By Nuno Soares and Aldo Estela
Ever since Dr. John Snow established that water could be a mode of transmission for deadly diseases such as cholera in 1854, water disinfection has become a basic requirement in all drinking water treatment processes. Chlorine, the first disinfection chemical discovered in 1774 by the chemist Karl Scheele (Centers for Disease Control and Prevention, 2016), was used for this purpose for the first time in a large scale in 1908, when Dr. John Leal, with the help of George W. Fuller, started the first chlorination facility in the United States for drinking water disinfection (McGuire, 2013). The use of chlorine significantly reduced waterborne diseases all over the western world and also, unfortunately in a much slower way in developing countries. The 2017 report from United Nations Children’s Fund (UNICEF) and World Health Organization (WHO) – Progress on Drinking Water, Sanitation and Hygiene: 2017 Update and SDG Baselines concluded that 2.1 billion people worldwide still lack access to safe readily available water.
Despite treated/safe water being crucial to avoid waterborne diseases, it has been known since the mid-1970s that the process of disinfection produces by-products (DBPs) that can be a hazard to human health. Chloroform and other trihalomethanes were the compounds that created the first concerns in the scientific community (Karlin, 1999).
Since then, other chemicals and techniques for water disinfection have been used in order to kill pathogens in drinking water. For instance, chlorine dioxide, ozone, chloramine, and in some cases combinations of them are being used in modern water treatment systems worldwide. Each one of them, depending on a number of factors, may be derived into DBPs.
The most used association between DBPs and adverse health outcomes is the consumption of chlorinated water and bladder cancer (although children born small for gestational age and miscarriages have also been reported). In a study about water disinfection by-products and bladder cancer, where a pool and a two-stage random-effect meta- analysis of three European case-control studies was conducted, bladder cancer was 47 percent more prevalent among those consuming water with THM4 > 50 μg/L compared to those consuming water with THM4 < 5 μg/L (Mitch, 2018).
DPBs can be categorized into the following groups:
What affects DBPs formation?
DBPs are formed by the reaction of natural organic matter (NOM) or inorganic substances in water (e.g. chloride, bromide) with the disinfectant chemical. This reaction may be affected by pH, temperature, concentration of the precursor or concentration of the disinfectant. The table below summarizes the effects of some of these parameters in the formation of DBPs.
How do you prevent/control the formation of DBPs?
Different methods to control DBPs have been developed. These methods can be preventive or corrective. Preventive methods look for reducing the probability to form DBPs (e.g. reduction of NOM, use of alternative disinfectants, enhanced coagulation, etc.).
Corrective methods are oriented to reduce DBPs that are already formed (e.g. granular activated carbon absorption).
- Enhanced coagulation: Is defined as an optimized coagulation process for removing DBP precursors, or NOM. NOM is measured as total organic carbon (TOC) or dissolver organic carbon (DOC). In general, enhanced coagulation is practiced at a higher coagulant dose and a lower pH. Considering that the process is done at a low pH, we need to consider the alkalinity of water, as it is more difficult to achieve a low pH in high alkalinity source waters. Coagulants that can be used are alum, ferric chloride, ferric sulfate and ferrous sulfate. The dose of coagulants must be established by jar tests and may vary from 9 to 60 mg/L, depending on the TOC of the water source. The conditions that affects TOC removal include alkalinity, pH, turbidity, TOC concentration, origin of NOM, temperature, coagulant dosage and type, peroxidation, mixing, among others, but the operations that greatly affect TOC removal are coagulant type and pH pre-adjustment.
- Carbon adsorption: Carbon adsorption can be used to remove DBP precursors and DBPs. Both granular activated carbon (GAC) and powdered activated carbon (PAC) are used for these applications. Carbon filters must be designed in order to achieve an EBCT (empty bed contact time) of at least 10 minutes, and in some cases EBCT can be as high as 30 minutes. A pilot study is recommended to evaluate carbon adsorption performance.
- Changing chlorination point: Moving back the chlorination point or eliminating pre-chlorination points are two effective ways to control DBP levels in finished waters. Alternatively, a peroxidation step with alternative disinfectants or oxidizers (e.g. potassium permanganate or chlorine dioxide) can be used.
