Trihalomethanes (THMs) are produced during the chlorination of water. The 4 regulated and most commonly occurring THMs are
• chloroform (CHCl3),
• bromodichloromethane (CHBrCl2),
• dibromochloromethane (CHBr2Cl), and
• bromoform (CHBr3).
Additional chlorination byproducts can be formed (including haloacetic acids and halonitriles; for example, see 5710 D) during the relatively slow organic reactions that occur between free chlorine and naturally occurring organic precursors such as humic and fulvic acids. The formation potentials of these additional byproducts also can be determined, but different quenching agents and different analytical procedures may be needed. Predictive models for estimating and calculating THM formation exist, but because eventual THM concentrations cannot be calculated precisely from conventional analyses, methods to determine the potential for forming THMs are useful in evaluating water treatment processes or water sources or for predicting THM concentrations in a distribution system.
To obtain reproducible and meaningful results, control such variables as temperature, reaction time, chlorine dose and residual, and pH. The formation of THM is enhanced by elevated temperatures and alkaline pH and by increasing concentrations of free chlorine residuals, although THM formation tends to level off at free chlorine residuals of 3 mg/L and above; a longer reaction time generally increases THM formation.1,2
Low concentrations of bromide exist in most natural waters and are responsible for the formation of brominated organic compounds. Figure 5710:1 shows that an oxidant ratio of about 40 times more chlorine than bromine (on a molar basis, = 40 on the x axis) is required to form equimolar amounts of substituted organic chloride and bromide (= 1 on the y axis). Small amounts of bromide also can increase the molar yield of THMs.3
The possible addition of organic precursors contained in reagent solutions cannot be accounted for accurately without a great deal of extra work; therefore, sample dilutions resulting from reagent additions (approximately 2%) are ignored in the final calculations. However, the sample dilution may need to be taken into account if other volumes are used. A sample’s dilution also changes the concentrations of bromide and organic matter, potentially leading to speciation changes.