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1986, American Journal of Public Health
AI
The paper discusses the long-standing practice of reclaiming wastewater for agricultural use and the emerging health concerns associated with its direct and indirect consumption. It highlights historical examples, such as the case in Chanute, Kansas, where municipal wastewater was treated and reused during a water crisis, noting the challenges in public acceptance despite meeting safety standards. The paper emphasizes the need for careful consideration of the potential health impacts of using treated wastewater, particularly in areas facing water scarcity, while also underscoring the importance of proper treatment processes.
Irrigation and Drainage - Sustainable Strategies and Systems, 2015
International Journal for Research in Applied Science & Engineering Technology (IJRASET), 2022
Water reuse generally refers to the process of using treated wastewater (reclaimed water) for beneficial purposes such as agricultural and landscape irrigation, industrial processes, nonpotable urban applications (such as toilet flushing, street washing, and fire protection), groundwater recharge, recreation, and direct or undirected water supply. Its increased application has been facilitated by modern wastewater treatment processes that have advanced substantially during the twentieth century. Water Reuse is a reality at international. Several practices have emerged around the world as results of different needs, perspectives and policies. Accelerating development occurred in the past 15 years, especially in the application field of potable reuse. Technologies and treatment flowsheets have been studied and validated, demonstrating advanced water quality, safety and suitability for potable reuse applications. Reuse of wastewater after its treatment may be a good alternative for regions, which suffer from lack of pure water or have limited access to water resources. Effective water reuse applications require a combination of advanced treatment technologies. Increasingly these include a combination of low-pressure technologies MF/UF followed by NF/RO (high pressure) to provide a high-quality grade of water. Submerged membrane bioreactor systems (MBR) have also become a viable alternative for wastewater reuse technologies. Reuse technologies may be applied for municipal and industrial wastewater. Reuse of wastewater is only possible if sanitary and environmental safety is provided with no hazard for current ecosystem. That fact requires strict fulfilment of laws and regulation. Wastewater to be reused has to follow a certain sequence of treatment procedures to reduce concentration of pollutants in it. Water reuse (also commonly known as water recycling or water reclamation) reclaims water from a variety of sources then treats and reuses it for beneficial purposes such as agriculture and irrigation, potable water supplies, groundwater replenishment, industrial processes, and environmental restoration. Water reuse can provide alternatives to existing water supplies and be used to enhance water security, sustainability, and resilience that might be traditional methods (waste separation, sedimentation), methods of removal of certain components (nitrogen and phosphorus), disinfection.
Treated wastewater (TWW) reuse in South Africa is historically limited to irrigation of recreation facilities (sports fields, urban parklands). In rare instances, uses of these waters are allowed for food-related activities such as fodder production. Environmental health practitioners discourage reuse of TWW for aquaculture and production of edible crops for fear of adverse health effects. However, South Africa is a semi-arid county with erratic rainfall patterns. Demands from communities in and around urban areas to use treated wastewater for food production in small-scale farming practices are rapidly increasing. The Department of Health applies the South African Guidelines for the Permissible Re-Use of Treated Sewage Effluents (1978) to help regulate reuse of treated wastewater. The Guideline approach appears to favour the treatment method -and configuration that produces the effluent -as a benchmark for decision-making rather than the actual quality of such effluent. Reuse applications that involve more elaborate treatment facilities (primary, secondary and tertiary treatment processes within the configuration) would generally be favourably considered for purposes of food production and recreation-related applications. Applications for the reuse of effluent from waste stabilisation pond systems (WSP) are generally discouraged -regardless of the effluent quality. To illustrate this discrepancy a study was undertaken over a period of twelve months to assess the levels of faecal coliform bacteria in the effluent of two system categories. ➀ Two fully configured waste stabilisation facilities. ➁ Two waste stabilisation ponds, each consisting of a series of an initial anaerobic pond followed by several facultative ponds and ending with maturation ponds. There were no statistical significant differences in the effluent quality. Further discrepancies are illustrated in another study undertaken over the same period that compared the levels of faecal coliform bacteria in the effluents of the abovementioned system categories to that of a public stream receiving polluted urban surface runoff. There were statistically significant differences in the quality, with higher levels of faecal coliforms in the stream. Yet, unrestricted irrigation of food crops could be undertaken from the public stream. In practice this implies that the Guide (1978) does not provide the public health protection desired, nor suitable discretionary measures that may conditionally permit the reuse of treated wastewater -regardless of the system producing the effluent. Officials would therefore tend to implement an absolute precautionary principlethereby denying poor communities the sustainable use of a valuable resource.
