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In environmental engineering, specific parameters are very important, one of which is water and its quality. A supply of clean water is essential for establishing and maintaining diverse human activities. Water resources are useful in the provision of valuable food through aquatic life as well as irrigation for agricultural production. However, liquid and solid wastes produced by human settlements and industrial activities pollute most of the water sources throughout the world (Dhote, Ingoleb, and Chavhana, 2012). It is therefore imperative that water quality should be assessed all over the world. Water quality is defined by several parameters which are physical, chemical, and biological. The deterioration of the quality of the surface water, groundwater systems is mainly controlled by the geological structure and the lithology of the watersheds/aquifers, the chemical reactions that take place within the watershed/aquifers as well as the type of land use and the anthropogenic activities (Melidis, Vaiopoulou, and Aivasidis, 2007). Furthermore, the quality of the water resources is vulnerable to a wide range of chemical components which includes organic materials, nutrients, salts, sediments, heavy metals, and other pollutants (Korfali and Jurdi 2011, Qadir 2010). Many of these wastes that emerge from industrialization and civilization enter into water bodies via discharge from domestic, industrial, and non-point sources (Welch and Naczk, 1992).
In the research by Amoatey and Bani (2011), a short history of wastewater treatment was presented. Wastewater treatment is reasonably a new practice, even though there has been a history of the construction of drainage long before the nineteenth century. Before this time, human faeces and urine usually regarded as “night soil” was put in buckets along the streets and workers come around to collect them into honey wagon tanks. The waste was taken to rural areas and disposed of on agricultural lands which served as fertilizers. At the advent of innovations in the nineteenth century, the flush toilet was invented, which caused an increase in the volume of waste generated for these agricultural lands. Cities like Rome due to their large population adopted the use of drainage and storm sewers to transport wastewater into water bodies against Edwin Chadwick’s 1842 recommendation that rain should go to the river while sewage goes to the soil. Irrespective of the massive supplies of fresh water and natural cleansing ability of surface water, in 1850, the population had so increased that there were several outbreaks of life-threatening diseases. These diseases were discovered to be caused by the pathogenic bacteria present in the polluted water. In 1842, the first modern sewerage system for conveying wastewater was built by an English engineer named Lindley in Hamburg, Germany. This invention has been improved over time and is still being adopted in today’s wastewater management practices. The treatment of wastewater was evident only the acceptable limit of the water bodies was surpassed and health challenges became unbearable. Gross pollution and ravaging health hazards were the results of discharging waste into water bodies, especially for downstream users. Between the late 1800s and early 1900s, many alternatives were explored until 1920, when more stable and adequate treatment processes used today were developed. Although its design was empirical, in the midcentury it became established and the centralized wastewater systems were incorporated.
Recently, advancements have been made to derive portable water from wastewater. Irrespective of the size of the collecting water body, it is required that wastewater is treated to a minimum level before discharging (Peavy, Rowe, and Tchobanoglous, 1985). Also, the more sustainable decentralized wastewater treatment (DEWATS) system is adopted over the centralized systems especially in developing countries where there is poor wastewater infrastructure (Adu-Ahyia and Anku, 2010). Filtration is one of the most important treatment processes used in water and wastewater treatment. In water treatment, it is used to purify the surface water for potable use whereas, in wastewater treatment, the main purpose of filtration is to produce effluent of high quality so that it can be reused for various purposes. Any type of filter with attached biomass on the filter media can be defined as a biofilter (Metcalf and Eddy, 2003). It can be the trickling filter in the wastewater treatment plant, or horizontal rock filter in a polluted stream, or granular activated carbon (GAC) or sand filter in the wastewater treatment plant. Biofilters have been successfully used for air, water, and wastewater treatment. It was first introduced in England in 1893 as a trickling filter in wastewater treatment (Metcalf and Eddy, 1991), and since then, it has been successfully used for the treatment of domestic and industrial wastewater. On research, it has been discovered that certain materials such as rice husk (or hull), coconut fiber (coir), sugar cane (also known as bagasse), maize cobs, sawdust, bed of sand, peat, shredded tires, foam, crushed glass, geo-textile fabric, and anthracite can be used for wastewater treatment in treating impurities present in the wastewater.