- Use of membrane technologies: Nanofiltration is an extremely effective method for reduction of DBP precursors and, if a proper pre-treatment is applied, ultrafiltration and microfiltration can be effective too. Traditionally, membrane technologies are more used in groundwater treatment systems, but by using a correct pre- and post- treatment, it can be used in surface water.
- Use of alternative disinfectants: Alternative disinfectants include chloramines, ozone, dioxide chloride, and UV.
- Chloramine is a much weaker disinfectant than free chlorine as it requires more contact time for an adequate disinfection and lasts longer in distribution systems. However, chloramine also produces DBPs: cyanogen chloride (or cyanogen bromide in case of high bromide concentration), THMs, and HAAs. The formation of these will depend on the chorine to ammonia ratio.
- Ozone is a stronger disinfectant than free chlorine and it is very effective against microorganisms like Giardiaand Cryptosporidium. It is highly reactive, so it does not provide a long-lasting residual in distribution systems. It reacts with bromide to produce bromate and hypobromous acid that reacts with NOM to produce brominated DBPs. In this case, pH and temperature must be controlled to reduce DBPs formation.
- Chlorine dioxide is a stronger bactericide and viricide with a long-lasting residual in distribution systems. Chlorine dioxide may produce chlorite as a DBP and with the effect of ozone or chlorine it may produce chlorate.
- UV radiation provides a physical method for disinfection and it is very effective against bacteria and viruses. UV does not leave a disinfectant residual so it is normally used with a secondary disinfectant like chlorine, chloramine, or chlorine dioxide.
Carbon adsorption: So far, carbon adsorption is the most common method to reduce DBPs in water once they are already formed.
Granular activated carbon filtration has been used effectively to reduce HAAs and THMs in finished water. The treatment is more effective if biologically active carbon (BAC) is used because biological degradation of HAAs contributes to the reduction of DBPs.
In January’s article, six steps were presented to manage water quality in the food industry. In step 1 – Define sources and purposes, the importance of knowing the characteristics of the water used right from the source is highlighted. This is also essential when you are designing a water treatment process. One thing if for sure, it is very unlikely that it does not generate disinfection by-products. However, treatment conditions can be optimized to reduce their formation in order to provide water that can be consumed safely.
We, food safety professionals, should always embrace preventive and risk-based approaches to hazards. The better you know in detail the quality of the source water, the better you can anticipate, monitor, and manage the formation of DBPs.
Despite all the above and the growing and growing concern regarding the long term health effects of the consumption of water with DBPs, we must always have in mind (specially in countries where safe water is not readily available) that according to the WHO: “Infectious diseases caused by pathogenic bacteria, viruses, protozoa, and helminths are the most common and widespread health risk associated with drinking water.”
Consequently, WHO states: “Where local circumstances require that a choice must be made between meeting either microbiological guidelines or guidelines for disinfectants or disinfectant by-products, the microbiological quality must always take precedence, and where necessary, a chemical guideline value can be adopted corresponding to a higher level of risk. Efficient disinfection must never be compromised.”
About the authors
Nuno Soares is a food engineer who has been working in food industry since 1999. Nuno has worked in roles including quality and production manager. With the goal of reaching further with his ideas for food safety and support other professionals in their daily work, Nuno recently embraced researching and publishing activities. For his PhD, he researched how to improve frozen fish shelf-life and protection by developing a new glazing solution. After publishing his first book Food safety in the Seafood Industry (Wiley), he recently self-published the e-book: ISO 22000:2018 Explained in 25 diagrams.
You can contact Nuno on LinkedIn or at email@example.com.
Aldo Estela has more than 10 years of experience in quality and food safety management in the food and beverages industry. He is currently the global head of quality at AJE Group, a multinational beverage company with presence in 21 countries of Latin America, Asia, and Africa. Previously, he worked in the flexible packaging industry at Amcor Flexibles and in the nutritional lipids industry at DSM.
He holds a Bachelor degree in Chemistry from National University of Engineering in Peru, a Masters degree in Business Administration from Pontifical Catholic University of Peru, and a Master degree in International Leadership from EADA Business School in Spain. He currently lives in Lima, Peru.