the product [50].


## 2.1. Lignocellulosic Biomass

The most abundant feedstock is lignocellulosic biomass. Any organic material that can be burned and used as a fuel is called lignocellulosic biomass. Lignocellulosic biomass is the most convenient energy asset that can be used to obtain different liquid fuels and bio-oils. All types of lignocellulosic biomass are classified into primary, secondary, and tertiary biomass based on their resource. Primary biomass can be formed directly by using solar energy and is grown from the land such as woody crops, oilseeds, rice husk, corn comb, rice straw, and bark from trees [38]. An energy research indicated that biomass has the capability to fulfil 10% of the energy supply globally [39]. Secondary biomass can be generated from chemical, physical, and biological processing of primary biomass resources. The bulging substitute as a raw material for bio-oil production for industrial corporations is usually plant-derived biomass, such as corn, sweet sorghum, sugarcane bagasse, wheat, and crop residue, and the feedstock prices are very practical, for example, 7.40 US$/ton in which transportation cost is also included. Accordingly, commercialization of this second-generation biomass turned is being considered as very auspicious and valuable [40]. Tertiary biomass consists of animal fats, used vegetable oil, packaging wastes, and construction wastes. Hossain et al. indicated that microalgae wedged the awareness of presence as third-generation source of biofuel, raw material, nutriment, and collections of extremely treasured products in medicinal and agricultural industries [41]. She also suggested microalgae fuel could be applied for electricity generation by using static diesel engines. They all are composed of cellulose, hemicellulose, lignin, and extractives. Lignocellulosic biomass has the tendency to be transformed into bio-oils, gases, and chemicals [42, 43].


## 2.2. Coal

The other feedstock is coal, which is the second largest source used for energy and can be classified into bituminous, subbituminous, and lignite according to property and origin. Coal is a natural and abundant source to be used. The United States has approximately 260 billion short tons of recoverable reserves, that is, 27% of total reserves around the world. There are many studies which prove the potential of different types of coal in the usage of thermochemical conversion process under different operating conditions.


## 2.3. Sewage Sludge

The next important feedstock is sewage sludge, which is obtained from the municipal and industrial wastewater treatment plants. Sludge is collected as lumps, so it is necessary to reduce particle size and remove the excess moisture content (<10%) to upgrade the quality of the feedstock. To improve the quality of the products, the feedstocks of different properties are mixed in desired blending ratios. Sewage sludge can provide energy and fuel by thermochemical conversion, so this is considered as the most promising alternate technology to reduce the amount of waste and harmful environmental impact. The amount of sewage sludge production is largely depending upon the level and method of treatment applied to wastewater, population growth, and volume of wastewater stream [44]. As indicated by Fytili et al., dried sewage has unpredictable substance of 30–88% and calorific esteem normally 11–25.5 MJ/kg [45]. The utilization of sewage sludge as sustainable power source assets is taken as a healthier choice since this source can give around 10% of worldwide vitality stock [30].


## 2.4. Thermal Coconversion

The conversion of individual coal through thermochemical conversation has environmental challenges in terms of harmful emission which can be minimized by using thermal coconversion of different raw materials, biomass, coal, and sewage sludge bends in different ratios [46]. The thermal coconversion depends upon how feedstock interacts under a specific condition with the specified ratio. Zhang et al. studied the synergy effect of lignite coal and biomass by grinding and sieving at a particle size range of 0.3–0.45 mm with 1 : 1 and dried it in an oven at 105°C for 24 h to improve the yield of the products [47]. Biomass and sewage sludge fuels usually contain a lower amount of fixed carbon and a higher percentage of volatile matter as compared to coal. Usually, thermal coconversion of coal and biomass or sewage sludge produces less carbon-containing compounds such as CO2, CO, CH4, and other light hydrocarbons as compared to the conversion of coal alone [48, 49]. Increasing biomass content in the blend can increase carbon-containing compounds like CO2, CO, and light hydrocarbon gases while hydrogen content decreases. Kumabe et al. used biomass with the higher hydrogen content to increase the proportion of the hydrogen in the product, but the contrary resulted in the product [50].


## 3. Factors for Synergistic Effects on Thermal Coconversion

### 3.1. Ultimate, Proximate, and Chemical Composition Analysis of Coal

Coal is the combustible material containing 50% by weight of carbon. It is a carbonaceous material with some percentage of hydrogen, oxygen, nitrogen, sulfur, and ash. Based on the fractions of hydrogen, oxygen, and carbon present in the sample, coal is ranked into four main categories such as bituminous coal, lignite, anthracite, and subbituminous coal [51]. Coal is usually dried at 105°C for 24 h in a muffle furnace or electric furnace to improve the high heating value (HHV). The raw hydrothermally treated moisture-free coal has some oxygenated functional group such as carboxyl, phenolic, hydroxyl, and all acidic groups. Table 1 shows the elemental composition, proximate analysis, and calorific value of the different coals. The ultimate analysis shows that coals contain higher carbon (60–90%). The proximate analysis shows volatiles between 38% and 40% which is less than that present in sewage sludge and bagasse. The calorific value of coal not only depends on the moisture, ash, and oxygen contents, but it also varies with the drying process. The raw coal has a high HHV than residual coal, biomass, and sewage sludge. It has ranged from 8 to 38 MJ/kg. Ash is the leftover residue after combustion at 900°C. The elemental analysis of char obtained from a sample of coal showed trace amounts of Li, B, Na, Mg, Al, P, K, Ca, Fe, and Ba [62]. Bhatt et al. reported the order of relative elemental abundance in coal as Si > Al > Fe > Ca > Mg > K > Na > Sr > V > Zn > Mn > Cr > Cu > Pb > Ni > Co > As > Cd [63]. According to the literature review, to obtain the maximum yield of liquid fuel through efficient pyrolysis operation, it is important to understand the properties, chemical composition, and behavior of different samples of coal. Bituminous coal has been used more often as it contains a higher amount of volatile matter, indicating its higher hydrocarbon potential. Depending on the region from where the coal was extracted, the amount of sulfur may vary between 1% and 4%. Sulfur is an undesirable constituent of coal; it requires a pretreatment step to eliminate to avoid SOx formation during combustion.Table 1
Elemental and chemical composition of coal.
YearSampleProximate analysis (wt.%)Ultimate analysis (wt.%)HHVRef.MoistureVolatilesAshFixed carbonCHNSOMJ/kg2017Coal8.5968.556.6216.1464.497.222.09—26.20—[52]2017Bituminous coal4.1830.5615.3849.8879.314.721.031.313.38—[53]2016Bituminous coal4.1830.5615.3849.8879.314.721.031.313.3825.44[54]2016South African coal2.129.413.970.670.583.991.770.637.9333.2[55]2016Bituminous coal—36.89.753.570.54.11.0—14.7—[56]2015Bituminous coal—34.3911.4356.9176.044.990.860.628.42—[57]2015Bituminous coal2.289.0916.5772.0674.502.661.390.4818.9628.10[58]2015Bituminous coal11.228.0130.3361.6662.072.301.162.211.9324.38[59]2014Bituminous coal4.1830.5615.3849.8879.314.721.021.313.3825.44[60]2014Bituminous coal3.3434.256.7055.7273.165.214.401.535.66—[61]


### 3.2. Ultimate, Proximate, and Chemical Composition Analysis of Lignocellulosic Biomass

Any organic material that can be burned and used as a fuel is called lignocellulosic biomass. It is the most convenient energy resource that can obtain different liquid fuels and bio-oils. Lignocellulosic biomass is a nonfossil and complex biogenic solid composed of many organic and inorganic constituents that originate from natural and technical resources. Natural resources are obtained from land- and water-based vegetation or generated by animal and human food digestion. Technical resources are obtained from the processing of the above natural resources [64]. Some of which are trees, shrubs, bamboos, grass, and plant leaves and waste such as food, rubbish, and industrial and municipal waste. Agriculture and forest residues are also called lignocellulosic biomass because they are composed of cellulose, hemicellulose, and lignin. Some lignocellulosic biomass may contain extractives up to 10% [65]. Lignocellulosic biomass shows high reactivity during conversion as they contain lower ash, carbon, sulfur, and nitrogen and usually contain a higher amount of volatile matters, hydrogen, oxygen, phosphorous, calcium, and magnesium. Ash obtained from lignocellulosic biomass can capture hazardous material. Using biomass in copyrolysis has many benefits, as these are widely available cheapest sustainable energy resource and neutralize CO2 in the atmosphere [66]. The chemical composition of lignocellulosic biomass affects thermal copyrolysis behavior. Lignocellulosic biomass containing a higher amount of hemicellulose and cellulose favors a high conversion rate during pyrolysis. The hemicellulose and cellulose degrade at a lower temperature range of 220–400°C while lignin degrades at a higher temperature of 500–900°C [67, 68]. The study of lignocellulosic constituents is relevant in copyrolysis as various constituents behave differently when subjected to thermal degradation. According to Naqvi and Naqvi, lignocellulosic biomass contains 35–50 wt.% cellulose, 20–40 wt.% hemicellulose, 20–27 wt.% lignin, and 1–10 wt.% extractives [26]. Properties differ among the biomass; their mixture or blends can be used to increase or reduce the required content at a certain level. Table 2 summarizes the proximate, ultimate, and chemical composition of different biomass samples. It can be observed that bagasse contains more volatiles than rice husk, showing that bagasse has higher thermal conversion ability than rice husk. Yu et al. find out that by increasing the pyrolysis temperature from 350–600°C, higher heating value (HHV) and volatile matter content of char were also increased [74]. Rice husk and corn stalk released CO2, CO, CH4, H2, and other light hydrocarbons after thermal conversion. Anil et al. investigated the physiochemical properties of various agricultural residues (cotton stalk, rice husk, rice straw, and baggase) in copyrolysis process [72]. It was observed that biomass has a higher percentage of volatile matter than that of coals and has a higher percentage of hemicellulose 47% as compared to cellulose and lignin. Table 3 depicts the elemental and chemical composition of products obtained from coal, lignocellulosic biomass, sludge, and their blends.Table 2
Elemental and chemical composition of lignocellulosic biomass.
YearBiomassProximate analysis (%)Ultimate analysis (%)Chemical composition (%)Ref.MoistureVolatilesAshFixed carbonCHNSOCelluloseHemicelluloseLignin2017Sugarcane bagasse6.2182.382.948.4745.37.920.15—46.6[69]2017Sugarcane bagasse8.584.005.861.6445.05.781.75—47.4[69]2017Rice husk10.8973.4115.1411.4441.96.341.850.4749.4[70]2017Rice husk9.567.616.66.349.22.20.400.0648.1[71]2016Sugarcane bagasse5.480.23.111.344.85.870.240.0648.947.63911.2[72]2016Sugarcane bagasse8.6473.281.7116.3741.66.210.370.0741.3[73]2016Rice husk8.859.226.214.635.64.50.190.0259.7353323[74]2015Sugarcane bagasse4.9973.52.4119.141.96.040.530.2448.835–5020–3020–27[75]2015Rice husk4.769.315.810.239.85.101.09—53.840.224.318.1[76]2015Rice husk3.5667.9314.8413.6744.86.350.42—48.3[77]2014Sugarcane bagasse4.9973.52.4119.141.96.040.530.2448.835–5020–302–27[76]2014Sugarcane bagasse—90.021.339.6047.16.140.30—46.4[78]2013Rice husk8.4368.2514.8316.9239.45.710.670.9954.141.5214.0433.67[79]2013Rice husk12.0860.5512.3515.245.45.400.480.0636.05[80]Table 3
Elemental and chemical composition of product obtained from coal, lignocellulosic biomass, sludge, and their blends.
Sample nameVolatile matter (%)Fixed carbon (%)Ash (%)Calorific value (MJ/kg)C (%)H (%)O (%)N (%)Ref.Apricot stone biochar19.8371.708.4730.76[81]Hazelnut shell biochar30.2663.166.5829.08Grapeseed biochar39.4550.969.5026.73Chestnut shell biochar34.3260.325.3625.86Microalgae + sewage sludge + coal mixtures9.80–15.8917.24–53.65[82](Bituminous coal + peanut shell) biochar45.12–8.4641.81–71.239.53–12.0323.99–28.7961.72–79.994.64–1.8321.38–2.070.28–0.20[83](Bituminous coal + wheat straw) biochar35.65–8.6753.36–77.998.15–11.8216.82–24.0749.81–70.293.99–1.9836.39–14.951.04–0.45Sewage sludge biochar43.9–12.54.1–2.752–84.1—25.7–9.42.8–0.366.8–89.54.7–1.1[84](Sewage sludge + rice husk) biochar63.2–31.60.4–2.936.4–65.535.8–26.33.9–0.657.8–71.32.8–1.8(Sewage sludge + sawdust) biochar75.1–44.82.1–5.722.8–52.542.5–39.55.0–1.550.9–56.61.6–2.4(Dewatered sewage sludge + pine sawdust) biochar5.6448.3646.035.871.6613.892.06[85]


