Abstract:
Waterborne diseases are still common in developing countries as drinking water sources
are contaminated and feasible means to reliably treat and disinfect these water sources
are not available. Many of these developing countries are in the tropical regions of the
world where sunlight is plentiful. The objective of this study was to optimize solar
disinfection system for household water treatment. An experimental study was carried out
from April1 to June7, 2011 at the laboratory of Environmental Health Sciences and
Technology, Jimma University. Inactivation of microbes was tested at different water and
environmental conditions (turbidity, pH, water depth, dissolved oxygen concentration,
water temperature, container type, color of container, solar intensity) using fecal
coliform as test organism. Optimization of solar disinfection (SODIS) system was done by
testing the efficiency of SODIS at optimized conditions (at turbidity of 2NTU, pH 7,
dissolved oxygen concentration of 6.52mg/L, half-surfaced black colored PET bottle, and
water depth of 10 cm ). Fecal coliform enumeration was performed by pour plate method.
The results showed that complete fecal coliform inactivation was found on clear water
samples having 2nephlometric turbidity unit (NTU) with six hour exposure time. On the
contrary, complete inactivation was not found for a water sample having turbidity of
13NTU. Statistically significant difference on the rate of fecal coliform inactivation was
not found on water samples having different pH value in the range of 5.5 to 9 (p=0.05).
Depth of water has shown significant impact on inactivation of fecal coliform (p=0.015).
After 3 hour of exposure time, higher log inactivation (2.91±0.001) was found on water
depth of 5.5 cm and the least log inactivation (0.474±0.044) was found on water depth of
10 cm. Higher log inactivation (0.79±0.03) was found on colorless Polyethylene
terephthalate (PET) bottle and the least log inactivation (0.16±0.03) was found on black
colored PET bottles. Aerating raw water samples prior to exposure enhanced the
inactivation rate by a factor of 2.2 even if the difference was not statistically significant
(p=0.05). Exposing raw water under half-surfaced black colored PET bottle has shown
significant increment on the rate of fecal coliform inactivation. Place of bottle exposure
didn’t show statistically significant effect on SODIS. Intensity of light has also shown
significant effect on the rate fecal coliform inactivation. After 3 hour of exposure,
1.65±0.05, 0.95±0.03 and 0.2±0.01 log inactivation was observed on raw water
II
samples exposed to sunlight having a cumulative solar irradiance of 3.99kWh/m2
,
2.77kWh/m2
and 0.6026kWh/m2
respectively. Complete microbial inactivation was
observed within exposure time of 3 to 4.5 hour, on raw water samples having
820CFU/mL under optimized conditions for water disinfection. Bacterial re-growth was
not observed after solar disinfection, confirming that the inactivation was irreversible.
The results demonstrated that under optimized conditions for water (at turbidity of
2NTU, pH 7, dissolved oxygen concentration of 6.52mg/L, half-surfaced black colored
PET bottle, and water depth of 10 cm ). Complete fecal coliform inactivation can be
achieved within an exposure time of less than four hour in all parts of the world which
are receiving solar irradiance of 3.99kWh/m2
and above