One of the more popular proprietary toxicants utilized in
industrial water applications is 5-chloro-2-methyl-4-isothiazolin-3-one which
makes use of a blend of two specific isomers. This material
has gained widespread acceptance because of its effectiveness on a broad
spectrum of microbes in a wide variety of water types.
Bacteria obtain their energy from a complex series of
oxidation-reduction reactions which are catalyzed by proteins called enzymes.
There is a specific enzyme for each reaction in this complex series. Any
disruption of this sequence will result in cell death. In addition, other
cellular proteins serve as a source for the essential amino acids necessary for
life. Almost all proteins possess covalent disulfide bonds as part of their
structure. The active isothiazolone molecule cleaves this disulfide linkage and
denatures the protein. Denaturation inactivates the enzymes and cellular
proteins essential for metabolism causing death to the organism (Figure 5-28).
Isothiazolone is effective against bacteria (including
sulfate-reducers), fungi and algae. This is not always the case with many
products because of the manner in which they function. For instance, a product
that kills an organism by tying up an essential metabolite will function only on
specific organisms. Such a product will be ineffective on an organism that does
not require that metabolite.
Isothiazolone has the added benefit of retaining its effectiveness across the
spectrum of pH values normally encountered in industrial water systems and is
not hindered in any way by waters high in dissolved or suspended solids, oil
contamination or nitrogen-bearing compounds.
The one situation that should be avoided when using this toxicant is waters
high in sulfide concentration. Since the primary mode of microbiocidal action is
the tying up of disulfide linkages present in the cell, isothiazolone will be
consumed by high levels of sulfide and not be available for microbe control.
Environmental characteristics of isothiazolone are also quite attractive with
degradation of the toxicant from the discharge stream occurring via a number of
pathways, including hydrolysis, biodegradability and photolytic breakdown.