### 3.3. Ultimate, Proximate, and Chemical Composition Analysis of Sewage Sludge

The major source of sewage sludge is municipal wastewater treatment plants. Sewage sludge is a complex mixture of organic and inorganic substances [86]. The organic constituents are mainly proteins, peptides, lipids, polysaccharides, and plant macromolecules with phenolic structures or aliphatic structures along with organic micropollutants such as polycyclic aromatic hydrocarbons. The inorganic materials come from soil and polymer waste [87]. Samolada and Zabaniotou find out that sewage sludge also contains some precarious materials such as heavy metals, organic pollutants, and pathogens [88]. In most of the studies, the sewage sludge was dried at a certain temperature (<110°C) to improve fuel quality. The dried lumps of sewage sludge were disintegrated to fine powder. Inguanzo et al. suggested the size range of sewage sludge used for different pyrolysis experiments in fixed bed systems [89]. Table 4 reviews the elemental and chemical composition of sewage sludge obtained from wastewater treatment plants. The volatile matters range between 38% and 70% and ash contents between 1 and 12%. As shown from the ultimate analysis, sewage sludge contains a higher percentage of carbon between 23% and 46% and a lower percentage of nitrogen and hydrogen contents. The extractives are slightly higher, about 7 wt.% dry ash free, than that present in biomasses. These extractives are composed of fatty acids, steroids, and aliphatic compounds and these extractives can improve the liquid fuel properties such as viscosity and heating value and can provide ease in phase separation of liquid fuels. Sewage sludge contains a relatively higher nitrogen content than lignocellulosic biomass [96]. This comes from the protein fragments of samples and can favor its usage in fertilizer [97]. The proximate analysis reveals that the sewage sludge has a high ash content than lignocellulosic biomass, and this study shows that ash removal system should be installed with reactor while using this type of material. The ash obtained as a result of sewage sludge pyrolysis contains minerals such as quartz and calcite. The elemental analysis gives information regarding the mineral composition in terms of Fe, Ca, Mg, and K which helps catalyze the pyrolysis reaction. Some heavy metals such as Cr, Ni, Co, Hg, Cd, Pb, and Zn are also present in sewage sludge [97]. Xu et al. found that sewage sludge contained 60.34% of volatile matters and a lower percentage of carbon content about 36.8% with a HHV of 14.90 MJ/kg [98]. According to the findings of Nadia et al., sewage sludge obtained from municipal wastewater treatment plant contained a higher percentage of carbon and oxygen and has a lower percentage of fixed carbon, ash, and nitrogen [84]. A higher amount of volatile matter makes sewage sludge a better candidate as a feedstock for thermal conversion. Sijiang et al. concluded that higher moisture content in the sewage sludge can lead to the hydrogen-rich fuel which can be compensated by the addition of volatile matters [85]. Xiong et al. described that sewage sludge contained a higher percentage of protein about 27% and a lower percentage of extractives about 9.9% [99].Table 4
Elemental and chemical composition of sewage sludge.
YearSewage sludgeProximate analysisUltimate analysisHVBiochemical compositionRef.M (%)VM (%)FC (%)Ash (%)C (%)H (%)N (%)S (%)O (%)MJ/kgProteinExtr.2017Municipal5.160.341.1333.4336.884.945.031.1452.0114.90——[90]2017Wastewater treatment plant75034027.94.74.51.434.612.50283.5[84]2016Wastewater treatment plant5.654.28.637.240.67.17.73.341.211.1——[91]2016Wastewater treatment plant7.463.17.122.538.05.16.91.219.0———[92]2016Wastewater treatment plant5.854.16.034.234.94.84.51.114.8———[93]2015Wastewater treatment plant8.7161.119.2026.8945.167.207.69—27.5916.18——[94]2014Wastewater treatment plant4.4368.5716.4215.0153.247.396.12—33.2524.2——[95]


### 3.4. Thermal Coconversion

#### 3.4.1. Copyrolysis

Copyrolysis is a simple and effective technique to obtain ideal liquid fuel or bio-oil. It is a process by which two or more different materials are mixed and used as feedstock. Copyrolysis of biomass can change the properties, quantity, and quality of liquid oil with no improvement in the system process. Copyrolysis has better applications in the industry than thermal cracking because of its attractive production and promising features. The successful feature of this technique is the combined effect of different materials. High yield of oil by using different blends of biomass with sewage sludge and coal has originated from hydrocarbons like paraffin, isoparaffins, olefins, naphthenes, and aromatics and a noncondensable gas [100]. The other main advantage of copyrolysis method is that it can reduce many environmental problems by reducing the amount of waste and avoiding disposal as landfills [101].The operating method and conditions of copyrolysis are the same as that of simple pyrolysis. The process is performed in a reactor system with optimum operating temperatures in the absence of an oxidizing environment to obtain liquid oils. There are three basic steps of the copyrolysis process: the preparation of feedstock, copyrolysis, and condensation [102]. Inert gas is optionally used to displace vapors from the pyrolysis zone. Residence time plays a vital role in minimizing secondary reactions and maximizing oil yield, and suitable residence time suggested by researchers is less than 2 seconds [103].Table4 shows a detailed description of the literature survey of the different types of biomass/coal and biomass/sewage sludge blends through copyrolysis, various types of reactors operated under different conditions and providing various products. Akhtar and Amin reviewed that oil yield obtained by the copyrolysis process of biomass, sewage sludge, and coal is also affected by many parameters including the type of biomass, temperature, heating rate, reaction time, and particle size of feed. 45 wt.% of the oil can be obtained by subjecting the biomass blend at the typical temperature range of 400–600°C, and the optimum temperature at which the maximum oil is obtained depends upon the type and characteristics of blends [104]. According to different reviews, the other very important parameter is the ratio of different blends which has a direct influence on the production of oil [105, 106]. The type of reactors can also influence the efficiency of copyrolysis process and can affect the quality and quantity of the product. The best conditions for obtaining a high yield of bio-oil are the high heating rate, moderate temperature, and short residence time. Each reactor has promising features to obtain a specific type of products. For example, for fast pyrolysis to obtain maximum liquid product, fluidized bed reactors are preferred over fixed bed reactors as their operation and scalability are simpler. Guo et al. investigated the co-pyrolytic behavior of biomass and coal and low heating rates (10–50°C/min) and higher heating rates (10°C/min) in tubular reactor and furnace and concluded that under inert atmospheric condition, the two fuels experience autonomous thermal conversion, but lower heating rates are better than higher heating rates in terms of better conversion [107]. Wang et al. explored the effect of residence time (30–150 min) on copyrolysis product of sewage sludge and biomass and concluded that extended residence times elevate the pH and ash contents of the biochars, but these conditions decreased the C, N, and H contents [108].


#### 3.4.2. Cocombustion

Cocombustion is a high-temperature thermochemical conversion technique in which sludge/coal, coal/biomass, and biomass/sludge blends undergo thermal degradation and release volatile matter such as CO, CO2, H2O, H2, CH4, and tar. Among all thermochemical conversion techniques, cocombustion is the only technique used to produce both heat and electricity. The advantages include low cost, high efficiency, and low emission of SOx and NOx. The main drawback of using cocombustion technique is its scale forming tendency in the boiler and limitation in using alkali metals. Due to unwanted changes in ash configurations, the proportion of biomass is usually kept limited to approximately 10% of the fuel intake. Cocombustion of biomass with coal is the most important technique with respect to the economic and environmental benefits to curb CO2 at a certain level [109]. Economically lower capital investment and lower amount of raw material are required, and the risk factor is minimal while using cocombustion techniques. Cocombustion techniques are further classified into three types; one is a direct cocombustion in which biomass or waste is directly fed into the reactor with coal (Figure 5).Figure 5
Cocombustion techniques: (a) direct cocombustion, (b) indirect cocombustion, and (c) parallel cocombustion [110].
(a)(b)(c)In this process, both feedstocks are milled directly and fed individually into the reactor. It has low flexibility; also, the possibility of producing slag and fouling is high. Other is the indirect cocombustion in which separate gasifier should be installed to convert solid feedstock into syngas. It is a more flexible technique, and the chance of slag formation and fouling is lower. Parallel cocombustion includes the setting up of a separate boiler to produce steam, which is useful in producing electricity. The parallel technique allows a greater amount of biomass and deals with contamination issues. The synergetic effect during cocombustion is usually articulated in terms of the high amount of gases, the high reactivity of the char during cocombustion, and reduction in harmful emission during cocombustion. Cocombustion operating parameters have a large influence on product quality and emission control. Xiao et al. studied the performance of sewage sludge and straw blends in cocombustion environment at heating rate of 10, 20, and 40°K·min−1 and concluded that better efficiency of cocombustion achieved at higher heating rates [111]. Munir et al. investigated the effect of the thermal ratio of different types of biomass in addition to municipal waste in cocombustion environment and found that the adding of biomass enlarged NO lessening under air stage conditions [112].


### 3.5. Blending Impact

Biomass, coal, and sewage sludge blends in feedstock greatly influence the amount and properties of products. The following are the key points.


#### 3.5.1. Blending Impact on Tar Release

Tar is defined as a mixture of aromatic compounds and derivatives of aromatic compounds produced under the partial oxidation environment at ambient to lower temperatures. The tar content produced during copyrolysis of lignocellulosic biomass, coal, and sewage sludge blends is one of the key factors affecting the succeeding process stages. It is one of the most stimulating elements of the syngas. The main factors that affect the yield of tar during copyrolysis are the type of feedstock and temperature. The blending of coal, sewage sludge, and lignocellulosic biomass particles can lower the yield of tar compared to the pyrolysis of individual feedstocks [113, 114]. Kumabe et al. found that increasing biomass ratio in a blend of lignocellulosic biomass and coal slightly decreased the yield of tar in a downdraft fixed bed reactor at 900°C [50]. Pinto et al. used a blend of 80% coal and 20% pine wood waste in a fluidized bed reactor operating at atmospheric pressure and at a temperature of 850–900°C [115]. They found that an increase in the polyethylene waste into the blend can cause an increase in tar release which can be attributed to the breaking down of the feed element into smaller elements by thermal cracking. This can be avoided by blending three materials: coal, polyethylene waste, and pine that brings down tar release. This effect can also be reduced by using a dolomite catalyst during the cocombustion of coal and biomass/waste mixtures [116]. Collot et al. experimented on a blend of Polish coal and forest residue and found no effect on synergy [117]. Aznar et al. and Andre et al. also acknowledged higher tar yield with an increase in the ratio of biomass percentage of the coal/biomass blend and found a greater impact on synergetic effect during cocombustion at specified conditions [49, 118]. More investigation is still required to briefly explain the issue regarding tar release and its impact on the synergy effect during thermal coconversion of different coal, lignocellulosic biomass, and sewage sludge blends.


