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Article

Potential of Briquetting as a Waste-Management Option for Handling Market-Generated Vegetable Waste in Port Harcourt, Nigeria

by
Olugbemiro M. Akande
1,* and
Abel O. Olorunnisola
2
1
Pan African University Life and Earth Sciences Institute (including Health and Agriculture), University of Ibadan, Ibadan 200284, Nigeria
2
Department of Wood Products Engineering, University of Ibadan, Ibadan 200284, Nigeria
*
Author to whom correspondence should be addressed.
Recycling 2018, 3(2), 11; https://doi.org/10.3390/recycling3020011
Submission received: 8 March 2018 / Revised: 22 March 2018 / Accepted: 27 March 2018 / Published: 28 March 2018
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Abstract

:
The conversion of biomass to high-density briquettes is a potential solution to solid waste problems as well as to a high dependence on fuel wood in developing countries. In this study, the potential of converting vegetable waste to briquettes using waste paper as a binder was investigated. A sample size of 30 respondents was interviewed using a self-administered questionnaire at the D-line fruit and vegetable market in Port Harcourt, Nigeria. Carrot and cabbage leaves were selected for briquetting based on their availability and heating value. This waste was sun-dried, pulverized, torrefied and fermented. Briquettes were produced with a manual briquette press after the processed vegetable waste was mixed with waste paper in four paper:waste ratios, i.e., 10:90, 15:85, 20:80 and 25:75. The moisture content, densities and cooking efficiency of the briquettes were determined using the oven-drying method, the water-displacement method, and the water-boiling test, respectively. There was no observed trend in moisture content values of the briquettes, which varied significantly between 3.0% and 8.5%. There was no significant variation in the densities, which ranged from 0.79 g/cm3 to 0.96 g/cm3 for all the briquette types. A degree of compaction above 300% was achieved for all the briquette types. Water-boiling test results revealed that 10:90 paper:sun-dried cabbage briquettes had the highest ignitability of 0.32 min. Torrefied carrot briquettes with 25% paper had the least boiling time and the highest burning rates of 9.21 min and 4.89 g/min, respectively. It was concluded that cabbage and carrot waste can best be converted into good-quality briquettes after torrefaction.

1. Introduction

The management of municipal solid waste poses various challenges to many countries of the world at varying intensities. The primary difference between waste materials generated in developing nations and those generated in industrialized countries is the higher organic content characteristic of the former. This further aggravates the already existing challenge due to the bulky nature of organic waste and the unpleasant accompaniments of putrefaction [1]. Nevertheless, embedded in this challenge is an opportunity which represents the direction in which the world is heading in the “energy cycle”. In recent decades, there has been a strong worldwide interest in the development of technologies that exploit renewable energy sources (green energy), both for its environmental and economic benefits [2]. According to Jekayinfa and Scholz [3] a country like Nigeria has abundant supplies of biomass resources, particularly in the form of agro-forestry residues and municipal solid waste which have the potential for energy generation.
Furthermore, deforestation partly resulting from the overarching dependence on forests for fuel wood and the burning of fossil fuels are two major contributors to anthropogenic climate change [4]. Adegbulugbe [5] predicted that by 2030 the demand for fuel wood is expected to have increased to about 213.4 × 103 metric tonnes, while the supply would have decreased to about 28.4 × 103 metric tonnes. This imbalance in fuel wood demand/supply has been reported in the National Energy Policy of Nigeria. On the national scale, increasing fuel wood consumption contributes to deforestation, with consequent desertification and soil erosion [6]. The decreasing availability of fuel wood engendered by large-scale deforestation, coupled with increasing prices of kerosene and cooking gas in Nigeria, emphasizes the need for alternative sources of energy which should be renewable and accessible to the poor [7]. Therefore, relying on biomass for the production of briquettes is a potential solution to solid waste problems in developing countries as well as the high dependence on fuel wood.
The conversion of biomass to energy can be achieved through various technologies such as direct/stove, biomass briquette and boiler combustion; thermochemical conversion (which includes gasification, pyrolysis and liquefaction); and biochemical conversion (anaerobic fermentation biogas, bioethanol and biodiesel) [8,9,10,11,12]. The major limitations of direct combustion are the low heating efficiency and difficulty in handling, storage and transportation resulting from the low bulk density and high moisture content of the biomass materials [9,13]. One solution to these problems is to increase the density of the biomass by conversion to briquettes [14]. Despite outstanding advantages (such as higher conversion rate and easy industrialization) of the more recent biomass energy technologies, there are certain limitations to their utilization. For example, biomass gasification requires a gasifier and the reaction process is very complex [9]. According to Veringa [10], interest in the liquefaction process is reduced by the high cost of pressure reactors. Although biomass briquetting tends to have relatively high operating costs [9], the combustion efficiency is greatly improved through torrefaction. Furthermore, sun-drying the raw materials and the briquettes after production prevent additional energy expenditure. Also, briquetting requires less expertise compared to more recent conversion techniques.
A number of studies point to the fact that feed stocks of municipal solid waste (MSW) origin have potential for briquetting. Omari et al. [15] characterized and evaluated MSW in Arusha, Tanzania and determined the amount of energy that could be recovered from the waste. Raju et al. [16] produced and tested briquettes from almond leaves, sawdust and cocoa-peat based on their availability and ability to bond together when compressed. Srivastava et al. [17] converted vegetable market waste to briquettes without pre-treatment and without using any external binders. Torrefaction combined with briquetting yields a highly energy-dense fuel carrier of 20–25 GJ/tonne [18] and this has been confirmed by Felfi et al. [19] in their study of wood briquette torrefaction. The aim of this study was to examine the current waste-management strategies for fruits and vegetables at D-line market in Port Harcourt, Nigeria and suitable pre-treatment methods for briquetting selected wastes that were more abundant and had relatively high energy contents.

