Clean water is a very important basic human need. However, the process of treating water to make it safe for consumption is not simple. One of the main challenges in water treatment is the emergence of disinfection byproducts (DBPs). This article will take an in-depth look at DBPs, from the history of their discovery, their formation process, their impact on health, to methods of controlling them in modern water treatment systems.
The discovery of DBPs was an important turning point in the water treatment industry. In the 1970s, scientists began identifying chlorinated organic compounds in drinking water in New Orleans. This discovery sparked public concern and led to the passage of the Safe Drinking Water Act in 1974 in the United States. This act laid the foundation for further research on DBPs and their impact on human health.
Thomas Bellar, a chemist from the US Environmental Protection Agency (EPA), played a key role in the early research of DBPs. Bellar developed the "purge and trap" method for measuring volatile organic contaminants in water. This breakthrough allowed researchers to detect the presence of chloroform and other DBPs compounds in various drinking water sources.
In mid-1973, Bellar sampled various drinking water sources and found that DBPs were closely associated with chlorination points in the water treatment process. Chloroform concentrations were found in the Ohio River, coagulation processes using alum, and water treatment plant effluents. These findings confirm that DBPs are formed during the water treatment process, particularly during disinfection using chlorine.
DBPs are formed when disinfectants such as chlorine react with natural organic matter (NOM) present in water. NOM can come from a variety of sources, including decaying leaves, algae, and other organic matter dissolved in water. When chlorine or other disinfectants are added to water containing NOM, a complex chemical reaction occurs, producing various DBPs.
Trihalomethanes (THMs) and haloacetic acids (HAAs) are the two main groups of DBPs that have been most studied. THMs include compounds such as chloroform, bromodichloromethanes, dibromochloromethanes, and bromoform. Meanwhile, HAAs include compounds such as dichloroacetic acid and trichloroacetic acid. In addition, there are also other groups of DBPs such as halonitromethanes, haloketones, and N-nitrosodimethylamine (NDMA).
Factors that influence the formation of DBPs include:
Understanding of these factors is critical in efforts to control the formation of DBPs in water treatment systems.
While water disinfection is essential to prevent waterborne diseases, the presence of DBPs poses a new dilemma in the water treatment industry. Several epidemiological and toxicological studies have linked long-term exposure to DBPs with various health risks, including:
However, it is important to note that the cause-and-effect relationship between DBPs and these health effects is still the subject of scientific research and debate. The risks associated with DBPs should be considered in the context of the far greater benefits of water disinfection in preventing infectious diseases.
As awareness of the potential risks of DBPs increases, regulatory agencies in various countries have established standards and regulations to limit the concentration of DBPs in drinking water. In the United States, the EPA has established Maximum Contaminant Levels (MCLs) for various DBPs through the Stage 1 and Stage 2 Disinfectants and Disinfection Byproducts Rules.
Some of the key standards for DBPs in the US include:
In Indonesia, the Minister of Health Regulation No. 492/MENKES/PER/IV/2010 on Drinking Water Quality Requirements also sets the maximum THMs limit at 100 μg/L.
In addition to setting the maximum limit, the regulation also sets the maximum THMs limit at 100 μg/L.
In addition to setting maximum limits, the regulation also encourages the use of treatment techniques that can reduce the formation of DBPs, such as enhanced coagulation and removal of DBPs precursors.
The water treatment industry has developed various strategies to control the formation of DBPs while still ensuring effective disinfection. Some of the main approaches include:
The choice of an appropriate strategy depends on raw water characteristics, existing infrastructure, and economic considerations. Often, a combination of several methods is required to achieve optimal results.
While large-scale water treatment plants have more options for controlling DBPs, residential water treatment systems face unique challenges. Many households use a combination of municipal water and well water, each of which has different characteristics and potential contaminants.
For systems using municipal water and well water, each has different characteristics and potential contaminants.
For systems using well water, common issues include iron, manganese, and potential bacterial contamination from septic tanks. Municipal water, even if treated, may still contain DBPs or their precursors. Some approaches that may be considered for residential systems include:
It is important to note that while many people dislike the smell of chlorine in water, it is actually an indicator that the water has been properly disinfected. Consumer education about the importance of disinfection and the relative risk of DBPs is essential.
Research on DBPs continues to grow, with a focus on identifying new DBPs, better understanding their formation mechanisms, and developing more effective treatment technologies. Some promising areas of innovation include:
In addition, there is a growing trend towards a more holistic approach in water quality management, which considers not only DBPs but also other emerging contaminants, such as microplastics and per- and polyfluoroalkyl compounds (PFAS)
.Disinfection byproducts represent a complex challenge in water treatment that requires a balanced approach between the need for effective disinfection and the minimization of long-term health risks. A better understanding of the formation of DBPs, their impact on health, and control strategies has changed the way the water industry approaches the treatment process.
Disinfection byproducts are a complex challenge in water treatment.
While DBPs are a cause for concern, it is important to remember that the risk from non-disinfected waterborne diseases is much greater and more direct. Therefore, the focus should be on optimizing the water treatment process to minimize the formation of DBPs while still ensuring adequate disinfection.
For consumers, an understanding of the sources of DBPs is important.
For consumers, an understanding of their water source and selection of an appropriate treatment system is essential. The use of high quality products such as Pentair Pentek cartridge filters or RO systems such as Pentair Merlin can help reduce exposure to DBPs at the household level.
With the continued development of research and development in water treatment processes, it is important to minimize the formation of DBPs.
With the continued development of research and technology, we can look forward to more effective and efficient solutions to the challenge of DBPs in the future. Collaboration between researchers, regulators, the water treatment industry, and communities will be key in ensuring a safe and sustainable drinking water supply for generations to come.
Packaged drinking water is not always free of DBPs. Although many manufacturers use advanced treatment methods such as reverse osmosis and ozonation, some may still use chlorine in their production process. In addition, if the raw water used contains precursors of DBPs, there is a possibility of DBPs forming even in small amounts. Consumers are advised to check the treatment information on the label or contact the manufacturer for more information.
To determine the content of DBPs in household water, you can take a few steps:
Boiling water is not effective for removing most DBPs. Instead, boiling water may increase the concentration of some DBPs due to water evaporation. Some volatile DBPs such as THMs may decrease slightly due to evaporation, but other non-volatile DBPs will remain or even become more concentrated. More effective methods to reduce DBPs include the use of activated carbon filters or reverse osmosis systems.
1. Hendricks, David W. "Fundamentals of Water Treatment Unit Processes: Physical, Chemical, and Biological", pp. 81-82. This passage provides a comprehensive summary of the issue of disinfection by-products (DBPs) in water treatment, including their history, research, and impact on the drinking water industry.
2. Binnie, Chris and Kimber, Martin. "Basic Water Treatment (5th Edition)", pp. 79. This source mentions several key terms related to DBPs such as DBP precursors, total organic carbon (TOC), enhanced coagulation, USEPA treatment techniques, MIEX, SIX, Cryptosporidium, and Giardia.
3. US Environmental Protection Agency (EPA). "Stage 1 and Stage 2 Disinfectants and Disinfection Byproducts Rules". This document sets standards and regulations to limit the concentration of DBPs in drinking water in the United States.
4. Regulation of the Minister of Health of the Republic of Indonesia Number 492/MENKES/PER/IV/2010 on Drinking Water Quality Requirements. This regulation sets the maximum limit of THMs in drinking water in Indonesia.
5. World Health Organization (WHO). "Guidelines for Drinking-water Quality, 4th edition". This document provides international guidance on drinking water quality standards, including recommendations related to DBPs.