#### 3.5.2. Blending Impact on Alkali and Ash

One of the major problems during thermal coconversion of blends is the deposition and formation of alkali and ash which can cause slagging, agglomeration, or fouling on the heat transfer surface of furnace and boiler because of the inorganic constituents of lignocellulosic biomass, waste, and coal mixture. The type of feedstock, operating condition, and flow dynamics have great influence on the characteristics of ash formation. Usually, ash obtained from lignocellulosic biomass has a low melting temperature as compared to ash obtained from coal, so it is necessary to pay attention to the behavior of ash produced from lignocellulosic biomass and coal mixture during copyrolysis or cocombustion. It is necessary to understand the different forms of alkali constituent present in blends and chemical reaction with a specific condition to investigate the ash produced from coal and biomass blends during thermal coconversion. Zheng et al. detected that the percentage of potassium in the fly ash is almost like the ash in the straw during combustion and the cocombustion process [119]. He determined that if the ash composition of the fuel and straw share are known, the total percentage of potassium in fly ash can be predicted. Condensation, vaporization, and agglomerations are the mechanisms used to produce ash during copyrolysis and cocombustion. Alkali metal and chloride present in biomass vaporize and KCl, NaCl, K2SO4, and Na2SO4 are formed. Strand et al. suggested two primary ways used to condense these vapors into particles: a homogeneous condensation in which vapor condenses into agglomerates and then into a particle, and the other is a heterogeneous condensation where the vapor on the surface of an existing particle entrains in the flue gas [120]. Wu et al. somewhat agree that the abrasive ash particles formed by mechanisms such as coalescence and shedding and fine particles are formed by vaporization and condensation mechanisms [121].


#### 3.5.3. Blending Impact on Char Characteristics

Bernardo et al. investigated the physical and chemical properties of chars obtained in the copyrolysis of three waste plastic, tires, and pine mixtures [122]. He concluded that the yield of char increases with the addition of tire because the addition of plastic waste in copyrolysis of pine biomass had no effect on char yield. The quality of char obtained from copyrolysis has a greater influence on the calorific value. Paradela et al. found that the char products obtained from the copyrolysis of a blend of biomass and plastic wastes have higher HHV than char obtained from pyrolysis of coal alone [116]. Brebu et al. concluded that char obtained from pyrolysis of pine cone contains higher oxygen content and lower calorific value than the char obtained from copyrolysis [123]. It was also found that the char contains less sulfur, so it can be easily used for the fuel in cocombustion of coal and lignocellulosic biomass. Another advantage of the char obtained from copyrolysis is its potential application as an absorbent to remove heavy metals.


## 3.1. Ultimate, Proximate, and Chemical Composition Analysis of Coal

Coal is the combustible material containing 50% by weight of carbon. It is a carbonaceous material with some percentage of hydrogen, oxygen, nitrogen, sulfur, and ash. Based on the fractions of hydrogen, oxygen, and carbon present in the sample, coal is ranked into four main categories such as bituminous coal, lignite, anthracite, and subbituminous coal [51]. Coal is usually dried at 105°C for 24 h in a muffle furnace or electric furnace to improve the high heating value (HHV). The raw hydrothermally treated moisture-free coal has some oxygenated functional group such as carboxyl, phenolic, hydroxyl, and all acidic groups. Table 1 shows the elemental composition, proximate analysis, and calorific value of the different coals. The ultimate analysis shows that coals contain higher carbon (60–90%). The proximate analysis shows volatiles between 38% and 40% which is less than that present in sewage sludge and bagasse. The calorific value of coal not only depends on the moisture, ash, and oxygen contents, but it also varies with the drying process. The raw coal has a high HHV than residual coal, biomass, and sewage sludge. It has ranged from 8 to 38 MJ/kg. Ash is the leftover residue after combustion at 900°C. The elemental analysis of char obtained from a sample of coal showed trace amounts of Li, B, Na, Mg, Al, P, K, Ca, Fe, and Ba [62]. Bhatt et al. reported the order of relative elemental abundance in coal as Si > Al > Fe > Ca > Mg > K > Na > Sr > V > Zn > Mn > Cr > Cu > Pb > Ni > Co > As > Cd [63]. According to the literature review, to obtain the maximum yield of liquid fuel through efficient pyrolysis operation, it is important to understand the properties, chemical composition, and behavior of different samples of coal. Bituminous coal has been used more often as it contains a higher amount of volatile matter, indicating its higher hydrocarbon potential. Depending on the region from where the coal was extracted, the amount of sulfur may vary between 1% and 4%. Sulfur is an undesirable constituent of coal; it requires a pretreatment step to eliminate to avoid SOx formation during combustion.Table 1
Elemental and chemical composition of coal.
YearSampleProximate analysis (wt.%)Ultimate analysis (wt.%)HHVRef.MoistureVolatilesAshFixed carbonCHNSOMJ/kg2017Coal8.5968.556.6216.1464.497.222.09—26.20—[52]2017Bituminous coal4.1830.5615.3849.8879.314.721.031.313.38—[53]2016Bituminous coal4.1830.5615.3849.8879.314.721.031.313.3825.44[54]2016South African coal2.129.413.970.670.583.991.770.637.9333.2[55]2016Bituminous coal—36.89.753.570.54.11.0—14.7—[56]2015Bituminous coal—34.3911.4356.9176.044.990.860.628.42—[57]2015Bituminous coal2.289.0916.5772.0674.502.661.390.4818.9628.10[58]2015Bituminous coal11.228.0130.3361.6662.072.301.162.211.9324.38[59]2014Bituminous coal4.1830.5615.3849.8879.314.721.021.313.3825.44[60]2014Bituminous coal3.3434.256.7055.7273.165.214.401.535.66—[61]


## 3.2. Ultimate, Proximate, and Chemical Composition Analysis of Lignocellulosic Biomass

Any organic material that can be burned and used as a fuel is called lignocellulosic biomass. It is the most convenient energy resource that can obtain different liquid fuels and bio-oils. Lignocellulosic biomass is a nonfossil and complex biogenic solid composed of many organic and inorganic constituents that originate from natural and technical resources. Natural resources are obtained from land- and water-based vegetation or generated by animal and human food digestion. Technical resources are obtained from the processing of the above natural resources [64]. Some of which are trees, shrubs, bamboos, grass, and plant leaves and waste such as food, rubbish, and industrial and municipal waste. Agriculture and forest residues are also called lignocellulosic biomass because they are composed of cellulose, hemicellulose, and lignin. Some lignocellulosic biomass may contain extractives up to 10% [65]. Lignocellulosic biomass shows high reactivity during conversion as they contain lower ash, carbon, sulfur, and nitrogen and usually contain a higher amount of volatile matters, hydrogen, oxygen, phosphorous, calcium, and magnesium. Ash obtained from lignocellulosic biomass can capture hazardous material. Using biomass in copyrolysis has many benefits, as these are widely available cheapest sustainable energy resource and neutralize CO2 in the atmosphere [66]. The chemical composition of lignocellulosic biomass affects thermal copyrolysis behavior. Lignocellulosic biomass containing a higher amount of hemicellulose and cellulose favors a high conversion rate during pyrolysis. The hemicellulose and cellulose degrade at a lower temperature range of 220–400°C while lignin degrades at a higher temperature of 500–900°C [67, 68]. The study of lignocellulosic constituents is relevant in copyrolysis as various constituents behave differently when subjected to thermal degradation. According to Naqvi and Naqvi, lignocellulosic biomass contains 35–50 wt.% cellulose, 20–40 wt.% hemicellulose, 20–27 wt.% lignin, and 1–10 wt.% extractives [26]. Properties differ among the biomass; their mixture or blends can be used to increase or reduce the required content at a certain level. Table 2 summarizes the proximate, ultimate, and chemical composition of different biomass samples. It can be observed that bagasse contains more volatiles than rice husk, showing that bagasse has higher thermal conversion ability than rice husk. Yu et al. find out that by increasing the pyrolysis temperature from 350–600°C, higher heating value (HHV) and volatile matter content of char were also increased [74]. Rice husk and corn stalk released CO2, CO, CH4, H2, and other light hydrocarbons after thermal conversion. Anil et al. investigated the physiochemical properties of various agricultural residues (cotton stalk, rice husk, rice straw, and baggase) in copyrolysis process [72]. It was observed that biomass has a higher percentage of volatile matter than that of coals and has a higher percentage of hemicellulose 47% as compared to cellulose and lignin. Table 3 depicts the elemental and chemical composition of products obtained from coal, lignocellulosic biomass, sludge, and their blends.Table 2
Elemental and chemical composition of lignocellulosic biomass.
YearBiomassProximate analysis (%)Ultimate analysis (%)Chemical composition (%)Ref.MoistureVolatilesAshFixed carbonCHNSOCelluloseHemicelluloseLignin2017Sugarcane bagasse6.2182.382.948.4745.37.920.15—46.6[69]2017Sugarcane bagasse8.584.005.861.6445.05.781.75—47.4[69]2017Rice husk10.8973.4115.1411.4441.96.341.850.4749.4[70]2017Rice husk9.567.616.66.349.22.20.400.0648.1[71]2016Sugarcane bagasse5.480.23.111.344.85.870.240.0648.947.63911.2[72]2016Sugarcane bagasse8.6473.281.7116.3741.66.210.370.0741.3[73]2016Rice husk8.859.226.214.635.64.50.190.0259.7353323[74]2015Sugarcane bagasse4.9973.52.4119.141.96.040.530.2448.835–5020–3020–27[75]2015Rice husk4.769.315.810.239.85.101.09—53.840.224.318.1[76]2015Rice husk3.5667.9314.8413.6744.86.350.42—48.3[77]2014Sugarcane bagasse4.9973.52.4119.141.96.040.530.2448.835–5020–302–27[76]2014Sugarcane bagasse—90.021.339.6047.16.140.30—46.4[78]2013Rice husk8.4368.2514.8316.9239.45.710.670.9954.141.5214.0433.67[79]2013Rice husk12.0860.5512.3515.245.45.400.480.0636.05[80]Table 3
Elemental and chemical composition of product obtained from coal, lignocellulosic biomass, sludge, and their blends.
Sample nameVolatile matter (%)Fixed carbon (%)Ash (%)Calorific value (MJ/kg)C (%)H (%)O (%)N (%)Ref.Apricot stone biochar19.8371.708.4730.76[81]Hazelnut shell biochar30.2663.166.5829.08Grapeseed biochar39.4550.969.5026.73Chestnut shell biochar34.3260.325.3625.86Microalgae + sewage sludge + coal mixtures9.80–15.8917.24–53.65[82](Bituminous coal + peanut shell) biochar45.12–8.4641.81–71.239.53–12.0323.99–28.7961.72–79.994.64–1.8321.38–2.070.28–0.20[83](Bituminous coal + wheat straw) biochar35.65–8.6753.36–77.998.15–11.8216.82–24.0749.81–70.293.99–1.9836.39–14.951.04–0.45Sewage sludge biochar43.9–12.54.1–2.752–84.1—25.7–9.42.8–0.366.8–89.54.7–1.1[84](Sewage sludge + rice husk) biochar63.2–31.60.4–2.936.4–65.535.8–26.33.9–0.657.8–71.32.8–1.8(Sewage sludge + sawdust) biochar75.1–44.82.1–5.722.8–52.542.5–39.55.0–1.550.9–56.61.6–2.4(Dewatered sewage sludge + pine sawdust) biochar5.6448.3646.035.871.6613.892.06[85]


