In recent years, researchers have investigated a variety of approaches to remove natural
organic matter (NOM) from source water since it has been problematic for water treatment
techniques. NOM is a complex organic matrix which contaminates freshwater bodies and
is the cause of numerous issues in water treatment plants such as membrane fouling, filter
clogging and algal growth. Most importantly, the NOM pool contains disinfection byproduct (DBP) precursors. Even though NOM has no direct adverse health effects, some
DBPs are toxic, and thus, NOM removal is a key part of water treatment.
The coagulation process is one of the generic water treatment methods used to remove
NOM. The primary mechanism of the coagulation process is surface charge neutralisation
which is done by coagulants. Finding the optimal coagulate dose is challenging without
measuring the surface charge. Therefore, this study elaborates a method that monitor the
surface charge, that is streaming potential (SP) measurements. The coagulation process can
be reliably optimised with SP measurements because SP data can be measured in real time.
Therefore, other factors influencing the coagulation process, such as pH, coagulant aids,
temperature and turbidity, can be optimised efficiently with SP measurements. The pH
value plays a critical role in the coagulation process. Suspended NOM changes its surface
according to the variation of the pH value of the solution. The further hydrolysis of
inorganic coagulants depends on the pH value. This study also investigates the effect of
coagulant aid on aggregation. Bentonite and kaolinite clays are applied in the coagulation
process. The results indicate that kaolinite is an effective aid for fast flocculation owing to
its self-aggregation ability, and also it is a non-swelling clay with less surface charge than
bentonite (swelling clay). Further, polyelectrolytes are charged (negatively/positively) and
therefore, they change the total surface charge when added after the primary coagulants.
Thus, the sequential addition of coagulants is important. This study, therefore, suggests that
metal coagulants should be added after adding polyelectrolytes.
So far, a few factors have been identified as being potentially significant in the coagulation
process. The number of suspended particles in source water is another significant factor
that affects the coagulation process. Suspended particles create turbidity in water. Thus,
turbidity is an excellent indicator of suspended particles. However, there is scant literature
on the effect of temperature in the coagulation process. In Australia, the water temperature
changes from 1 °C to 40 °C approximately with seasonal changes. Hence, this study
investigates the coagulation process during temperature variations. The results indicate that
the coagulant dose is proportional to the temperature because the solubility of metalxvii
coagulants (Fe3+) and the surface charge of NOM depends on the temperature. Further, the
results show that floc settling is considerably slow at low temperatures (<10) and high
temperatures (>30). Turbidity removal efficiency was calculated to be 83% at 2 °C and
reduced to 78 % at 40 °C. Thus, the sludge recirculation method is employed with
coagulation in the temperature range of 2 °C- 40 °C. It can be concluded that the sludge
recirculation method improves coagulation-flocculation efficiency, and NOM removal
efficiency improved by more than 20 %. This study also investigated hydraulic conditions
on floc settling, and G is 20.5 s-1 to 28.7 s-1 (40-60 rpm) range is better for faster settling of
flocs formed by NOM coagulation by the dual coagulation system.
The climate is critical in summer in Australia. Due to extreme high-temperature levels,
bushfires occur in many parts of Australia. Bushfires increase the temperature of water
sources, while bushfire residuals leach inorganic and organic materials in water bodies.
This is one of the primary reasons for water pollution. Hence, this study evaluates the
impact of bushfire residuals, including NOM on water pollution and the treatment method
as coagulation. The results show that of the bushfire residuals tested, fly ash had the most
significant impact on water quality: pH increased from 7 to 9, alkalinity increased to 750
mg/L as HCO13−, turbidity increased to 24.5 NTU. Whereas soil that is affected by bushfire
shows fewer pollutants in water than the ash. i.e. heated soil (300 °C) leached organic
matter and showed UV254 absorbance of 0.069, and it was reduced to 0.036 when the soil
that was heated at 600 °C leached in water. Which means, that NOM is absent after
complete oxidation when the soil is burnt at 600 °C.
The literature indicates that the coagulation process has been modified with many
engineered components, including centrifuge coagulation reactors and laminar clarifiers.
However, few researchers have investigated venturi oxidation coupled with the coagulation
process. Therefore, this study attempts to investigate the effects of venturi oxidation on the
coagulation process. The venturi setup injects fine air bubbles into the coagulation reactors.
The study investigates whether the dissolved oxygen level increases rapidly and reaches
saturation level. Additionally, the coagulation system coupled with the venturi setup
effectively removes both suspended and dissolved NOM. Also, Venturi setup provides
good flocculation conditions and thus improves particle collision frequency. As a result,
turbidity and UV254 removal increased to 82% and 87%, respectively, with the venturi
application.