2006
Of the projected 1 billion growth in global population by 2015, 88 percent will take place in cities, nearly all of it in developing countries. Investments in urban water supply and sewerage coverage are rising. However, adequate treatment for agricultural reuse with acceptable risk mitigation for human health and the environment will require further investment. While this Investment Note addresses reuse after treatment, it is critical to ensure that investments in treatment appropriate for reuse schemes will be made. Urban wastewater is well suited to agricultural reuse and landscaping because of the reliability of supply, proximity to urban markets, and its nutrient content. To have an impact on scarcity, reuse of wastewater must substitute for, not add to, existing uses of higher-quality water. Moreover, reuse of treated wastewater often disproportionately benefits the poor. It must be combined with strategies to prevent or mitigate health risks from pathogens, heavy metals, pest...
2014
In Greece, and particularly in many southeastern and island areas, there is severe pressure on water resources, further exacerbated by the high demand of water for tourism and irrigation in summertime. The integration of treated wastewater into water resources management is of paramount importance to meet future demands. Despite this need, only a few projects of effluent reuse have been implemented, most of them being pilot projects of crop or landscape irrigation. The most important projects which are currently in practice are those of Thessaloniki, Chalkida, Malia, Livadia, Amfisa, Kalikratia, and Chersonissos. In Thessaloniki, at the most important wastewater reuse site, the secondary effluent of the city's Waste Water Treatment Plant (WWTP) (165,000 m 3 /day) is used for agricultural irrigation after mixing with freshwater at a 1:5 ratio. The main crops irrigated are rice, corn, alfalfa and cotton. A few other projects are under planning, such as that at Iraklion, Agios Nikolaos and several island regions. Finally, it should be mentioned that there are several cases of indirect reuse, especially in central Greece. However, the reuse potential in Greece is limited, since effluent from Athens's WWTP, serving approximately half of the country's population, is not economically feasible due to the location of the plant.
13 De facto wastewater reuse is the incidental presence of treated wastewater in a water supply 14 source. In 1980 the EPA identified drinking water treatment plants (DWTPs) impacted by 15 upstream wastewater treatment plant (WWTP) discharges and found the top 25 most impacted 16 DWTPs contained between 2% and 16% wastewater discharges from upstream locations (i.e. de 17 facto reuse) under average streamflow conditions. This study is the first to provide an update to 18 the 1980 EPA analysis. An ArcGIS model of DWTPs and WWTPs across the USA was created 19 to quantify de facto reuse for the top 25 cities in the 1980 EPA study. From 1980 to 2008, de 20 facto reuse increased for 17 of the 25 DWTPs, as municipal flows upstream of the sites increased 21 by 68%. Under low streamflow conditions, de facto reuse in DWTP supplies ranged from 7% to 22 100%, illustrating the importance of wastewater in sustainable water supplies. Case studies were 23
Desalination, 2006
Wastewater reclamation holds promise as an important water resource as the desire to develop arid regions continues to place increasing demands on finite water resources. The debate surrounding the consumption of reclaimed wastewater finds risk managers pondering the question of what types of water quality standards might be set in order to provide the proper level of safety associated with the use of reclaimed wastewater. We propose quality categories for different reuses such as irrigation or indirect aquifer recharge with different requirements towards microbial and chemical parameters. Based on recent existing guidelines and risk estimations, microbial and chemical limits for each category were compiled. Since economic calculations are very important, analytical costs are included and measurements frequency is proposed. Biological parameters have to indicate all potential pathogenic organisms including viruses, bacteria and parasites from different origins. The selected biological indicator parameters most used in rules and regulations are coliforms and E. coli, indicating the occurrence of a former faecal contamination and the possible presence of all pathogens occurring in faeces of warm-blooded animals. In the case of wastewater reuse, biological parameters have to indicate all potential pathogens causing infection diseases and/or intoxication in all living beings including plants and animals. The large number of possible chemical parameters in relation with wastewater reclamation and reuse has to be adapted and minimized with respect to the origin of the sewage, the extent of the treatment process and the intended use. These parameters must cover a broad spectrum of toxicological and ecological risks as well as possible technical disorders. Risk assessment and risk management are also necessary.
7th International Conference on Thermal Equipment, Renewable Energy and Rural Development (TE-RE-RD)
The problem of water resources is aggravating as a result of accelerated urbanization, population growth, industrial and agricultural development. In addition to these factors, climate changes represent a substantial risk because it affects considerably both water resources and crops. Globally, agriculture is the largest consumer of water, accounting for approximately 70% of all freshwater. Farmers in many arid and semiarid areas are forced to find solutions to irrigate their crops, so they often must use treated, untreated or undiluted wastewater which is cheaper than other water sources. Increasing water needs (for drinking, food and irrigation) make the use of effluents (treated wastewater) an effective solution to solve the problem of water scarcity, to save significant quantities of drinking water, to reduce the use of chemical fertilizers (nutrients in the wastewater can replace conventional fertilizers), thereby protecting the environment and improving crop yield.