## 3.3. Ultimate, Proximate, and Chemical Composition Analysis of Sewage Sludge

The major source of sewage sludge is municipal wastewater treatment plants. Sewage sludge is a complex mixture of organic and inorganic substances [86]. The organic constituents are mainly proteins, peptides, lipids, polysaccharides, and plant macromolecules with phenolic structures or aliphatic structures along with organic micropollutants such as polycyclic aromatic hydrocarbons. The inorganic materials come from soil and polymer waste [87]. Samolada and Zabaniotou find out that sewage sludge also contains some precarious materials such as heavy metals, organic pollutants, and pathogens [88]. In most of the studies, the sewage sludge was dried at a certain temperature (<110°C) to improve fuel quality. The dried lumps of sewage sludge were disintegrated to fine powder. Inguanzo et al. suggested the size range of sewage sludge used for different pyrolysis experiments in fixed bed systems [89]. Table 4 reviews the elemental and chemical composition of sewage sludge obtained from wastewater treatment plants. The volatile matters range between 38% and 70% and ash contents between 1 and 12%. As shown from the ultimate analysis, sewage sludge contains a higher percentage of carbon between 23% and 46% and a lower percentage of nitrogen and hydrogen contents. The extractives are slightly higher, about 7 wt.% dry ash free, than that present in biomasses. These extractives are composed of fatty acids, steroids, and aliphatic compounds and these extractives can improve the liquid fuel properties such as viscosity and heating value and can provide ease in phase separation of liquid fuels. Sewage sludge contains a relatively higher nitrogen content than lignocellulosic biomass [96]. This comes from the protein fragments of samples and can favor its usage in fertilizer [97]. The proximate analysis reveals that the sewage sludge has a high ash content than lignocellulosic biomass, and this study shows that ash removal system should be installed with reactor while using this type of material. The ash obtained as a result of sewage sludge pyrolysis contains minerals such as quartz and calcite. The elemental analysis gives information regarding the mineral composition in terms of Fe, Ca, Mg, and K which helps catalyze the pyrolysis reaction. Some heavy metals such as Cr, Ni, Co, Hg, Cd, Pb, and Zn are also present in sewage sludge [97]. Xu et al. found that sewage sludge contained 60.34% of volatile matters and a lower percentage of carbon content about 36.8% with a HHV of 14.90 MJ/kg [98]. According to the findings of Nadia et al., sewage sludge obtained from municipal wastewater treatment plant contained a higher percentage of carbon and oxygen and has a lower percentage of fixed carbon, ash, and nitrogen [84]. A higher amount of volatile matter makes sewage sludge a better candidate as a feedstock for thermal conversion. Sijiang et al. concluded that higher moisture content in the sewage sludge can lead to the hydrogen-rich fuel which can be compensated by the addition of volatile matters [85]. Xiong et al. described that sewage sludge contained a higher percentage of protein about 27% and a lower percentage of extractives about 9.9% [99].Table 4
Elemental and chemical composition of sewage sludge.
YearSewage sludgeProximate analysisUltimate analysisHVBiochemical compositionRef.M (%)VM (%)FC (%)Ash (%)C (%)H (%)N (%)S (%)O (%)MJ/kgProteinExtr.2017Municipal5.160.341.1333.4336.884.945.031.1452.0114.90——[90]2017Wastewater treatment plant75034027.94.74.51.434.612.50283.5[84]2016Wastewater treatment plant5.654.28.637.240.67.17.73.341.211.1——[91]2016Wastewater treatment plant7.463.17.122.538.05.16.91.219.0———[92]2016Wastewater treatment plant5.854.16.034.234.94.84.51.114.8———[93]2015Wastewater treatment plant8.7161.119.2026.8945.167.207.69—27.5916.18——[94]2014Wastewater treatment plant4.4368.5716.4215.0153.247.396.12—33.2524.2——[95]


## 3.4. Thermal Coconversion

### 3.4.1. Copyrolysis

Copyrolysis is a simple and effective technique to obtain ideal liquid fuel or bio-oil. It is a process by which two or more different materials are mixed and used as feedstock. Copyrolysis of biomass can change the properties, quantity, and quality of liquid oil with no improvement in the system process. Copyrolysis has better applications in the industry than thermal cracking because of its attractive production and promising features. The successful feature of this technique is the combined effect of different materials. High yield of oil by using different blends of biomass with sewage sludge and coal has originated from hydrocarbons like paraffin, isoparaffins, olefins, naphthenes, and aromatics and a noncondensable gas [100]. The other main advantage of copyrolysis method is that it can reduce many environmental problems by reducing the amount of waste and avoiding disposal as landfills [101].The operating method and conditions of copyrolysis are the same as that of simple pyrolysis. The process is performed in a reactor system with optimum operating temperatures in the absence of an oxidizing environment to obtain liquid oils. There are three basic steps of the copyrolysis process: the preparation of feedstock, copyrolysis, and condensation [102]. Inert gas is optionally used to displace vapors from the pyrolysis zone. Residence time plays a vital role in minimizing secondary reactions and maximizing oil yield, and suitable residence time suggested by researchers is less than 2 seconds [103].Table4 shows a detailed description of the literature survey of the different types of biomass/coal and biomass/sewage sludge blends through copyrolysis, various types of reactors operated under different conditions and providing various products. Akhtar and Amin reviewed that oil yield obtained by the copyrolysis process of biomass, sewage sludge, and coal is also affected by many parameters including the type of biomass, temperature, heating rate, reaction time, and particle size of feed. 45 wt.% of the oil can be obtained by subjecting the biomass blend at the typical temperature range of 400–600°C, and the optimum temperature at which the maximum oil is obtained depends upon the type and characteristics of blends [104]. According to different reviews, the other very important parameter is the ratio of different blends which has a direct influence on the production of oil [105, 106]. The type of reactors can also influence the efficiency of copyrolysis process and can affect the quality and quantity of the product. The best conditions for obtaining a high yield of bio-oil are the high heating rate, moderate temperature, and short residence time. Each reactor has promising features to obtain a specific type of products. For example, for fast pyrolysis to obtain maximum liquid product, fluidized bed reactors are preferred over fixed bed reactors as their operation and scalability are simpler. Guo et al. investigated the co-pyrolytic behavior of biomass and coal and low heating rates (10–50°C/min) and higher heating rates (10°C/min) in tubular reactor and furnace and concluded that under inert atmospheric condition, the two fuels experience autonomous thermal conversion, but lower heating rates are better than higher heating rates in terms of better conversion [107]. Wang et al. explored the effect of residence time (30–150 min) on copyrolysis product of sewage sludge and biomass and concluded that extended residence times elevate the pH and ash contents of the biochars, but these conditions decreased the C, N, and H contents [108].


### 3.4.2. Cocombustion

Cocombustion is a high-temperature thermochemical conversion technique in which sludge/coal, coal/biomass, and biomass/sludge blends undergo thermal degradation and release volatile matter such as CO, CO2, H2O, H2, CH4, and tar. Among all thermochemical conversion techniques, cocombustion is the only technique used to produce both heat and electricity. The advantages include low cost, high efficiency, and low emission of SOx and NOx. The main drawback of using cocombustion technique is its scale forming tendency in the boiler and limitation in using alkali metals. Due to unwanted changes in ash configurations, the proportion of biomass is usually kept limited to approximately 10% of the fuel intake. Cocombustion of biomass with coal is the most important technique with respect to the economic and environmental benefits to curb CO2 at a certain level [109]. Economically lower capital investment and lower amount of raw material are required, and the risk factor is minimal while using cocombustion techniques. Cocombustion techniques are further classified into three types; one is a direct cocombustion in which biomass or waste is directly fed into the reactor with coal (Figure 5).Figure 5
Cocombustion techniques: (a) direct cocombustion, (b) indirect cocombustion, and (c) parallel cocombustion [110].
(a)(b)(c)In this process, both feedstocks are milled directly and fed individually into the reactor. It has low flexibility; also, the possibility of producing slag and fouling is high. Other is the indirect cocombustion in which separate gasifier should be installed to convert solid feedstock into syngas. It is a more flexible technique, and the chance of slag formation and fouling is lower. Parallel cocombustion includes the setting up of a separate boiler to produce steam, which is useful in producing electricity. The parallel technique allows a greater amount of biomass and deals with contamination issues. The synergetic effect during cocombustion is usually articulated in terms of the high amount of gases, the high reactivity of the char during cocombustion, and reduction in harmful emission during cocombustion. Cocombustion operating parameters have a large influence on product quality and emission control. Xiao et al. studied the performance of sewage sludge and straw blends in cocombustion environment at heating rate of 10, 20, and 40°K·min−1 and concluded that better efficiency of cocombustion achieved at higher heating rates [111]. Munir et al. investigated the effect of the thermal ratio of different types of biomass in addition to municipal waste in cocombustion environment and found that the adding of biomass enlarged NO lessening under air stage conditions [112].


## 3.4.1. Copyrolysis

Copyrolysis is a simple and effective technique to obtain ideal liquid fuel or bio-oil. It is a process by which two or more different materials are mixed and used as feedstock. Copyrolysis of biomass can change the properties, quantity, and quality of liquid oil with no improvement in the system process. Copyrolysis has better applications in the industry than thermal cracking because of its attractive production and promising features. The successful feature of this technique is the combined effect of different materials. High yield of oil by using different blends of biomass with sewage sludge and coal has originated from hydrocarbons like paraffin, isoparaffins, olefins, naphthenes, and aromatics and a noncondensable gas [100]. The other main advantage of copyrolysis method is that it can reduce many environmental problems by reducing the amount of waste and avoiding disposal as landfills [101].The operating method and conditions of copyrolysis are the same as that of simple pyrolysis. The process is performed in a reactor system with optimum operating temperatures in the absence of an oxidizing environment to obtain liquid oils. There are three basic steps of the copyrolysis process: the preparation of feedstock, copyrolysis, and condensation [102]. Inert gas is optionally used to displace vapors from the pyrolysis zone. Residence time plays a vital role in minimizing secondary reactions and maximizing oil yield, and suitable residence time suggested by researchers is less than 2 seconds [103].Table4 shows a detailed description of the literature survey of the different types of biomass/coal and biomass/sewage sludge blends through copyrolysis, various types of reactors operated under different conditions and providing various products. Akhtar and Amin reviewed that oil yield obtained by the copyrolysis process of biomass, sewage sludge, and coal is also affected by many parameters including the type of biomass, temperature, heating rate, reaction time, and particle size of feed. 45 wt.% of the oil can be obtained by subjecting the biomass blend at the typical temperature range of 400–600°C, and the optimum temperature at which the maximum oil is obtained depends upon the type and characteristics of blends [104]. According to different reviews, the other very important parameter is the ratio of different blends which has a direct influence on the production of oil [105, 106]. The type of reactors can also influence the efficiency of copyrolysis process and can affect the quality and quantity of the product. The best conditions for obtaining a high yield of bio-oil are the high heating rate, moderate temperature, and short residence time. Each reactor has promising features to obtain a specific type of products. For example, for fast pyrolysis to obtain maximum liquid product, fluidized bed reactors are preferred over fixed bed reactors as their operation and scalability are simpler. Guo et al. investigated the co-pyrolytic behavior of biomass and coal and low heating rates (10–50°C/min) and higher heating rates (10°C/min) in tubular reactor and furnace and concluded that under inert atmospheric condition, the two fuels experience autonomous thermal conversion, but lower heating rates are better than higher heating rates in terms of better conversion [107]. Wang et al. explored the effect of residence time (30–150 min) on copyrolysis product of sewage sludge and biomass and concluded that extended residence times elevate the pH and ash contents of the biochars, but these conditions decreased the C, N, and H contents [108].