According to Benetti, (2008), water, food, and energy supply are the three main problems faced by the world today. Therefore, to solve these problems, domestic wastewater is now treated as a resource instead of a waste. The 1st and 3rd problems can be solved by treating wastewater for domestic consumption, landscaping, and crop irrigation. This process saves water as well as utilizes the fertilizing elements wastewater contains. Domestic wastewater can be used as a source of energy through anaerobic digestion, to solve the 3rd problem. It involves the production of methane gas (CH4) from wastewater organic content by anaerobic digestion (Myint, Nirmalakhandan, and Speece, 2007).
Day (1996) presented due to the massive increase in the world’s human population, water will become one of the scarcest resources in the 21st century. As human numbers increase, there would be greater strains on the available resources and a greater threat will be posted on the environmental sources. A report by the Secretary-General of the United Nations Commission on Sustainable Development (UNCSD, 1997) concluded that there is no sustainability in the current use of freshwater by either developing or developed nations and that worldwide, water usage has been growing at more than three times the world’s population increase, consequently leading to widespread public health problems, limiting economic and agricultural development and adversely affecting a wide range of ecosystems. This has motivated more comprehensive research in water treatment and management.
Given the above-cited problems, wastewater must be properly treated and managed to retain equilibrium in the earth. Wastewater treatment in many countries is relatively expensive and people would not readily want to engage in such due to the expenses in putting up a sewage treatment plant or activated sludge system. They would rather opt-out to use the general septic tanks which are below the earth's surface and would continually pollute underground water as the population of people increases. The reasons behind the high price of establishing one of the above-listed wastewater treatment techniques are; the limitation in materials to be used, low numbers of expertise, inaccessibility of the technology, unavailability of infrastructure that supports such systems, and money to access the technology. In this study, the suggestion of certain biofilter materials such as; coconut fiber (coir) that are easily accessible in the environment especially in African and European countries where a lot of fiber food is consumed if properly invested into, will reduce the outrageous prices of wastewater treatment, make it user friendly as well as easily accessible. Thus, by the discoveries made in the preparation process of this study, the whole engineering world can go a step closer in the reduction of costs and expensive filtration medium.
The study aims to maximize the use of a certain material easily accessible in the environment which is coconut fiber (coir) for tertiary wastewater treatment.
Specifically, the research is set out to achieve the following objectives:
The deliverables of this project are a project report, influent of wastewater sample, the effluent of filtered wastewater sample through coir, as well as results and comparison. The influent and effluent would be tested for physical, chemical, and biological parameters of wastewater according to WHO and national standards and would be compared to the calculated efficiency and treatment rate of coir. Also, the report should contain complete documentation of the laboratory experiment procedure from start to finish, how various process variables were gotten, how the physical, chemical, and biological parameters were tested and the instruments used for the test, as well as how the biofilter was used and how the results were gotten.
This project mainly focuses on the assessment of the usage of coconut fiber (coir), a material regarded as agricultural waste in the tertiary treatment of wastewater. In simple terms, using waste to treat waste.
This project focuses on secondary research and laboratory experiments. They are discussed below:
The secondary research in this project will utilize a systematic approach (Johnson et al., 2016) to review the works of literature. The steps involved in the systematic review of the literature are provided below:
Step 1: Identify the research questions that can be used for the project.
Step 2: Identify the keywords that should be used to research the works of literature.
Step 3: Extract the journals and books that are appropriate for this project.
Step 4: Write the literature review chapter.
The laboratory experiments would cover a large part of this project. They would be carried out in stages, and as such described below;
The risk assessment conducted for this project is provided in the table below:
Table 1: Risk assessment
Risk
Impact
Mitigation Plan
Inability to meet the deadline
Low
Get an extension from the supervisor in due time
Inability to get required process inputs
Moderate
Refer to municipalities, research institutes, and laboratory technicians for help
Inability to properly develop the wastewater treatment process set up
Refer to laboratory technicians for help
Inability to test for a wide range of physical, chemical, and biological properties of the sample
High
Use important and custom parameters for making conclusions.
