CE 6305 Water pollution and its control Term paper On WATER POLLUTION AND ITS CONTROL STRATEGIES IN KHULNA CITY PERSPECTIVE Submitted To Khondoker Mahbub Hassan Professor Department of Civil Engineering Submitted By Name: Md.Tahasin Khan Roll No: 1901560 Department of Civil Engineering Khulna University of Engineering & Technology Khulna-9203, Bangladesh Abstract Khulna is the third largest city of Bangladesh and situated at the Southwest region of the country having 1.4 million populations living in 45.65 square kilometers area. It has been facing growing urban environmental problems due to daily generated wastewater. There is no sewerage network or any central treatment system in Khulna city. Conventional wastewater treatment plant needs large space for treating vast quantities of wastewater and also requires very high initial as well as operation and maintenance cost. This study is concerned about the two decentralized wastewater treatment (DEWAT) plants constructed at the Peoples Panchtola Colony' at Khalishpur in Khulna. DEWAT system may be defined as the collection treatment, and disposal or reuse of wastewater from individual homes, clusters of homes, isolated communities, industries or industrial facilities at or near the point of waste generation. The specific objectives of this study were to study the performance of two DEWAT plants regarding its technical and socio-economic acceptance by ordinary population in Panchtola Colony, compare the performance of two DEWAT plants based on field and laboratory investigations. To conduct necessary investigation both in field and laboratory, wastewater samples were collected from six different points. The experimental results when wastewater passed through ABR, achieved removal efficiency are 65%, 64%, 93%, 44%, 32%, 48%, and 50% for BOD5, COD, TSS, TDS, FC, Nitrate and Phosphate respectively in the DEWAT plant . The results show that the concentration of all harmful parameters were reduced significantly and lowered to an acceptable level. The results also indicate the effectiveness of ABR and AFBBR over the planted gravel filter considering the area required for PGF. Introduction Due to unaffordable cost of construction, most of the drains in the towns and cities are open and as a result they are misused, sometimes serving as defecating sites for homes without adequate toilet facility(Arifurrahman et al., 2013).Sewage water management is one of the major environmental issues of recent times. Waste is produced by all human being, but the amount is very large for humans. So it is our responsibility to manage it efficiently. Due to rapid urbanization, industrialization and massive growth of population waste management has become more critical nowadays. Normally if the quantity of waste water is small, nature can cope with it but if large amount of wastewater and sewage are not treated then nature can’t endure it. Normally sewers are discharged into lake, river, and stream. But now in developed countries it is not directly discharged into it. At first the water is treated then it is discharged. In most of the case in Bangladesh though there is soak well in office building, there is hardly any septic tank in residential or private building. Though the population is increasing in an alarming rate the area is same. In major cities of Bangladesh the buildings are congested so there is not enough area for the treatment process. So the management process should be done carefully keeping in mind of the little space. Waste produced by residential buildings should be treated before discharging to the environment. Sewage is of two kinds one is black water, which is from toilet and the other is gray water, which is from domestic uses except toilets. Bangladesh provides a striking example of progress to meet the Millennium Development Goal (MDG) - 7 to halve, by 2015, the “proportion of urban population with access to improved sanitation”. Open defecation has reduced from 19% in 2000 to 3% in 2012, though 53% of households still do not use improved sanitation (WHO-UNICEF, 2014). Blockage of drainage systems occurred for wastewater overflow during rainy season. In consequence, self-purification capacity of receiving water bodies is overloaded and it causes surface and ground water pollution, impacting directly to the health of community, reducing the value of environment(Systems, 2002). Progress in reducing open defecation and use of improved