Annals of the New York Academy of Sciences, 1977
The recent concern about the possible health effects of reuse of waste water for potable supply was prefaced by numerous discussions of the topic during the 1950s. Berger' discussed whether it is feasible to treat sewage so that the water recovered may serve all municipal purposes, including human consumption. Specifically, that report described reuse of a high proportion of sewage for potable supply during a several-month period in Ottumwa, Iowa,' in 1940, and in Chanute3 and Lyndon, Kansas,' in 1956. At that time, the main emphasis was on health risks due to microbiologic contamination of the reclaimed water. In 1959, Essen, Federal Republic of Germany had to use the Ruhr River for its water supply; the river contained up to 86% of effluent, which caused nonbacterial gastroenteritis among 7% of the population of the cityS during that crisis.
Annual Review of Public Health, 1982
Wastewater reuse is one element of the water resources management of an area. Reuse involves considerations of public health and may also involve considerations of water conservation, water pollution control, and water utility management. Among sanitary engineers this has been a subject of growing interest for at least three generations. Reuse is only one alternative in planning to meet the water resource needs of an area. Water recycling, water conservation, and new project development are other alternatives. Whether reuse will be appropriate depends upon economic considerations, potential uses for the reclaimed water, the degree of severity of waste discharge requirements, and public policy wherein the desire to conserve rather than develop available water resources may override economic and public health considerations. Domestic wastewater was first reused in the nineteenth century with the development of sewerage systems. Farms using raw sewage were established in England, Australia, Germany, France, and Italy after 1870. By 1900 sewer farms were numerous in the old and the new world; for example, ten California communities had sewer farms. These "farms" were primarily disposal operations and incidental use was made of the water for crop production. It is reported that by 1910, 35 California communities were using sewage for irrigation-II without previous treatment, 24 after septic tank treatment (1). Gradually, landmark "uses" were initiated. In 1926, at Grand Canyon National Park, treated wastewater was fi rst used in a dual water system for 419
GeoJournal, 1981
Recycling is all around us: notebooks come loaded with recycled paper, parks have playground mats made of recycled tires, and younger children everywhere get the opportunity to recycle the clothes of their older siblings. But what about recycled water? The thought of reusing water is somewhat counterintuitive-the water we receive must be fresh and clean, according to both our standards and those of the U.S. government. However, all of the water on the planet is technically recycled water. In a closed system like Earth, the water coming out of your tap has probably been through the water cycle tens of thousands of times, passing through dinosaurs, pharaohs, and astronauts along the way. Though the water our utilities send out is most definitely old, it is always cleaned up to drinking water standards in water treatment plants prior to distribution (Fig. 1). This drinking-quality water is used for many purposes beyond drinking, including lawn and landscape irrigation, toilet-flushing, and industrial processes. The used water then heads to a wastewater treatment plant, where it can be cleaned up again before it is released into a body of surface water. This is where wastewater reclamation comes in: the wastewater in these treatment plants can be treated back up to high standards of purity that allow reuse.
Irrigation with polluted water or wastewater is a widespread reality, especially in low-income countries where it is popularly used for vegetable cultivation. Yet many policymakers are unaware of the significance of the practice and the benefits it can bring. Nor do they know that practical recommendations are now available to make wastewater use safer and more sustainable without relying on non-affordable treatment technologies alone. These recommendations tackle the problem from many angles, over the short, medium and long term, and harmonize with new World Health Organization guidelines. Vegetable production on open spaces in Kumasi, Ghana, using highly polluted stream water Photo credit: IWMI
Recent Progress in Materials
Water recycling is a potential tool for reducing the dependency on traditional water sources, which would eventually reduce the likelihood of volumetric restrictions and their impacts on the water sector. Therefore, exploration, development, and use of alternative water sources are required for sustainable development. Scientific studies on the efficient and economical use of nontraditional water sources developed using the recycling process have attracted the attention of agriculturists, planners, and engineers for the last two decades. Recycled wastewater types, including greywater, sewage, stormwater, and industrial wastewater, have been discussed in this study. This article reviewed various forms of recycled wastewater, especially wastewater from treated sewage, and their effects on human health and irrigated environment. In addition, the necessity of exploration and usage of alternative sources of water in agriculture over traditional sources has also been reviewed. Legislation...