Insufficient data
Refer to journals and textbooks for help
Table 2: Project Plan
Task Name
Start Date
End Date
Duration (Days)
Initial Research
15/01/2022
29/01/2022
14
Proposal
06/02/2022
21
Secondary Research
18/03/2022
40
Introduction Chapter
23/03/2022
5
Literature Review Chapter
20/04/2022
24
Methodology Chapter
02/05/2022
12
Sourcing of required wastewater samples and materials
02/06/2022
30
Presentation 1
10/06/2022
8
Laboratory Experiments
24/06/2022
Evaluation of Gotten Results
01/07/2022
7
Discussion Chapter
11/07/2022
10
Evaluation Chapter
16/07/2022
Conclusion Chapter
18/07/2022
2
Project Management Chapter
20/07/2022
Abstract and Report compilation
22/07/2022
Report Proofreading
01/08/2022
Presentation 2
11/08/2022
Adu-Ahyiah, M. and Anku, R. E. (2010). “Small Scale Wastewater Treatment in Ghana (a Scenario)” Retrieved, 03-10-2010:1-6
Amoatey Peace (Mrs.) and Professor Richard Bani (2011). Wastewater Management. Waste Water - Evaluation and Management, Faculty of Engineering Sciences, University of Ghana, Ghana.
Benetti, A.D. 2008. Water reuse: issues, technologies, and applications. Engenharia Sanitaria eAmbiental, 13(3), 247-248.
Day, D. (1996). How Australian social policy neglects environments. Australian Journal of Soil and Water Conservation, 9: 3-9.
Dhote, J., Ingoleb, S. and Chavhana, A., 2012. REVIEW ON WASTEWATER TREATMENT TECHNOLOGIES. International Journal of Engineering Research & Technology (IJERT) ISSN: 2278-0181, Vol. 1(Issue 5).
Johnson, D., Deterding, S., Kuhn, K.A., Staneva, A., Stoyanov, S., and Hides, L., 2016. Gamification for health and wellbeing: A systematic review of the literature. Internet interventions, 6, pp.89-106.
Korfali S.I. and Jurdi M. (2011). Suitability of surface water for domestic water use: Awali River case study. European Waters 35, 3-12,2011.
Melidis P., Vaiopoulou E., Aivasidis A., An activated sludge treatment plant for integrated removal of carbon, nitrogen, and phosphorus, Desalination, Volume 211, Issues 1–3, 2007, Pages 192-199, ISSN 0011-9164. https://doi.org/10.1016/j.desal.2006.02.092.
Metcalf and Eddy, Inc. (1991) “Wastewater Engineering”: Treatment Disposal and Reuse, third edition. New York: McGraw-Hill.
Metcalf and Eddy, Inc. (2003) “Wastewater Engineering: Treatment and Reuse,” Fourth edition.: McGraw-Hill, New York.
Myint M., Nirmalakhandan N., and Speece R.E., (2007). Anaerobic fermentation of cattle manure: Modeling of hydrolysis and acidogenesis, Water Research, Volume 41, Issue 2, Pages 323-332, ISSN 0043-1354. https://doi.org/10.1016/j.watres.2006.10.026.
Peavy, S. H., Rowe, D. R. and Tchobanoglous, G., (1985) Environmental Engineering, International Edition MacGraw-Hill 207-322.
Qadir M., Wichelns D., Raschid-Sally L., McCornick P.G., Drechsel P., Bahri A., Minhas P.S. The challenges of wastewater irrigation in developing countries, Agricultural Water Management, Volume 97, Issue 4, 2010, Pages 561-568, ISSN 0378-3774. https://doi.org/10.1016/j.agwat.2008.11.004.
Welch, E.B., & Naczk, F. (1992). Ecological Effects of Waste Water: Applied limnology and pollutant effects, Second Edition (2nd ed.). CRC Press. https://doi.org/10.4324/9780203038499
Last updated: Jan 04, 2022 12:37 PM
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