2. Materials and Methods

2.1. Study Area

The study area was the D-line fruit and vegetable market in Port Harcourt, Rivers State, Nigeria. Port Harcourt is the capital and largest city of Rivers State, Nigeria. It lies on latitude 40°49′ N and longitude 70°21′ E. The population of Port Harcourt urban area is said to have increased to an estimated 1,865,000 inhabitants in 2016, from 1,382,592 as of 2006 [20]. Annual municipal solid waste generation for Port Harcourt was estimated to be 265,129 MT and 352,853 MT for the years 1990 and 2000, respectively [21], while per capita generation ranges between 1.11 and 1.25 kg/cap/day [22,23,24]. About 69% of the waste generated in Port Harcourt is organic in composition [24] as shown in Figure 1.

2.2. Data-Collection Methods

Primary data was obtained from 30 randomly selected respondents through a self-administered questionnaire to determine the types of fruit and vegetable waste found in the market and the strategies adopted in the management of fruit and vegetable waste at the market. Samples of vegetable waste were also collected for conversion to briquettes. Secondary data sources such as journal articles were consulted to determine the heating values of various biomass materials for briquetting.

2.3. Briquette Preparation

The waste for briquetting was selected using a Likert scale based on respondents’ perception of which wastes were highly available, moderately available, or poorly available at the market. This selection was based on: (i) the heating value of the materials as tabulated in literature—for example, residues with relatively high energy content were selected; and (ii) the level of availability of the waste—for example, the residues that met the aforementioned condition and were readily available were given preference.
The waste materials selected were cabbage and carrot leaves. The vegetable waste was collected and sun-dried for 10 days. The dried biomass was manually pulverized. A portion of the vegetable waste was used as is, another portion was torrefied by roasting in a container on a kerosene stove for about 2 h, while the third portion was left to ferment for 5 days. Each of the portions was mixed with waste paper which had been turned to pulp to serve as a binder in the following paper:waste ratios: 10:90, 15:85, 20:80, and 25:75. The paper and vegetable waste materials were thoroughly mixed and then hand fed into the manual briquetting press and compacted at an average pressure of 3.5 MPa using a hydraulic jack equipped with a pressure gauge. The briquettes were allowed to dry for about 2 weeks.

2.4. Moisture Content Determination

The moisture content of the vegetable waste was determined by measuring their fresh weight and dry weight. The percentage difference between these two weights gave an estimate of the moisture content of the waste materials. The moisture content (dry basis) of the briquettes was determined using the oven-dry method as carried out by Onukak et al. [25] using three samples of briquettes from each treatment.