## 3.4.2. Cocombustion

Cocombustion is a high-temperature thermochemical conversion technique in which sludge/coal, coal/biomass, and biomass/sludge blends undergo thermal degradation and release volatile matter such as CO, CO2, H2O, H2, CH4, and tar. Among all thermochemical conversion techniques, cocombustion is the only technique used to produce both heat and electricity. The advantages include low cost, high efficiency, and low emission of SOx and NOx. The main drawback of using cocombustion technique is its scale forming tendency in the boiler and limitation in using alkali metals. Due to unwanted changes in ash configurations, the proportion of biomass is usually kept limited to approximately 10% of the fuel intake. Cocombustion of biomass with coal is the most important technique with respect to the economic and environmental benefits to curb CO2 at a certain level [109]. Economically lower capital investment and lower amount of raw material are required, and the risk factor is minimal while using cocombustion techniques. Cocombustion techniques are further classified into three types; one is a direct cocombustion in which biomass or waste is directly fed into the reactor with coal (Figure 5).Figure 5
Cocombustion techniques: (a) direct cocombustion, (b) indirect cocombustion, and (c) parallel cocombustion [110].
(a)(b)(c)In this process, both feedstocks are milled directly and fed individually into the reactor. It has low flexibility; also, the possibility of producing slag and fouling is high. Other is the indirect cocombustion in which separate gasifier should be installed to convert solid feedstock into syngas. It is a more flexible technique, and the chance of slag formation and fouling is lower. Parallel cocombustion includes the setting up of a separate boiler to produce steam, which is useful in producing electricity. The parallel technique allows a greater amount of biomass and deals with contamination issues. The synergetic effect during cocombustion is usually articulated in terms of the high amount of gases, the high reactivity of the char during cocombustion, and reduction in harmful emission during cocombustion. Cocombustion operating parameters have a large influence on product quality and emission control. Xiao et al. studied the performance of sewage sludge and straw blends in cocombustion environment at heating rate of 10, 20, and 40°K·min−1 and concluded that better efficiency of cocombustion achieved at higher heating rates [111]. Munir et al. investigated the effect of the thermal ratio of different types of biomass in addition to municipal waste in cocombustion environment and found that the adding of biomass enlarged NO lessening under air stage conditions [112].


## 3.5. Blending Impact

Biomass, coal, and sewage sludge blends in feedstock greatly influence the amount and properties of products. The following are the key points.


### 3.5.1. Blending Impact on Tar Release

Tar is defined as a mixture of aromatic compounds and derivatives of aromatic compounds produced under the partial oxidation environment at ambient to lower temperatures. The tar content produced during copyrolysis of lignocellulosic biomass, coal, and sewage sludge blends is one of the key factors affecting the succeeding process stages. It is one of the most stimulating elements of the syngas. The main factors that affect the yield of tar during copyrolysis are the type of feedstock and temperature. The blending of coal, sewage sludge, and lignocellulosic biomass particles can lower the yield of tar compared to the pyrolysis of individual feedstocks [113, 114]. Kumabe et al. found that increasing biomass ratio in a blend of lignocellulosic biomass and coal slightly decreased the yield of tar in a downdraft fixed bed reactor at 900°C [50]. Pinto et al. used a blend of 80% coal and 20% pine wood waste in a fluidized bed reactor operating at atmospheric pressure and at a temperature of 850–900°C [115]. They found that an increase in the polyethylene waste into the blend can cause an increase in tar release which can be attributed to the breaking down of the feed element into smaller elements by thermal cracking. This can be avoided by blending three materials: coal, polyethylene waste, and pine that brings down tar release. This effect can also be reduced by using a dolomite catalyst during the cocombustion of coal and biomass/waste mixtures [116]. Collot et al. experimented on a blend of Polish coal and forest residue and found no effect on synergy [117]. Aznar et al. and Andre et al. also acknowledged higher tar yield with an increase in the ratio of biomass percentage of the coal/biomass blend and found a greater impact on synergetic effect during cocombustion at specified conditions [49, 118]. More investigation is still required to briefly explain the issue regarding tar release and its impact on the synergy effect during thermal coconversion of different coal, lignocellulosic biomass, and sewage sludge blends.


### 3.5.2. Blending Impact on Alkali and Ash

One of the major problems during thermal coconversion of blends is the deposition and formation of alkali and ash which can cause slagging, agglomeration, or fouling on the heat transfer surface of furnace and boiler because of the inorganic constituents of lignocellulosic biomass, waste, and coal mixture. The type of feedstock, operating condition, and flow dynamics have great influence on the characteristics of ash formation. Usually, ash obtained from lignocellulosic biomass has a low melting temperature as compared to ash obtained from coal, so it is necessary to pay attention to the behavior of ash produced from lignocellulosic biomass and coal mixture during copyrolysis or cocombustion. It is necessary to understand the different forms of alkali constituent present in blends and chemical reaction with a specific condition to investigate the ash produced from coal and biomass blends during thermal coconversion. Zheng et al. detected that the percentage of potassium in the fly ash is almost like the ash in the straw during combustion and the cocombustion process [119]. He determined that if the ash composition of the fuel and straw share are known, the total percentage of potassium in fly ash can be predicted. Condensation, vaporization, and agglomerations are the mechanisms used to produce ash during copyrolysis and cocombustion. Alkali metal and chloride present in biomass vaporize and KCl, NaCl, K2SO4, and Na2SO4 are formed. Strand et al. suggested two primary ways used to condense these vapors into particles: a homogeneous condensation in which vapor condenses into agglomerates and then into a particle, and the other is a heterogeneous condensation where the vapor on the surface of an existing particle entrains in the flue gas [120]. Wu et al. somewhat agree that the abrasive ash particles formed by mechanisms such as coalescence and shedding and fine particles are formed by vaporization and condensation mechanisms [121].


### 3.5.3. Blending Impact on Char Characteristics

Bernardo et al. investigated the physical and chemical properties of chars obtained in the copyrolysis of three waste plastic, tires, and pine mixtures [122]. He concluded that the yield of char increases with the addition of tire because the addition of plastic waste in copyrolysis of pine biomass had no effect on char yield. The quality of char obtained from copyrolysis has a greater influence on the calorific value. Paradela et al. found that the char products obtained from the copyrolysis of a blend of biomass and plastic wastes have higher HHV than char obtained from pyrolysis of coal alone [116]. Brebu et al. concluded that char obtained from pyrolysis of pine cone contains higher oxygen content and lower calorific value than the char obtained from copyrolysis [123]. It was also found that the char contains less sulfur, so it can be easily used for the fuel in cocombustion of coal and lignocellulosic biomass. Another advantage of the char obtained from copyrolysis is its potential application as an absorbent to remove heavy metals.


## 3.5.1. Blending Impact on Tar Release

Tar is defined as a mixture of aromatic compounds and derivatives of aromatic compounds produced under the partial oxidation environment at ambient to lower temperatures. The tar content produced during copyrolysis of lignocellulosic biomass, coal, and sewage sludge blends is one of the key factors affecting the succeeding process stages. It is one of the most stimulating elements of the syngas. The main factors that affect the yield of tar during copyrolysis are the type of feedstock and temperature. The blending of coal, sewage sludge, and lignocellulosic biomass particles can lower the yield of tar compared to the pyrolysis of individual feedstocks [113, 114]. Kumabe et al. found that increasing biomass ratio in a blend of lignocellulosic biomass and coal slightly decreased the yield of tar in a downdraft fixed bed reactor at 900°C [50]. Pinto et al. used a blend of 80% coal and 20% pine wood waste in a fluidized bed reactor operating at atmospheric pressure and at a temperature of 850–900°C [115]. They found that an increase in the polyethylene waste into the blend can cause an increase in tar release which can be attributed to the breaking down of the feed element into smaller elements by thermal cracking. This can be avoided by blending three materials: coal, polyethylene waste, and pine that brings down tar release. This effect can also be reduced by using a dolomite catalyst during the cocombustion of coal and biomass/waste mixtures [116]. Collot et al. experimented on a blend of Polish coal and forest residue and found no effect on synergy [117]. Aznar et al. and Andre et al. also acknowledged higher tar yield with an increase in the ratio of biomass percentage of the coal/biomass blend and found a greater impact on synergetic effect during cocombustion at specified conditions [49, 118]. More investigation is still required to briefly explain the issue regarding tar release and its impact on the synergy effect during thermal coconversion of different coal, lignocellulosic biomass, and sewage sludge blends.


## 3.5.2. Blending Impact on Alkali and Ash

One of the major problems during thermal coconversion of blends is the deposition and formation of alkali and ash which can cause slagging, agglomeration, or fouling on the heat transfer surface of furnace and boiler because of the inorganic constituents of lignocellulosic biomass, waste, and coal mixture. The type of feedstock, operating condition, and flow dynamics have great influence on the characteristics of ash formation. Usually, ash obtained from lignocellulosic biomass has a low melting temperature as compared to ash obtained from coal, so it is necessary to pay attention to the behavior of ash produced from lignocellulosic biomass and coal mixture during copyrolysis or cocombustion. It is necessary to understand the different forms of alkali constituent present in blends and chemical reaction with a specific condition to investigate the ash produced from coal and biomass blends during thermal coconversion. Zheng et al. detected that the percentage of potassium in the fly ash is almost like the ash in the straw during combustion and the cocombustion process [119]. He determined that if the ash composition of the fuel and straw share are known, the total percentage of potassium in fly ash can be predicted. Condensation, vaporization, and agglomerations are the mechanisms used to produce ash during copyrolysis and cocombustion. Alkali metal and chloride present in biomass vaporize and KCl, NaCl, K2SO4, and Na2SO4 are formed. Strand et al. suggested two primary ways used to condense these vapors into particles: a homogeneous condensation in which vapor condenses into agglomerates and then into a particle, and the other is a heterogeneous condensation where the vapor on the surface of an existing particle entrains in the flue gas [120]. Wu et al. somewhat agree that the abrasive ash particles formed by mechanisms such as coalescence and shedding and fine particles are formed by vaporization and condensation mechanisms [121].