sanitation in Bangladesh has been remarkable. Only 4% of the population are practicing open defecation, 15% of the population are using unimproved latrines, 25% of the population are sharing improved latrines and 56% of the population are using improved latrines (WHO-UNICEF, 2014). According to JMP, open defecation reduced from 34% in 1990 to 3% in 2012 and now it said to be of 1% (WHO-UNICEF, 2014).Conventional wastewater treatment plant needs large space for treating vast quantities of wastewater and also requires very high initial as well as operation and maintenance cost that Khulna municipality faces structural and financial adjustment problems (Shuma rani saha, 2014). Sewage/Wastewater treatment involves breakdown of complex organic compounds in the wastewater into simpler compounds that are stable and nuisance-free, either physio-chemically and or by using micro-organisms (Cheremisinoff, n.d.). Methods of wastewater treatment were first developed in response to the adverse conditions caused by the discharge of wastewater to the environment and the concern for public health. Further, as cities became larger; limited land was available for wastewater treatment and disposal, principally by irrigation and intermittent filtration. Also, as populations grew, the quantity of wastewater generated rose rapidly and the deteriorating quality of this huge amount of wastewater exceeded the self-purification capacity of the streams and river bodies(Spellman, 2010). Khulna is the third largest city of Bangladesh located in the south-western part of the country and lies in the delta of the river Ganges. The city has an estimated population of 1.6 million and total number of household is 66,257 (SNV, 2014). Human deposits about 70 g per capita per day of solids into water and also produce more and more waste water daily. Direct or indirect contact to wastewater and fecal sludge is associated with microbial and chemical hazards, which frequently result in adverse effect both on humans and animals. Khulna City Corporation (KCC) is adversely affected by the influence of sewage water. This city has no sewer network. The household sanitation is predominantly on-site technologies, 68.4% septic tanks and 31.6% pits(Foundation, 2011), which require regular emptying. But formal emptying is rare as most are directly connected to surface water drains or water bodies. In many developed countries, fecal sludge is often allowed to accumulate in poorly designed plant whereas this scenario is not very common in the developing countries. Without proper management, fecal sludge is often allowed to accumulate in poorly designed pits and wastewater is discharged into storm drains and open water, or is dumped into waterways, wasteland, and unsanitary dumping sites (Water and Sanitation Program, 2014).The major obstacle on the way to successful implementation of any sewage treatment process in middle and low income countries are the stake holders. In Khulna as well as Bangladesh, the key stakeholders are household’s users and owners, municipal authority, pit or septic tank emptier or sweepers, government, local or international organizations and NGOs with sanitation activities. Adequate water and wastewater management, essential for human health and economic Development, poses a major challenge to many countries around the globe. Whereas in Industrialized countries water and wastewater control had reached a fairly high Standard, in lower and middle income countries1 severe problems with respect to water Supply and wastewater management are still apparent (Hophmayer-Tokich, 2006). As the water supply system is given the first priority, waste water treatment is lagging behind and is becoming a major issue in different cities in a developing country like Bangladesh. The main aim of this paper is to investigate the existing treatment systems, assessment of raw sewage and effluent sewage quality through different treatment systems in small space. Materials and Methods Performance study of existing two DEWAT plant and its modification Baseline survey Questionnaire for DEWAT users Questionnaire for non DEWAT users Analysis of field data Evaluation of socioeconomic acceptance of DEWAT plant Identification of technical problems in O & M Collection of wastewater samples Laboratory determination of wastewater quality parameters Analysis of test results Comparison of performance of existing two DEWAT plants Providing