Precursor removal
Through coagulation and filtration, for example.
Chlorine disinfection can produce disinfection byproducts (DBPs) when chlorine reacts with organic material in water, such as algae, river weeds, and decaying leaves — an effect often more pronounced in warm weather.
Of the identified DBPs, the two classes of greatest concern are trihalomethanes (THMs) and haloacetic acids (HAAs) — typically tasteless and odorless, but suspected human carcinogens. The quantity formed depends on several factors, including the amount and type of organic material present, its composition and structure, temperature, pH, chlorine dosage, contact time, and bromide concentration — meaning the optimal DBP-minimization strategy generally requires bench and pilot testing along with some trial and error.
Because the full range of DBPs formed from chlorine’s reaction with organic matter isn’t fully understood, THMs have become the standard indicator used to represent all potentially harmful compounds formed through chlorination.
The EPA’s Stage 2 Disinfectants/Disinfection Byproducts Rule sets MCLs of 80 μg/L for four THMs (chloroform, bromodichloromethane, dibromochloromethane, and bromoform) and 60 μg/L for five HAAs, based on a locational running annual average rather than a system-wide average.
Because residual chlorine allows THM formation to continue within the distribution system, sampling sites are chosen where DBP and THM formation potential is greatest.
THM formation from water chlorination was first identified in the 1970s, and THMs are considered carcinogenic environmental pollutants. Studies of populations drinking chlorinated water — where chloroform is the predominant THM — have consistently shown small increases in rectal, colon, and bladder cancer incidence, with the strongest evidence for bladder cancer. Among people who take hot showers and baths, inhalation and dermal absorption during bathing account for greater THM exposure than drinking water itself.
Effective THM treatment requires identifying the right combination of approaches — removing organic precursors, removing THMs after formation, or a combination of both, along with optimized chlorination. Each situation calls for case-by-case evaluation through a well-executed pilot study.
Through coagulation and filtration, for example.
Removing THMs after they have formed.
To minimize THM formation downstream.
Our ability to conduct pilot studies quickly and cost-effectively is a clear differentiator for our company. We mobilize our pilot study team to test a slipstream of your water, evaluating precursor removal (through coagulation and filtration, for example), THM removal by air stripping, and chlorination optimization to minimize THM formation downstream.
Our pilot study report guides the design of a customized solution and supports TCEQ approval documentation. WETS has successfully installed more than a dozen THM treatment systems to date.
Another approach to THM contamination is switching from chlorine to chloramine (chlorine plus ammonia) disinfection, which is less aggressive toward organic precursors — though also less effective as a bactericide, viricide, and taste/odor oxidizer, so care is needed when converting a chlorination system to chloramination.
Water storage tank aeration has been used to address THM contamination, but WETS rarely recommends it as the best option — providing adequate air/water contact surface area is far more effective with a packed tower aerator and inlet spray system than with storage tank aeration alone.
Whether you want a new water treatment system installed, need your current one inspected and repaired, or just want a free quote, contact the WETS LLC. With years of experience in the industry, our skilled team members are trained and knowledgeable with a variety of leading water equipment and products. Our certified water purification experts are here to help.
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