## 3.5.3. Blending Impact on Char Characteristics

Bernardo et al. investigated the physical and chemical properties of chars obtained in the copyrolysis of three waste plastic, tires, and pine mixtures [122]. He concluded that the yield of char increases with the addition of tire because the addition of plastic waste in copyrolysis of pine biomass had no effect on char yield. The quality of char obtained from copyrolysis has a greater influence on the calorific value. Paradela et al. found that the char products obtained from the copyrolysis of a blend of biomass and plastic wastes have higher HHV than char obtained from pyrolysis of coal alone [116]. Brebu et al. concluded that char obtained from pyrolysis of pine cone contains higher oxygen content and lower calorific value than the char obtained from copyrolysis [123]. It was also found that the char contains less sulfur, so it can be easily used for the fuel in cocombustion of coal and lignocellulosic biomass. Another advantage of the char obtained from copyrolysis is its potential application as an absorbent to remove heavy metals.


## 4. Behavior of Thermal Coconversion through TGA

The behavior of thermal coconversion or synergetic effect of different types of coal, lignocellulosic biomass, and sewage sludge can be obtained by using thermal analysis tools such as thermogravimetric (TGA), derivative thermogravimetric (DTG), and differential scanning calorimetric (DSC) analyses (Table5). TGA is an important tool to measure the percentage of mass loss with respect to temperature and time and to examine the thermal decomposition behavior during pyrolysis. A detailed review of TGA and kinetics of degradation of substances during pyrolysis can help in plan and develop the pyrolysis process [132]. According to different results obtained by TGA, pyrolysis of biomass is usually divided into three main stages; in the first stage, removal of moisture takes place at the temperature range of less than 200°C. In the second stage, from a temperature range of 200–600°C, the main decomposition of substance occurs due to devolatilization and oxidation.Table 5
Thermal coconversion of different samples by using copyrolysis and cocombustion techniques.
YearSampleSample ratio (%)Reactor typeExperimental conditionsProductObservationsRef.TemperatureResidence timeHeating rateFeed2017Sewage sludge + lignocellulosic biomassSS : B20 : 8040 : 6060 : 4080 : 20Moving bed reactor25–1200°C30 min—200 kg/hSyngas (H2 + CO)H2 content increased from 33% to 47% in blending of 60%SS + 40%biomass[124]2017Coal + lignocellulosic biomassCoal : B100 : 050 : 50Tubular furnace25–900°C40 min10°C/min25 gAshAsh properties were performed for leaching test[57]2016Rice husk + plastic wasteRH : PW20 : 8030 : 7040 : 6050 : 50Batch reactor25–800°C35 min5-6°C/min—Bio-oilAround 66% of liquid compounds can be obtained by copyrolysis of 20% of RH blended with plastic waste.More than 20% RH is not favored for liquid oil production[125]2016Coal + lignocellulosic biomassCoal : B0:10025 : 7550 : 5075 : 25100 : 0Moving bed pyrolyzer500–850°C2 h—200 g/hGases and tarTar and gas yields showed an incremental trend with the increase in biomass ratio[99]2015Sewage sludge + rice huskSS : RH50 : 50Vacuum fixed bed reactor900°C2 h10°C/min10 gGas productsHigher amount of SS promoted CO2-C and H2O-C gasification reactions[126]2015Bituminous coal + rice huskB : coal0:10020 : 8040 : 6080 : 40100 : 0Fixed bed reactorUp to 900°C15 min10–30°C/min—BiofuelsExperimental and calculated value observed differently for blended samples[127]2015Sugarcane bagasse + sewage sludgeSS : SB50 : 5025 : 75Pyrolyzer25–600°C—10°C/min10 mgBiofuelsCocombustion process showed lower activation energy[128]2014Sewage sludge + lignocellulosic biomassSS : B0:10030 : 7050 : 5070 : 30100 : 0TG-MS40–800°C—10°C/min10 mgGas productsCO2, SO2, NH3, HCN, and NO were mainly gaseous species produced at temperature of 523–873°K[60]2013Sewage sludge + rice huskSS : RH0:10010 : 9020 : 8030 : 7050 : 5070 : 30100 : 0Fixed bed reactor25–900°C1-2 s10°C/min2 gBio-oil, biogasWithout external heat source, copyrolysis could be the technology to dispose excessive sludge[129]2013Sewage sludge + biomassSS : B0:100100 : 090 : 1080 : 2070 : 3060 : 40Fixed bed tubular reactor25–800°C—40°C/min10 mgBio-oil, biogasPresence of petroleum sludge promotes NH3 and HCN formation with biomass coconversion[130]2012Biomass + waste materialsB : WM30 : 7050 : 50Autoclave450°C15 min5°C/min—Bio-oil, char, gasesA recovery of 63–81% of the pyrolysis oils was observed[94]2011Sewage sludge + rice huskSS : RH70 : 3050 : 5030 : 70Fluidized bed reactor500–650°C2 s30°C/min—Bio-oilCombination of feedstock helps in maximizing the volume of feedstock for energy conversion via pyrolysis[131]Usually, during this stage cellulose, hemicellulose and lignin decompose and this stage is further subdivided into two parts; in the first part, at lower temperature range (200–450°C), cellulose and hemicellulose of any biomass sample decompose, and at a higher temperature (455°C to 1000°C), lignin is thermally degraded. In the third stage, at a temperature above 600°C, the reduction in the decomposition reaction occurs due to oxidation of char and remaining substance. The leftover material after complete burning is called ash. Ash contains different types of metallic substances that act as catalysts during the pyrolysis process. The weight of the sample in TGA can be varied from 1 to 150 mg, and sample weight greater than 10 mg is often reported with a sensitivity of 0.01 mg. However, lower sample weight of 1-2 mg is usually preferred, making sure the interior sample temperature remains close to the measured furnace temperature. The sample can be loaded in TGA as a fine powder or small pieces. DTG is a simple analytical tool to determine the amount of mass loss rate as a function of temperature. By examining the DTG curves, the temperature at which maximum rate mass loss appears can be determined by the position of the peaks in the curve. It is also used to find out the kinetic parameters (activation energy, preexponential factor, and order of reaction) of different organic materials during isothermal and nonisothermal conditions.


### 4.1. Thermogravimetric Analysis of Coal/Biomass Blends

The thermal coconversion of lignocellulosic biomass and coal blends has the advantage of reducing greenhouse gas emissions, such as sulfur oxides (SOx) and nitrogen oxides (NOx) [5]. The conversion of different types of lignocellulosic biomass such as sugarcane bagasse and rice husk blended with coal can be easily realized cheaply with minor modifications in the current coal operating plants to adopt the use of blend. Coconversion of coal and lignocellulosic biomass gives the advantage of using cleaner feedstock to dispose of wastes/biomass safely and economically [133]. Cothermal characteristics of coal and lignocellulosic biomass blends can be examined widely by thermal analytical techniques such as TG, DTG, and DTA. TGA can rapidly assess the fuel value, the initial temperature at which degradation of component starts, and the final temperature at which degradation of component ends, and other characteristics such as maximum reactivity temperature, the rate of maximum reactivity, and amount of final residue. Thermal methods such as TG, DTG, and DTA have been used extensively to study a variety of thermal characteristics and parameters for the thermal conversion of different materials with coal. Thermal analysis can be used also to estimate kinetic parameters of different thermal processes. The main concern of the thermogravimetric study is to show that the decrease in particle size can cause a decline in ignition temperature. Thermal analysis of different coal and lignocellulosic biomass samples showed different stages in terms of temperature ranges during pyrolysis, combustion, and gasification processes. In coal-biomass blends, three different stages can be commonly observed. During the first stage, removal of moisture is carried out, and during the second stage, decomposition of cellulose and hemicellulose components occurs, and in the third stage, lignin degradation can be observed. By using the blends of biomass and coal, the decomposition of biomass is more dominant in the second stage than the decomposition of coal and the third stage is decomposition of coal with residual biomass. The major gaseous pollutants released from the thermal processes CO, CO2, CH4, NO, and SO2 were studied previously by TG-DTA. The thermal behavior of the material during thermal analysis techniques depend on heating rates (5, 10, 20, 30, 40, 50, and 100°C/min), reacting medium or environment (inert and oxidative by using N2, argon, O2, and CO2), mass and size of the sample used, and temperature ranges to be operated. These parameters can affect the product distribution and percentage of solid-liquid and gaseous fuels. Knowledge of these parameters can help to optimize the process. Table 6 gives a detailed description of a literature survey on the thermal behavior of various biomass and coal blends using different thermal analysis techniques. The commonly used blend ratios are 1 : 1, 2 : 3, 3 : 4, 4 : 3, and 3 : 2. Recently, Kandasamy Jayaraman et al. studied coal and biomass blends and they concluded that by increasing the ratio of biomass in the blends, the mass loss percentage increases, indicating the high reactivity of samples, and the activation energies were also increased by increasing biomass ratio in the blends [57]. Betancur et al. studied that coal and biomass blends increased combustion efficiency [124]. Blends showed lower ignition temperatures, and activation energies were decreased in the CO2 environment as compared to N2. Guangwei Wang et al. stated the synergistic effect of the combustion process of coal and biomass blends was prevalent as they increased the ignition performance by increasing the ratio of biomass [125]. Li et al. studied the copyrolysis of the coal and biomass blends and indicated the deviations in weight fractions [127].Table 6
A list of literature about the thermal coconversion of coal and lignocellulosic biomass using thermogravimetric analysis.
YearSampleExperimental facilityBlends coal : biomassThermal behaviorMediumInitial mass (mg)Heating rate (°C/min)Temperature range (°C)TvaTfb−DTGmaxcTDTGmaxd (°C)Ref.2017Coal and bagasseTGA-DTG80 : 20CombustionCO212525–9004603806045701.8%/°C0.8/°C300, 470[124]2017Coal and hazelnut shellTGA-DTG with MS25 : 7550 : 5075 : 25CombustionAir102025–95037636334960263363512%/min10%/min7%/min415416425[57]2016Coal and rice huskTG-DTA80 : 2060 : 4040 : 6020 : 80CombustionAir52.55102025–9005745455345247727707607492.4%/°C1.5%/°C1.0%/°C1.3%/°C738737722598[125]2015Bituminous coal and rice strawTG-DTG80 : 2060 : 4040 : 6020 : 80PyrolysisNitrogen—101520253025–900220–240346–7400.08–0.5%/°C330–350[127]2015Coal and sugarcane bagasseTG-DTG80 : 2060 : 4040 : 6020 : 80PyrolysisNitrogen251025–11001609000.16%/°C0.31%/°C0.49%/°C0.63%/°C308, 353, 440[134]2014Bituminous coal and bagasseTG-DTG75 : 25PyrolysisNitrogen1010204025–950318, 208, 271346, 293, 4615.8%/min1.2%/min346, 293, 349[60]2014Coal and bagasseTG-DTA4 : 13 : 21 : 12 : 31 : 4GasificationCO220525–13002952942962902914163903843763740.99%/°C1.77%/°C2.11%/°C2.50%/°C3.28%/°C346345344344343[135]2013Coal and sugarcane bagasseTG-DTG90 : 1080 : 2070 : 3060 : 4050 : 50PyrolysisNitrogen5–252025–900210–390390–4509–10.8%/min210, 365[136]2013Lignite and rice huskTG-DTA0.20.40.60.8PyrolysisNitrogen51025–800200400—330, 490[137]2013Bituminous coal and sugarcane bagasseTG-DTA75 : 25CombustionAir72.551020253025–7502006000.05%/min330[138]a = Tv; b = Tf; c = −DTGmax; d = TDTGmax.