recommendations for necessary modifications of DEWATS for its sustainable development Fig 1: Flowchart showing the sequential steps in the research works Selection of study area After the independence in 1971 there was no reformation of the pipes that were used in khalishpur area. Among all the wards in Khulna, The wards under khalishpur have the worst sanitation system. The sewerage system is directly connected to the drain which is very harmful. Most of the residential building don’t have any soak pit. That’s why the BOD and fecal coliform limit for wastewater crosses the allowable limit and causes different diseases to different people. Here sewage and waste from residential buildings are dumped beside their residence as there is hardly any sewerage systems or dumping place for management. That’s why the area under ward no.10 was selected to be surveyed. Fig 2: Khulna City Corporation wards Two DEWAT plants have been already constructed in Panchtola Colony at Khalishpur in Khulna by a local NGO named as Nabolok. A field survey was carried out to investigate the performance of the existing DEWAT plants. A sample of 166 families who are users of DEWAT plants was selected. Family interviews were conducted in the families of the colony. This was done with assistance of a Nabolok staff One questionnaire was prepared for the users of DEWAT plants considering much information such as general, socio-economic, environmental condition, hygiene practice, benefits of DEWAT plant, maintenance of DEWAT plants, and aesthetic view of DEWAT plant, and recommendation on existing DEWAT plants. The aim of this survey was to find out the socio-economic acceptance and technical problems of existing DEWAT plant Fig 3: DEWATS system A total of 1 liter sample was collected in 6 bottles from six different points such as inlet and outlet of settler tank, middle of AFBBR, outlet of ABR, PGF and PP of two existing DEWAT plants of the Panchtola Colony. Wastewater samples were collected from the DEWAT plants once a month. Then the sample bottles were put in a cool box with ice cubes before being transported to the environment laboratory at KUET campus. This was to prevent any change of wastewater quality which could occur between the time of collection and analysis in the laboratory. Some parameters which were determined immediately upon arrival in the laboratory included Faecal Coliform, DO and BOD5. - Results and Discussion To get a broad view of community acceptance and management of the system, interviews were carried out with key stakeholders. The interviewees were local people, relevant stakeholders and authorities. This work gave few answers and evidences. Total 166 families were using the DEWAT plants. During the field inspection, the users were asked only how much money they spent when they had been suffering from diarrhea, cholera, hookworms etc. before implementation of DEWAT plants.In this study, six sampling points of the two DEWAT plants and eleven experimental parameters were selected as stated by Nabolok with the assistance of Water Aid Bangladesh. Those points are in and outlet of settler tank, middle of anaerobic filter bed baffled reactor, outlet of anaerobic baffled reactor, planted gravel filter and polishing pond. It is observed from the result that when wastewater passed through ABR, achieved removal efficiency are 65%, 64%, 93%, 44%, 32%, 48%, and 50% for BOD5, COD, TSS, TDS, FC, Nitrate and Phosphate respectively in the DEWAT plant. Removal efficiency only planted gravel filter are 61%, 37%, 38%, 12%, 29%, 38%, and 29% concentration based removal efficiency for BOD5, COD, TSS, TDS, FC, Nitrate and Phosphate respectively. Removal efficiency only polishing pond are 28%, 37%, 45%, 11%, 39%, 34%, and 38% for BOD5, COD, TSS, TDS, FC, Nitrate and Phosphate respectively. Moreover, the total construction cost of DEWAT plant was BDT 900000, whereas the construction cost of planted gravel filter was BDT 343112 (Table 4.9). It is observed from the result (Table 4.8) that when wastewater passed through ABR, the 2' DEWAT plant achieved 58%, 38%, 93%, 38%, 29%, 53%, and 37% for BOD5, COD, TSS, TDS, FC, Nitrate and Phosphate respectively. Removal efficiency only planted gravel filter are 58%, 21%, 26%, 13%, 24%, 38%, and 28% concentration based removal efficiency for BOD5, COD, TSS, TDS, FC, Nitrate and Phosphate respectively. Removal efficiency only polishing pond are 34%, 38%, 58%, 18%, 28%, 