Polish Journal of Environmental Studies
With the increasing population and urbanization in the world, generated wastewater is an alternative to water scarcity. Treated wastewater has environmental, human health and socioeconomic benefits. However, in Africa, 95% of raw-wastewater is released into the environment. Therefore, this paper emphasizes wastewater reuse meeting the standard criteria, particularly in Africa. Data were collected based on peer review literature on wastewater reuse systems, and handling systems in general and specifically in Africa. In addition, online publications and onsite visits in Burkina Faso and Nigeria allow apprehending wastewater reuse systems in the world including Africa. Then, analysis was done and challenging prospects were identified. Results show that from ancient to the present, wastewater is disposed of or reused for different purposes. Because of increasing waterborne diseases, advanced water reclamation technologies were developed for water reuse. In Africa, raw wastewater is still disposed of and reused while cost-effective technologies and facilities are now developed for wastewater reclamation. Consequently, populations are suffering from waterborne diseases. Produced effluent meeting the standards for reuse is the appropriate treatment. To make it possible in Africa, leaders must pay attention to population wellbeing as a priority, to infrastructures and their maintenance, to integrated technologies for cost-effective treatment, and to consider the removal of antimicrobial resistances.
DEĞİŞEN ve DÖNÜŞEN DÜNYADA MÜHENDİSLİK BİLİMİ: DİSİPLİNLER ARASI BİR YAKLAŞIM, 2021
Global concerns about water scarcity have led to studies and approaches to beneficial reuse of treated wastewater. Today, in many countries in the world, studies are carried out on sustainable water resources management and water efficiency in order not to face bad scenarios. The reclamation and reuse of used water is considered as a globally accepted solution alternative. Due to the decreasing fresh water resources, the treatment of waste water with appropriate methods and the evaluation of its reuse in various fields has become a necessity today. In order to eliminate the shortage of fresh water, the use of treated wastewater other than drinking water is encouraged. Studies show that treated domestic and industrial wastewater can be used in many areas such as agriculture, aquaculture, industrial, domestic and recreational use in many parts of the world.....................
County Sanitation District No.14 of Los Angeles County operates the Lancaster Water Reclamation Plant in a way that promotes beneficial reuse of the treated effluent. Current beneficial uses include agricultural irrigation of fodder crops, maintenance of an aquatic habitat, and municipal recreation. The District is implementing a plan for accommodating a projected increase in population and the accompanying increase in wastewater generation. The plan includes replacing the existing 16-MGD (60.560 m 3 /d) oxidation pond facilities with a 26-MGD (98.410 m 3 /d) tertiary treatment facility, which will include activated sludge, filtration, and disinfection. In addition to the existing reuse sites, future sites will include an expanded agricultural operation and municipal projects.
Current Opinion in Environmental Science & Health, 2018
Index 3.1. Introduction 3.2. Rationale of the wastewater treatment processes 3.3. Advances on wastewater treatment and reclamation 3.4 Objectives and requirements of wastewater reuse regulations 3.5 Conclusions 3.6 References Summary To implement tariffs and regulations on sanitation and wastewater treatment, as well as for disposal or reuse of treated effluents, it is necessary to know the treatment technologies, which one would be best adapted to the present circumstances of any site and finally if the treated wastewater can be disposed of, legally or reused complying the rules and regulations, in a safe way. Wastewater treatment has been evolving at different pace along the history, according to the increasing concentration of people in towns and cities. With the increasing pressures on water resources, concerns on how to find new resources capable to help reaching equilibrium within demand and offer arise. In this context, one of the main possibilities to cope with water scarcity is wastewater reclamation and reuse.
International Journal of Economic and Environmental Geology, 2019
Ministry of Agriculture and Water (MAW) in Saudi Arabia had setup very stringent standards for wastewater reuse and discharge (WWRD) in 1989, for example, turbidity and nitrate as nitrogen were not to exceed 1NTU and 10 mg/l respectively. Those limits cannot be met without additional expensive tertiary treatment. Those standards are not needed for all WWRD. In fact, secondary treatment with disinfection and efficient management are adequate for most of WWRD. The author published an article back in 1999 in Water Research Journal, Vol. 33, in which he assessed the standards and recommended setting up less stringent standards as a function of intended reuse and method of irrigation. The standards were re-evaluated and modified by MAW and other ministries in 2003, 2005 and 2006. Unfortunately, the modifications were not to the expected level, and still only a small part of treated wastewater is being used. The remaining portion of wastewater is discharged into a wadi/sea. This article reassessed the standards published in 2003, 2005 and recommended setting up revised standards for reuses and discharges relevant to the intended uses and discharges.
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