### 4.2. Thermogravimetric Analysis of Sewage Sludge/Biomass Blends

Cothermal processes such as copyrolysis and cocombustion of sewage sludge with different types of lignocellulosic biomass can be applied for converting sewage sludge into useful energy and construction materials [139]. The other advantage of copyrolysis and cocombustion can help in reducing hazardous emissions to the atmosphere. Sludge has a low HHV, so burning of sewage sludge alone is neither cost-effective nor environmentally friendly. The blending of sewage sludge with lignocellulosic biomass material can make burning easier. The physical and chemical properties of the different materials used can affect the characteristics of the thermal process and residue obtained [140]. TGA is effective in studying the thermal behavior and characteristics of combustion of sewage sludge, biomass, coal, and other materials [141, 142]. It is an important technique to measure the percentage of mass loss of a sample with respect to temperature and time and to examine the thermal decomposition behavior during copyrolysis and cocombustion. It is also helpful in studying the kinetics of degradation of organic material during copyrolysis and cocombustion processes. Thermal degradation is a key element in designing sustainable copyrolysis and cocombustion processes. The thermal degradation of lignocellulosic biomass and sewage sludge is a very complicated process because of a variety of reactions. Conversion of different solid biomass and sewage sludge blends to gaseous and liquid products is difficult and complicated, so TG-DTA can be helpful by interpreting the kinetics to better understand the cocombustion and copyrolysis processes. The advantage of TGA is that it can easily assess the fuel value and the temperature at which combustion, pyrolysis, and gasification start and end. It can provide information about the highest reactivity temperature, the total amount of ash remaining, and complete burning time, and these techniques are important to study the thermal behavior of the pyrolysis process. The other advantage of TG-DTA is that it can determine the purity of mineral, organic, and inorganic compounds [75]. Ergudenler et al. describe that the weight of the sample can be varied from range 1–150 mg; usually, the weight of sample greater than 10 mg is preferred with a sensitivity of 0.01 mg. But if the excellent results are required, weight must be 1-2 mg [143].Table7 describes the detailed description of the literature about the TG-DTA analysis of a different type of sample to study the pyrolysis and copyrolysis behavior under certain conditions. Mian Hu et al. stated that by blending sewage sludge with biomass (pine sawdust), the devolatilization properties of sewage sludge increased whereas the initial decomposition temperatures increased by increasing biomass ratio [144]. Jiang et al. stated that by increasing the ratio of biomass with sewage sludge, the reactivity of blends increases [145]. Yang et al. studied the synergistic effect of copyrolysis of sewage sludge and wheat straw. The synergistic effect resulted in speeding up the pyrolysis process, the increase in the volatiles, and reduction in char yield. The synergistic effect was maximum at a biomass proportion of 60% [146].Table 7
A list of literature about the thermal coconversion of sewage sludge and lignocellulosic biomass using thermogravimetric analysis.
YearSampleExperimental facilityBlending SS : BiomassThermal behaviorMediumInitial Mass mgTemp range (°C)Heating rate (°C/min)TvaTfb−DTGmaxc (%/min)TDTGmaxc (°C)Ref.2017Rice husk and sewage sludgeTG-DTG70 : 3050 : 5030 : 70CombustionAir1025–100025272.1269.1264.8532.5559.6547.59.7510.9010.05333.8295.1338.5[77]2016Sewage sludge and rice strawTG-DTA25 : 7550 : 2.5075 : 25CombustionAir525–80020263258269765745714912.530299.2299.3293.1[78]2016Sewage sludge and biomassTG-DTA80 : 2060 : 4040 : 6020 : 80PyrolysisNitrogen—30–1000201791801811827277196036023433443443446.548.5410.5912.68[79]2015Sludge + lingo- cellulosic biomassTG-DTA50 : 50PyrolysisNitrogen1025–90015200575–3702015Sewage sludge and rice strawTG-DTA50 : 50PyrolysisNitrogen—150–50020200500163302015Sewage sludge and sawdustTG-DTA25 : 7550 : 5075 : 25PyrolysisNitrogen1025–100010315900–6502013Sewage sludge and rice huskTG-DTG10 : 9020 : 8030 : 7050 : 5070 : 30PyrolysisNitrogen1025–900202005006.05310a = Tv; b = Tf; c = −DTGmax; d = TDTGmax.


### 4.3. Thermogravimetric Analysis of Coal/Sewage Sludge Blends

TGA is a useful tool to examine the copyrolysis and cocombustion behavior of sewage sludge, coal, and their mixture. Different atmospheric conditions (inert condition for copyrolysis and oxidizing condition for cocombustion) can be used.Table8 describes the detailed description of thermal coconversion of coal and sewage sludge obtained from different sources through thermogravimetric analysis to examine the copyrolysis or cocombustion characteristics. Previous studies on the TGA of thermal coconversion of coal and dewatered sewage sludge blends show that the addition of 10% of sewage sludge in the coal-sludge blend has hardly brought any change in heat release and weight loss during thermal coconversion processes [147, 148]. Barbosa et al. worked on the sewage sludge and coal blend impregnated with molasses to study the cocombustion characteristics and found that fuel quality obtained from this type of blend was improved [149]. But the char characteristics remained the same as that of bituminous coal. Zhuo et al. experimented on 80% coal and 20% sludge blends to study the cocombustion behavior under N2/O2 and CO2/O2 atmosphere and find out that blend gives distinctive combustion peaks as compared to combustion of sludge [150]. Jin et al. studied the influence of the blend ratio of 60% coal and 40% dewatered sewage sludge on flammability index, combustion characteristic index, and release of harmful emission and heavy metals [151]. This effect is ignorable if the dewatered sewage sludge ratio is kept at less than 20%. Coimbra et al. studied the copyrolysis and cocombustion behavior of bituminous coal and pulp mill sludge blend of ratio 90 : 10 and concluded that cocombustion behavior of blend is similar to that of conversion behavior of coal alone, but the copyrolysis of blends occurs at lower devolatilization temperature than that of pyrolysis of coal [52]. Zhang et al. also studied the combustion characteristics of blends of different ratios of sewage sludge and coal [53]. Xia and Li concluded from their result that the TG and DTG profiles of sewage sludge should be the same as the profile of coal but different from coal under different blending ratios [152].Table 8
A list of literature pertaining to the thermal coconversion of coal and sludge using thermogravimetric analysis.
YearSampleExperimental facilityBlends coal : sludgeThermal behaviorMediumInitial mass (mg)Temperature range (°C)Heating rate (C/min)TvaTfbDTGmaxc (%/min)TDTGmaxc (°C)Reference2017Coal and sewage sludgeTGA-DTG50 : 50CocombustionAir1525–800202006000.80450[82]2017Coal and textile dying sludgeTGA-DSC80 : 20CocombustionAir10.520–100020536.6682.711.4605.7[83]2016Coal and sewage sludgeTGA-DTG40 : 20CocombustionAir1020–1000254288001.5550[90]2016Bituminous coal and sludgeTG-DTG90 : 10CopyrolysisN22525–1200547512000.0114605[91]2016Bituminous coal and sludgeTG-DTG90 : 10CocombustionO22525–1200550511050.1128900[91]2015Coal and sewage sludgeTG-DTG1 : 1, 2 : 1, 3 : 1CocombustionAir530–9002020065010450[92]2014Coal and sewage sludgeTG-DTG10 : 90, 20 : 80, 30 : 70, 50 : 50CopyrolysisN21025–1200302008500.16420[93]2013Coal and sewage sludgeTG-DTG90 : 10CocombustionAir1525–100010, 40, 1002008000.03450a = Tv; b = Tf; c = −DTGmax; d = TDTGmax.


## 4.1. Thermogravimetric Analysis of Coal/Biomass Blends

The thermal coconversion of lignocellulosic biomass and coal blends has the advantage of reducing greenhouse gas emissions, such as sulfur oxides (SOx) and nitrogen oxides (NOx) [5]. The conversion of different types of lignocellulosic biomass such as sugarcane bagasse and rice husk blended with coal can be easily realized cheaply with minor modifications in the current coal operating plants to adopt the use of blend. Coconversion of coal and lignocellulosic biomass gives the advantage of using cleaner feedstock to dispose of wastes/biomass safely and economically [133]. Cothermal characteristics of coal and lignocellulosic biomass blends can be examined widely by thermal analytical techniques such as TG, DTG, and DTA. TGA can rapidly assess the fuel value, the initial temperature at which degradation of component starts, and the final temperature at which degradation of component ends, and other characteristics such as maximum reactivity temperature, the rate of maximum reactivity, and amount of final residue. Thermal methods such as TG, DTG, and DTA have been used extensively to study a variety of thermal characteristics and parameters for the thermal conversion of different materials with coal. Thermal analysis can be used also to estimate kinetic parameters of different thermal processes. The main concern of the thermogravimetric study is to show that the decrease in particle size can cause a decline in ignition temperature. Thermal analysis of different coal and lignocellulosic biomass samples showed different stages in terms of temperature ranges during pyrolysis, combustion, and gasification processes. In coal-biomass blends, three different stages can be commonly observed. During the first stage, removal of moisture is carried out, and during the second stage, decomposition of cellulose and hemicellulose components occurs, and in the third stage, lignin degradation can be observed. By using the blends of biomass and coal, the decomposition of biomass is more dominant in the second stage than the decomposition of coal and the third stage is decomposition of coal with residual biomass. The major gaseous pollutants released from the thermal processes CO, CO2, CH4, NO, and SO2 were studied previously by TG-DTA. The thermal behavior of the material during thermal analysis techniques depend on heating rates (5, 10, 20, 30, 40, 50, and 100°C/min), reacting medium or environment (inert and oxidative by using N2, argon, O2, and CO2), mass and size of the sample used, and temperature ranges to be operated. These parameters can affect the product distribution and percentage of solid-liquid and gaseous fuels. Knowledge of these parameters can help to optimize the process. Table 6 gives a detailed description of a literature survey on the thermal behavior of various biomass and coal blends using different thermal analysis techniques. The commonly used blend ratios are 1 : 1, 2 : 3, 3 : 4, 4 : 3, and 3 : 2. Recently, Kandasamy Jayaraman et al. studied coal and biomass blends and they concluded that by increasing the ratio of biomass in the blends, the mass loss percentage increases, indicating the high reactivity of samples, and the activation energies were also increased by increasing biomass ratio in the blends [57]. Betancur et al. studied that coal and biomass blends increased combustion efficiency [124]. Blends showed lower ignition temperatures, and activation energies were decreased in the CO2 environment as compared to N2. Guangwei Wang et al. stated the synergistic effect of the combustion process of coal and biomass blends was prevalent as they increased the ignition performance by increasing the ratio of biomass [125]. Li et al. studied the copyrolysis of the coal and biomass blends and indicated the deviations in weight fractions [127].Table 6
A list of literature about the thermal coconversion of coal and lignocellulosic biomass using thermogravimetric analysis.
YearSampleExperimental facilityBlends coal : biomassThermal behaviorMediumInitial mass (mg)Heating rate (°C/min)Temperature range (°C)TvaTfb−DTGmaxcTDTGmaxd (°C)Ref.2017Coal and bagasseTGA-DTG80 : 20CombustionCO212525–9004603806045701.8%/°C0.8/°C300, 470[124]2017Coal and hazelnut shellTGA-DTG with MS25 : 7550 : 5075 : 25CombustionAir102025–95037636334960263363512%/min10%/min7%/min415416425[57]2016Coal and rice huskTG-DTA80 : 2060 : 4040 : 6020 : 80CombustionAir52.55102025–9005745455345247727707607492.4%/°C1.5%/°C1.0%/°C1.3%/°C738737722598[125]2015Bituminous coal and rice strawTG-DTG80 : 2060 : 4040 : 6020 : 80PyrolysisNitrogen—101520253025–900220–240346–7400.08–0.5%/°C330–350[127]2015Coal and sugarcane bagasseTG-DTG80 : 2060 : 4040 : 6020 : 80PyrolysisNitrogen251025–11001609000.16%/°C0.31%/°C0.49%/°C0.63%/°C308, 353, 440[134]2014Bituminous coal and bagasseTG-DTG75 : 25PyrolysisNitrogen1010204025–950318, 208, 271346, 293, 4615.8%/min1.2%/min346, 293, 349[60]2014Coal and bagasseTG-DTA4 : 13 : 21 : 12 : 31 : 4GasificationCO220525–13002952942962902914163903843763740.99%/°C1.77%/°C2.11%/°C2.50%/°C3.28%/°C346345344344343[135]2013Coal and sugarcane bagasseTG-DTG90 : 1080 : 2070 : 3060 : 4050 : 50PyrolysisNitrogen5–252025–900210–390390–4509–10.8%/min210, 365[136]2013Lignite and rice huskTG-DTA0.20.40.60.8PyrolysisNitrogen51025–800200400—330, 490[137]2013Bituminous coal and sugarcane bagasseTG-DTA75 : 25CombustionAir72.551020253025–7502006000.05%/min330[138]a = Tv; b = Tf; c = −DTGmax; d = TDTGmax.