2.5. Density Determination

The bulk density of the vegetable waste was determined by weighing the materials in an open top rectangular carton box of 2338.125 cm3 volume. True densities of the biomass and briquettes (dry basis) were determined using the mass and volume relationship [26]. The degree of compaction of the briquetted materials was calculated as percent increase in true density over bulk density of ground residues, as in Srivastava et al. [17].

2.6. Water-Boiling Test

This test was carried out to compare the cooking efficiency of the various briquette types. It involved boiling an equal volume (100 cm3) of water with a fixed mass (100 g) of the various briquette types as reported by Onuegbu et al. [27], using a typical local charcoal stove. During this test, the smoke evolution level was observed and other properties including ignition time, boiling time and burning rate of the briquettes were measured, as reported by Onukak et al. [25] and Onuegbu et al. [27].

2.7. Statistical Analysis

The statistical analysis was performed using the Statistical Package for Social Sciences (IBM SPSS Statistics 20) after a coding questionnaire. Simple descriptive statistics such as mean, standard deviation and graphs were obtained. Moisture content and density data were subjected to one-way analysis of variance (ANOVA) in the same software. Homogeneity of variance assumption was tested using Levene’s test. The Games-Howell testwas used when the homogeneity of variance assumption was violated.

3. Results

3.1. Respondents’ Demographics

Out of the 30 respondents interviewed, 43% (13) were males while 57% (17) were females (Table 1). On the basis of age group, 38% of the male respondents were between 21 and 30 years old, while 29% of the female respondents were 31 and 40 years (Table 1).

3.2. Fruit and Vegetable Waste Availability and Management Methods

As shown in Figure 2, cabbage waste ranked the highest with a count of 49, followed by lettuce waste (40), green bean waste (34) and carrot (26). The least available waste materials were those of maize, pear and banana (1). The interviewswith respondents revealed that a lot of vegetable waste was generated at the market and this was poorly managed beyond the point of storage. The process of solid waste management at the market typically included storage, collection, and final disposal. The sellers swept and gathered their refuse into nylons or sacks and took them to the section of the market designated for temporary storage of the waste in heaps. This usually continued, sometimes for weeks due to delayed collection, leading to decay of the waste, producing an offensive odour around that section of the market.
Crop, rabbit and snail farmers were involved in the collection of the vegetable wastes. While the crop farmers converted the waste to compost, the rabbit and snail farmers used them as animal feedin some cases.Rather than collecting these materials from the waste themselves, the farmers paid the sellers at the market to store waste separately. However, these respondents reported that the farmers were only able to utilize a very small proportion of the waste, as a huge pile of waste was still left to decay at the storage point.
The relatively large leftover matter (not quantified in this study) was handled by waste collectors for disposal; 46.7% of the respondents stated that collection was done twice a week (Wednesdays and Saturdays), but the remaining 53.3% stated that this was not the case as the waste is allowed to rot and constitutesan environmental nuisance. It was also observed during field visits that while collection was done one Wednesday, there was no collection on the next Wednesday, indicating some level of inconsistency. After the waste was collected, it was disposed of at dumpsites whose locations were unknown to the respondents.

3.3. Energy Needs, Sources and Estimated Cost

Information on the domestic and business energy needs of the respondents was also obtained (Figure 3a). All (100%) respondents indicated that they required energy for cooking, 93.3% of respondents needed energy for lighting, while 86.6% needed energy for heating.
As shown in Figure 3b, a majority (87%) of the respondents made use of kerosene while about half (47%) were making use of liquefied petroleum gas (LPG). On the other hand, charcoal, firewood and electricity ranked the least (10% each). About 67% of the respondents utilized only one source of energy (kerosene or LPG) while about 23% used a combination of kerosene and LPG. As shown in Table 2, 36.7% of respondents spent between ₦1000 and ₦4999on energy for cooking. Also, 36.7% of the respondents spent between ₦5000 and ₦9999. In other words, more than 70% of the respondents spent less than ₦10,000 on energy for cooking in a month.

3.4. Selection of Waste Materials for Briquetting

None of the respondents at the market had heard of briquetting. Based on availability and heating value, cabbage and carrot leaf waste materials were selected for briquette production. In addition, waste paper was selected for use as a binder due to its availability and relatively high heating value. Table 3 provides a summary of the summed ranks of the most abundant wastes from the survey, with their energy content (in Kilojoules per 100 g) and ash content (in g per 100 g).