60%, and 23% for BOD5, COD, TSS, TDS, FC, Nitrate and Phosphate respectively. Moreover, the total construction cost of 2 DEWAT plant was BDT 1500000, whereas the construction cost of planted gravel filter was BDT 834762 Table 1: Comparison of the 1st and 2nd DEWAT plants Parameters Mean removal efficiency, (%) 1st DEWAT plant Mean removal efficiency, (%) 2nd DEWAT plant BOD5 88.58 83.37 COD 77.12 58.12 TSS 92.26 96.22 TDS 39.87 19.3 FC 65.86 17.66 Nitrate 52.75 68.73 Phosphate 52.91 37.28 Conclusions This research investigated the performance of Decentralized Wastewater Treatment Plants in Khulna. The study had four major objectives: (a) to study the performance of two DEWAT plants regarding its technical and socio-economic acceptance by ordinary population in Panchtola Colony in Khulna, Bangladesh; (b) to compare the performance of two DEWAT plants based on field and laboratory investigations Concerning the first objective of this thesis, the performance of DEWAT plants regarding its technical and socio-economic acceptance by ordinary residents in Panchtola Colony in Khulna, Bangladesh is highly appreciated in response to colony residents who are using the DEWAT plant .With reference to second objectives of this paper, from the performance study of two DEWAT plants it can be seen that the removal rate was higher in the 1st DEWAT plant compared to the 2nd DEWAT plant. According to economic point of view, DEWAT plants were impended as a source of water supply for irrigation purposes. It was found that treated wastewater comes from polishing can be reused for irrigation purposes or reused for the community toilet flushing. DEWAT plants can be reduced the withdrawal of fresh water from ground water. DEWAT plants not only save fresh water but also save withdrawal cost such as power cost. DEWAT plants were also profitable through reduction of medical cost and loss of income due to illness which is another positive attitude of this technology. Finally, it can be concluded that the modified DEWAT system should be practiced in low incoming developing countries as a mid-term solution to improve the sanitation condition. - Reference Adu-ahyiah, M., & Anku, R. E. (2001). Small Scale Wastewater Treatment in Ghana ( a Scenerio ). Design, (1), 1–6. Arifurrahman, S. … Khair, S. (2013). Scenario of Clinical Waste Management : A Case Study in Khulna City, 13(8), 978–984. Cheremisinoff, N. P. (n.d.). HANDBOOK OF WATER AND WASTEWATER TREATMENT TECHNOLOGIES. Foundation, M. G. (2011). Landscape Analysis and Business Model Assessment in Faecal Sludge Management : Extraction and Transportation Models in Bangladesh Final report – Bangladesh 20 October 2011, (October), 1–67. Hophmayer-Tokich, S. (2006). Wastewater Management Strategy: centralized versus decentralized technologies for small communities. CSTM-Reeks, 271(271), 27. Retrieved from https://research.utwente.nl/en/publications/wastewater-management-strategycentralized-v-decentralized-techno Shuma rani saha. (2014). Study on the Decentralized Wastewater Treatment Plants in Khulna $. Spellman, F. R. (2010). Spellman’s standard handbook for wastewater operators. CRC Press (Vol. II). https://doi.org/10.1201/EBK1439818862 Systems, W. T. (2002). Decentralized wastewater treatment - new concept and technologies for Vietnamese conditions. Science And Technology, (September), 24–26. Arifurrahman, S. … Khair, S. (2013). Scenario of Clinical Waste Management : A Case Study in Khulna City, 13(8), 978–984. Cheremisinoff, N. P. (n.d.). HANDBOOK OF WATER AND WASTEWATER TREATMENT TECHNOLOGIES. Foundation, M. G. (2011). Landscape Analysis and Business Model Assessment in Faecal Sludge Management : Extraction and Transportation Models in Bangladesh Final report – Bangladesh 20 October 2011, (October), 1–67. Hophmayer-Tokich, S. (2006). Wastewater Management Strategy: centralized versus decentralized technologies for small communities. CSTM-Reeks, 271(271), 27. Retrieved from https://research.utwente.nl/en/publications/wastewater-management-strategycentralized-v-decentralized-techno Shuma rani saha. (2014). Study on the Decentralized Wastewater Treatment Plants in Khulna $. Spellman, F. R. (2010). Spellman’s standard handbook for wastewater operators. CRC Press (Vol. II). https://doi.org/10.1201/EBK1439818862 Systems, W. T. (2002). Decentralized wastewater treatment - new concept and technologies for Vietnamese conditions. Science And Technology, (September), 24–26.