## 4.2. Thermogravimetric Analysis of Sewage Sludge/Biomass Blends

Cothermal processes such as copyrolysis and cocombustion of sewage sludge with different types of lignocellulosic biomass can be applied for converting sewage sludge into useful energy and construction materials [139]. The other advantage of copyrolysis and cocombustion can help in reducing hazardous emissions to the atmosphere. Sludge has a low HHV, so burning of sewage sludge alone is neither cost-effective nor environmentally friendly. The blending of sewage sludge with lignocellulosic biomass material can make burning easier. The physical and chemical properties of the different materials used can affect the characteristics of the thermal process and residue obtained [140]. TGA is effective in studying the thermal behavior and characteristics of combustion of sewage sludge, biomass, coal, and other materials [141, 142]. It is an important technique to measure the percentage of mass loss of a sample with respect to temperature and time and to examine the thermal decomposition behavior during copyrolysis and cocombustion. It is also helpful in studying the kinetics of degradation of organic material during copyrolysis and cocombustion processes. Thermal degradation is a key element in designing sustainable copyrolysis and cocombustion processes. The thermal degradation of lignocellulosic biomass and sewage sludge is a very complicated process because of a variety of reactions. Conversion of different solid biomass and sewage sludge blends to gaseous and liquid products is difficult and complicated, so TG-DTA can be helpful by interpreting the kinetics to better understand the cocombustion and copyrolysis processes. The advantage of TGA is that it can easily assess the fuel value and the temperature at which combustion, pyrolysis, and gasification start and end. It can provide information about the highest reactivity temperature, the total amount of ash remaining, and complete burning time, and these techniques are important to study the thermal behavior of the pyrolysis process. The other advantage of TG-DTA is that it can determine the purity of mineral, organic, and inorganic compounds [75]. Ergudenler et al. describe that the weight of the sample can be varied from range 1–150 mg; usually, the weight of sample greater than 10 mg is preferred with a sensitivity of 0.01 mg. But if the excellent results are required, weight must be 1-2 mg [143].Table7 describes the detailed description of the literature about the TG-DTA analysis of a different type of sample to study the pyrolysis and copyrolysis behavior under certain conditions. Mian Hu et al. stated that by blending sewage sludge with biomass (pine sawdust), the devolatilization properties of sewage sludge increased whereas the initial decomposition temperatures increased by increasing biomass ratio [144]. Jiang et al. stated that by increasing the ratio of biomass with sewage sludge, the reactivity of blends increases [145]. Yang et al. studied the synergistic effect of copyrolysis of sewage sludge and wheat straw. The synergistic effect resulted in speeding up the pyrolysis process, the increase in the volatiles, and reduction in char yield. The synergistic effect was maximum at a biomass proportion of 60% [146].Table 7
A list of literature about the thermal coconversion of sewage sludge and lignocellulosic biomass using thermogravimetric analysis.
YearSampleExperimental facilityBlending SS : BiomassThermal behaviorMediumInitial Mass mgTemp range (°C)Heating rate (°C/min)TvaTfb−DTGmaxc (%/min)TDTGmaxc (°C)Ref.2017Rice husk and sewage sludgeTG-DTG70 : 3050 : 5030 : 70CombustionAir1025–100025272.1269.1264.8532.5559.6547.59.7510.9010.05333.8295.1338.5[77]2016Sewage sludge and rice strawTG-DTA25 : 7550 : 2.5075 : 25CombustionAir525–80020263258269765745714912.530299.2299.3293.1[78]2016Sewage sludge and biomassTG-DTA80 : 2060 : 4040 : 6020 : 80PyrolysisNitrogen—30–1000201791801811827277196036023433443443446.548.5410.5912.68[79]2015Sludge + lingo- cellulosic biomassTG-DTA50 : 50PyrolysisNitrogen1025–90015200575–3702015Sewage sludge and rice strawTG-DTA50 : 50PyrolysisNitrogen—150–50020200500163302015Sewage sludge and sawdustTG-DTA25 : 7550 : 5075 : 25PyrolysisNitrogen1025–100010315900–6502013Sewage sludge and rice huskTG-DTG10 : 9020 : 8030 : 7050 : 5070 : 30PyrolysisNitrogen1025–900202005006.05310a = Tv; b = Tf; c = −DTGmax; d = TDTGmax.


## 4.3. Thermogravimetric Analysis of Coal/Sewage Sludge Blends

TGA is a useful tool to examine the copyrolysis and cocombustion behavior of sewage sludge, coal, and their mixture. Different atmospheric conditions (inert condition for copyrolysis and oxidizing condition for cocombustion) can be used.Table8 describes the detailed description of thermal coconversion of coal and sewage sludge obtained from different sources through thermogravimetric analysis to examine the copyrolysis or cocombustion characteristics. Previous studies on the TGA of thermal coconversion of coal and dewatered sewage sludge blends show that the addition of 10% of sewage sludge in the coal-sludge blend has hardly brought any change in heat release and weight loss during thermal coconversion processes [147, 148]. Barbosa et al. worked on the sewage sludge and coal blend impregnated with molasses to study the cocombustion characteristics and found that fuel quality obtained from this type of blend was improved [149]. But the char characteristics remained the same as that of bituminous coal. Zhuo et al. experimented on 80% coal and 20% sludge blends to study the cocombustion behavior under N2/O2 and CO2/O2 atmosphere and find out that blend gives distinctive combustion peaks as compared to combustion of sludge [150]. Jin et al. studied the influence of the blend ratio of 60% coal and 40% dewatered sewage sludge on flammability index, combustion characteristic index, and release of harmful emission and heavy metals [151]. This effect is ignorable if the dewatered sewage sludge ratio is kept at less than 20%. Coimbra et al. studied the copyrolysis and cocombustion behavior of bituminous coal and pulp mill sludge blend of ratio 90 : 10 and concluded that cocombustion behavior of blend is similar to that of conversion behavior of coal alone, but the copyrolysis of blends occurs at lower devolatilization temperature than that of pyrolysis of coal [52]. Zhang et al. also studied the combustion characteristics of blends of different ratios of sewage sludge and coal [53]. Xia and Li concluded from their result that the TG and DTG profiles of sewage sludge should be the same as the profile of coal but different from coal under different blending ratios [152].Table 8
A list of literature pertaining to the thermal coconversion of coal and sludge using thermogravimetric analysis.
YearSampleExperimental facilityBlends coal : sludgeThermal behaviorMediumInitial mass (mg)Temperature range (°C)Heating rate (C/min)TvaTfbDTGmaxc (%/min)TDTGmaxc (°C)Reference2017Coal and sewage sludgeTGA-DTG50 : 50CocombustionAir1525–800202006000.80450[82]2017Coal and textile dying sludgeTGA-DSC80 : 20CocombustionAir10.520–100020536.6682.711.4605.7[83]2016Coal and sewage sludgeTGA-DTG40 : 20CocombustionAir1020–1000254288001.5550[90]2016Bituminous coal and sludgeTG-DTG90 : 10CopyrolysisN22525–1200547512000.0114605[91]2016Bituminous coal and sludgeTG-DTG90 : 10CocombustionO22525–1200550511050.1128900[91]2015Coal and sewage sludgeTG-DTG1 : 1, 2 : 1, 3 : 1CocombustionAir530–9002020065010450[92]2014Coal and sewage sludgeTG-DTG10 : 90, 20 : 80, 30 : 70, 50 : 50CopyrolysisN21025–1200302008500.16420[93]2013Coal and sewage sludgeTG-DTG90 : 10CocombustionAir1525–100010, 40, 1002008000.03450a = Tv; b = Tf; c = −DTGmax; d = TDTGmax.


## 5. Future Perspectives

This review provides a detailed description on the thermal coconversion of different biomass, sewage sludge, and coal blends through TGA to obtain optimum energy recovery entrained from a different type of sewage sludge, biomass, and coal; however, there are still many challenges to solve the problem related to the copyrolysis and cocombustion of blends. To overcome these challenges, some steps should be taken to improve the process in order to obtain maximum conversion. The production of biofuels through thermal coconversion processes is not fully established on a commercial scale, so work should be done to make it better energy recovery option commercially. The different kinetic models should be developed to find out the optimum operating condition to design the copyrolysis or cocombustion process to obtain the highest yield with lower investment. More research is required in the field of thermal coconversion of coal, biomass, and sewage sludge blends in which focus should be on scaling up and cost reduction. A computational model should be developed to optimize the physical, chemical, and reaction parameters that will help to design the process.


## 6. Conclusions

This review investigates the thermal coconversion of biomass/sewage sludge, coal/sewage sludge, and coal/biomass by using thermogravimetric analysis (TGA). Different elemental, chemical composition, and experimental conditions like the type of sample, type of reactors, different temperature ranges, heating rates, and residence time were reviewed to observe synergetic effects during copyrolysis of sewage sludge, lignocellulosic biomass, and coal blends. Many researchers have acknowledged that the copyrolysis process can expressively improve the yield and eminence of pyrolysis oil without helping aid such as catalysts, solvents, and pressure.This technique can be considered as a simple, cheap, and effective to obtain the optimum yield. This study will provide a better understanding to reduce the failure points in obtaining and applying the copyrolysis process to obtain the maximum yield of the product. A detailed review of TGA of copyrolysis of different substances like sewage sludge, lignocellulosic biomass, and coal blends, therefore, can help plan and develop efficient industrial copyrolysis process. Based on the critical analysis, the following recommendations are suggested for future perspective:(i)
Low energy intensive operation with high-quality products techniques should be explored(ii)
Feedstock advance pretreatment processes could be adopted to enhance the devolatilization(iii)
Synergistic effect of biomass types with other residues and their interactions should be comprehensively investigated(iv)
Strict dewatering and drying steps are required before thermal coconversion processes proceeding for higher energy consumption(v)
Researcher should investigate the economic and environmental concern related to thermal coconversion processes to reduce greenhouse gases



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*Source: 5024369-2020-08-04.xml*