3.5. Effects of Pre-Treatment on Briquetting

The briquettes produced with torrefied waste materials were more compact and definite in shape than those formed from sun-dried residues. The carrot leaves could not be adequately briquetted until after fermentation for a period of 5 days. After fermentation they became more compact than the briquettes made from the sun-dried cabbage leaves which were not fermented. Ease of briquetting was observed to reduce with increase in the proportion of paper used as binder for all the feed stock types (torrefied, sun-dried and sun-dried fermented). Cracks were observed on the walls of briquettes with 25% paper as they attained dryness (Figure 4).

3.6. Moisture Content and Densities of Briquettes

The moisture content of the dry loose vegetable waste materials were 48.5% and 84.9% for carrot leaves and cabbages, respectively. The moisture content of the briquettes ranged from 3.03% to 8.47%, as shown in Table 4. There was a significant difference among the percentage moisture content of the 16 briquette types, F (15, 32) = 4.34 (F values at degrees of freedom between and within groups), p < 0.001 (p significant at values less than 0.5). There was no discernable pattern in percentage moisture content variation either due to torrefaction or increasing the ratio of paper in the mixture.
The bulk density of the loose carrot leaves (0.228 g/cm3) was slightly higher than that of the cabbage leaves (0.224 g/cm3). The densities of briquettes ranged from 0.79 g/cm3 to 0.96 g/cm3. There was no significant difference among the densities of the 16 briquette types, F (15, 64) = 1.14, p = 0.338. There was also no observable trend in variation of densities with an increase in the amount of paper used as binder for both cabbage and carrot briquettes. Degree of densification ranged from 343% to 436% for all briquette types, the highest being 15:85 paper:sun-dried cabbage briquettes and the lowest being 15:85 paper:sun-dried carrot briquettes.

3.7. Water-Boiling Test

As the briquettes burned, it was observed that while those made from sun-dried residues emitted much smoke, those made from torrefied residues emitted very little smoke. As shown in Table 5, the ignition time ranged from 0.32 min to 4.12 min. An increase in ignitability with increase in paper concentration was observed in the cabbage briquettes (Figure 5a,b). The reverse was the case for the carrot briquettes (Figure 6a,b). Boiling time ranged from 9.21 min to 32.32 min, while the burning rate was between 1.75 g/min and 4.89 g/min. The burning rates for all briquette types increased with the increase in percentage of paper used as binder (Figure 5 and Figure 6).

4. Discussion

The current management of solid waste at D-line fruit and vegetable market, Port Harcourt, Nigeria, conformed to the manner described by Binafeigha and Enwin [31] for Port Harcourt Metropolis. According to the authors, there were no measures in place to ensure the orderly execution of the basic principles of waste management. The waste-management strategies employed at the market included storage, collection and outright disposal at dumpsites.
Cabbage leaves were the most abundant vegetable waste material at the market. The relatively high abundance of this material could be attributed to the large microbial population on the outer leaves of the vegetable leading to spoilage [32]. This part of the vegetable is usually shredded, often in order to make the cabbage look attractive to buyers, as is also described by Ngu and Ledin [33]. Carrot leaves were also observed to be relatively abundant. Apart from the high abundance of cabbage and carrot leaves, their higher heating values of 126 kJ/100 g and 322 kJ/100 g respectively [28] also influenced their being chosen as feedstock for the briquetting process. The ash content of the selected residues (0.81% and 1.2% for cabbage and carrot leaves, respectively) was also within the value of less than 4% recommended by Grover and Mishra [34].
The enhanced compactness and shape of the briquettes formed from torrefied materials compared to those formed from sun-dried and fermented materials was in line with the findings of Koppejan et al. [35]. Torrefaction helps to develop a uniform feedstock which improves binding during pelletization [13] and degrades lignin, which plays an important role in the internal binding of pellets [35]. Sun-dried carrot briquettes became more compact after fermentation. This may be attributed to the low levels of lignin (1.78 g/100 g) and ash (1.2 g/100 g) contained in the carrot leaves [30,36]. The reduced compactness of the briquettes with increased proportion of paper could be due to the relatively larger particle sizes of the paper, which engendered greater pore spaces [37]. Water from these pores was removed and created voids along the structure of the briquettes, which led to cracks [26].
The moisture content of the cabbage and carrot leaves (84.9% and 48.5%) was lower than the 90.3% and 86.5% respectively reported by Islam et al. [30]. The moisture content of the briquettes ranged from 3.03% to 8.47%. This range is slightly lower than the ranges of 5.4–13.3%, wet basis, reported by Olorunnisola [7] for waste paper and coconut admixture. The lower moisture levels of the briquettes are an advantage in the sense that energy will not be utilized to exhume much moisture during combustion. Also, a damp fuel will lead to the excessive emission of fumes and a risk of explosion [25]. The lower moisture content of the torrefied briquettes compared to the sun-dried ones could be explained by the removal of free and chemically bonded moisture resident in the residues with increasing temperature [38]. The lower moisture content of the sun-dried carrot briquettes (3.53–6.13%) compared to the sun-dried cabbage briquettes (4.61–8.47%) agrees with the finding of Onukak et al. [25] and may be a result of the levels of moisture in the waste materials. Carrot residues had lower moisture (48.5%) than cabbage residues (84.9%).
Briquettes produced with the torrefied carrot waste were denser (0.86 g/cm3–0.90 g/cm3) than those of sun-dried carrot waste (0.79 g/cm3–0.90 g/cm3) with few exceptions. This could be attributed to an increase in lignin concentration caused by the pre-heating treatment, thereby improving the binding ability of the biomass and, consequently, enhancing the density [38,39]. Several researchers have found that density values are greatly influenced by a material’s moisture content, particle size, the process pressure, and temperature [40,41]. A closer look at the densities of the 20:80 and 25:75 ratios of all the briquette types indicates that the briquettes made from sun-dried carrot have greater densities than those made from sun-dried cabbage, and this could be linked to the higher moisture content and particle sizes of the cabbage residues [13]. The briquettes produced in the study were denser (0.79 g/cm3–0.96 g/cm3) than those reported by Omoniyi and Igbo [42] within the range of 491.46 kg/m3–623.18 kg/m3 for rice-husk briquettes using different binders. The degree of compaction achieved for all the briquette types ranged between 343–436%. These values were found to be higher than the 231%, 203%, 202% and 219% reported by Srivastava et al. [17] for cauliflower + cabbage leaves, coriander stalk + leaves, field beans and green bean pods, respectively. The high percentage increase in density from the original bulk density was because the particle sizes of the cabbage and carrot residues were reduced to the point of achieving higher compaction [14].
The relatively lower emissions observed for the briquettes made from torrefied residues could be attributed to the removal of most of the smoke-producing compounds by the pre-heat treatment [13]. The briquettes made from sun-dried cabbage residues had the shortest ignition time of all the briquette types because of their larger particle sizes [25]. The larger particle sizes offered more pronounced pore spaces for the easy percolation of oxygen and the outflow of combustion products during combustion [25,37]. The increase in the time taken to ignite this particular briquette type (Figure 5a) with an increase in the percentage of paper could be due to the increase in the concentration of biomass in those briquette types [16]. Conversely, the time taken to ignite briquettes made from sun-dried and torrefied carrot decreased with the increase in the percentage of paper used as binder (Figure 6a,b). This could be attributed to the reduced compaction, hence more porosity with the increase in percentage of waste paper. This porosity could have led to an inflow of oxygen and an outflow of combustion products [43].
For both the sun-dried and torrefied carrot and cabbage briquettes, boiling time was observed to decrease with an increase in the percentage of the paper binder. Ucuncu and Vesilind [44] reported that the white office paper used in this study had a heating value of 6234 Btu/Ib (1450 kJ/100 g). This value is higher than those of carrot and cabbage leaves and could have resulted in the reduced boiling time observed with the increase in the percentage of paper from 10% to 25%. This is in conformity with the findings of Oyelaran et al. [43] on groundnut shell briquettes with a paper binder. Generally, all the briquettes made from torrefied residues boiled water faster than those made from sun-dried residues. This could be due to the increased calorific value which results from the torrefaction process [38,45]. Comparing the boiling time of carrot briquettes to that of cabbage briquettes revealed that the carrot briquettes boiled water faster than the cabbage briquettes with few exceptions. This could be attributed to the higher calorific value of carrot leaves (322 kJ/100 g) than cabbage (126 kJ/100 g) [28,43]. The higher boiling time recorded in 20:80 paper:sun-dried carrot briquettes, 25:75 paper:sun-dried carrot briquettes and 10:90 paper:torrefied carrot briquettes than their cabbage counterparts may be due to their lower burning rates of 3.24 g/min, 3.40 g/min, and 1.75 g/min, respectively [27,43].

5. Conclusions

This study revealed that solid waste management at the D-line market, Port Harcourt, is poor in terms of storage, inconsistent collection and disposal in dumpsites in tandem with the practices across Port Harcourt itself. It also found that the carrot and cabbage waste from the D-line fruit/vegetable market can be readily converted to good quality biomass briquettes with low proportions of waste paper as a binding agent. While the cabbage leaves could be briquetted right after sun-drying for a period of 10 days, the carrot leaves needed to be fermented for relevant compaction to be achieved. Both carrot and cabbage leaves could be subjected to torrefaction in order to increase the heating values, reduce their moisture content and drive off smoke-producing compounds as well as other volatile matter, resulting in higher-quality and better-burning briquettes. The briquettes that were produced had low moisture content within an acceptable range of 3.03–8.47%. The briquettes had high densities within the range of 0.79 g/cm3–0.96 g/cm3 as compared to 491.46 kg/m3–623.18 kg/m3 for rice-husk briquettes. Also, the briquettes produced had relatively high ignitability (0.32–4.12 min), fair cooking efficiency judging from the duration each took to boil water (9.21–32.32 min), and burning ratesthat can suit various purposes (1.75–4.86 min).

Acknowledgments

This paper was extracted from the Master’s thesis submitted to the Pan-African University Life and Earth Sciences Institute, University of Ibadan, Nigeria. The research was funded by the African Union Commission. The authors express their sincere gratitude to the Department of Wood Products Engineering, University of Ibadan, for providing the materials and facility for the research, and Enoch Bessah and Davison Kafuli, who edited the manuscript.

Author Contributions

Author O.M.A. carried out the survey, experiments, data analysis and prepared the initial and final drafts of the manuscript. Author A.O.O. conceived the study, supervised the experiments and edited the research report as well as the manuscript drafts. Both authors contributed immensely to the reported study and approved of its publication.

Conflicts of Interest

The authors declare no conflict of interest.

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Figure 1. Waste heap at the D-line fruit and vegetable market, Port Harcourt, Nigeria.
Figure 1. Waste heap at the D-line fruit and vegetable market, Port Harcourt, Nigeria.
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Figure 2. Availability of waste at D-line market.
Figure 2. Availability of waste at D-line market.
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Figure 3. Distribution of energy (a) needs and (b) sources.
Figure 3. Distribution of energy (a) needs and (b) sources.
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Figure 4. Samples of briquettes produced.
Figure 4. Samples of briquettes produced.
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Figure 5. Thermal characteristics of (a) sun-dried and (b) torrefied cabbage briquettes.
Figure 5. Thermal characteristics of (a) sun-dried and (b) torrefied cabbage briquettes.
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Figure 6. Thermal characteristics of (a) sun-dried and (b) torrefied carrot briquettes.
Figure 6. Thermal characteristics of (a) sun-dried and (b) torrefied carrot briquettes.
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Table
Table 1. Interview respondents’ age-gender cross tabulation.
Table 1. Interview respondents’ age-gender cross tabulation.
Age GroupMale %Female %
20 and below15.4%23.6%
21–3038.4%17.6%
31–4023.1%29.4%
41–5015.4%29.4%
Over 507.7%0%
Total100%100%
Table
Table 2. Monthly expenditure on energy.
Table 2. Monthly expenditure on energy.
Cost (₦)FrequencyPercentCumulative Percent
1000–49991136.736.7
5000–99991136.773.3
10,000–14,999310.083.3
15,000–19,999413.396.7
Missing value13.3100.0
Total30100.0
Note: Missing value means the respondent did not supply this information.
Table
Table 3. Selection criteria for residues.
Table 3. Selection criteria for residues.
ResidueAvailability (Summed Rank)Energy Content (kJ/100 g)Ash Content (g/100 g)Observed Availability
Cabbage491260.81Abundant
Lettuce40911.11Scarce
Green beans341021.05Scarce
Carrot leaves263221.2Abundant
Energy and ash content are adapted from Longvah et al. [28], Gopalan et al. [29] and Islam et al. [30].
Table
Table 4. Moisture content and densities of the briquettes.
Table 4. Moisture content and densities of the briquettes.
Briquette CodeBriquette TypeMC (%)Density (g/cm3)Degree of Compaction (%)
BO1010:90 paper: sun-dried cabbage 8.37 ± 1.910.86 ± 0.13391
BO1515:85 paper: sun-dried cabbage8.47 ± 0.400.96 ± 0.16436
BO2020:80 paper: sun-dried cabbage4.61 ± 1.420.85 ± 0.04386
BO2525:75 paper: sun-dried cabbage4.71 ± 1.670.83 ± 0.06377
TBO1010:90 paper: torrefied cabbage3.03 ± 1.400.84 ± 0.04382
TBO1515:85 paper: torrefied cabbage3.25 ± 0.880.79 ± 0.06359
TBO2020:80 paper: torrefied cabbage3.14 ± 0.510.81 ± 0.06368
TBO2525:75 paper: torrefied cabbage3.74 ± 1.360.89 ± 0.09405
DC1010:90 paper: sun-dried carrot6.13 ± 0.210.79 ± 0.13343
DC1515:85 paper: sun-dried carrot5.47 ± 0.360.90 ± 0.13391
DC2020:80 paper: sun-dried carrot7.92 ± 4.730.87 ± 0.13378
DC2525:75 paper: sun-dried carrot3.53 ± 0.070.87 ± 0.06378
TDC1010:90 paper: torrefied carrot3.16 ± 0.060.87 ± 0.06378
TDC1515:85 paper: torrefied carrot4.11 ± 0.100.90 ± 0.07391
TDC2020:80 paper: torrefied carrot5.47 ± 2.160.89 ± 0.09387
TDC2525:75 paper: torrefied carrot3.20 ± 0.060.86 ± 0.13391
Table
Table 5. Results of water-boiling test of briquettes.
Table 5. Results of water-boiling test of briquettes.
Briquette CodeBriquette TypeMass of Briquette Consumed (g)Ignition Time (min)Water Boiling Time (min)Burning Rate (g/min)
BO1010:90 paper: sun-dried cabbage610.3232.321.89
BO1515:85 paper: sun-dried cabbage660.4525.032.64
BO2020:80 paper: sun-dried cabbage651.0618.133.59
BO2525:75 paper: sun-dried cabbage681.4314.374.73
TBO1010:90 paper: torrefied cabbage361.1919.351.86
TBO1515:85 paper: torrefied cabbage411.4116.302.52
TBO2020:80 paper: torrefied cabbage392.5714.162.75
TBO2525:75 paper: torrefied cabbage601.5112.424.83
DC1010:90 paper: sundried carrot784.1226.522.94
DC1515:85 paper: sundried carrot653.0019.343.36
DC2020:80 paper: sundried carrot621.4019.113.24
DC2525:75 paper: sundried carrot731.3221.473.40
TDC1010:90 paper: torrefied carrot392.4422.251.75
TDC1515:85 paper: torrefied carrot431.3514.243.02
TDC2020:80 paper: torrefied carrot461.5212.133.79
TDC2525:75 paper: torrefied carrot451.479.214.89

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Akande, O.M.; Olorunnisola, A.O. Potential of Briquetting as a Waste-Management Option for Handling Market-Generated Vegetable Waste in Port Harcourt, Nigeria. Recycling 2018, 3, 11. https://doi.org/10.3390/recycling3020011

AMA Style

Akande OM, Olorunnisola AO. Potential of Briquetting as a Waste-Management Option for Handling Market-Generated Vegetable Waste in Port Harcourt, Nigeria. Recycling. 2018; 3(2):11. https://doi.org/10.3390/recycling3020011

Chicago/Turabian Style

Akande, Olugbemiro M., and Abel O. Olorunnisola. 2018. "Potential of Briquetting as a Waste-Management Option for Handling Market-Generated Vegetable Waste in Port Harcourt, Nigeria" Recycling 3, no. 2: 11. https://doi.org/10.3390/recycling3020011

APA Style

Akande, O. M., & Olorunnisola, A. O. (2018). Potential of Briquetting as a Waste-Management Option for Handling Market-Generated Vegetable Waste in Port Harcourt, Nigeria. Recycling, 3(2), 11. https://doi.org/10.3390/recycling3020011

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