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Results
and Discussion
Water used in
flushing activities.
Prior to polyphosphate-blend addition, flushing typically
required 20 to 30 acre- ft/month, and occasionally, as much
as 65 acre-ft/month. Following polyphosphate-blend addition
that began June 1999, the required flushing volume dropped
to 2 to 3 acre-ft; three years later, it has fallen as low
as 0 to 1 acre-ft/month.
A crew of two to three people flushed the area as frequently
as twice per week. In general, flushing was done until water
quality goals were met.
Customer Complaints.
One of the primary goals of the polyphosphate-blend addition
was to reduce the number of customer complaints. During the
summer of 1998, the number of complaints was as high as 35
per month. Because of its color-sequestering ability, the
polyphosphate-blend addition had an immediate impact, reducing
the number of complaints to fewer than five per month. The
number of complaints has consistently, remained fewer than
five per month, including a number of summer months in which
zero complaints were received ((Figure 1).
Total
chlorine residuals.
Total chlorine
residual was monitored in the field, using pocket colorimeters
with DPD-method procedures to determine if the District goal
to maintain a total chlorine residual greater than 1.0 mg/L
was being met. Prior to the addition of the polyphosphate-blend,
as few as 30 percent of monthly samples had a measured chlorine
residual greater than 1.0 mg/L. Approximately six months later,
90 to 100 percent of the residuals in the study area were
greater than 1.0 mg/L. Also, less water was used in flushing
to achieve the goal.
HPC bacteriological analyses.
HPC levels, which are the main indicator of bacterial activity
in the study area, also decreased significantly following
the addition of polyphosphate-blend. However, it took almost
two years for the level to consistently remain below 100 colony
forming Units/mL, which is the District goal. We suspect that
initially the polyphosphate-blend agent dissolves the corrosion
product-biofilm matrix on the pipe wall, resulting in higher
HPC levels. Throughout the study period, all bacteriological
samples were absent of coliform bacteria.
For this system, a minimum of two years of polyphosphate-blend
addition is required to establish low HPC levels. The length
of time following polyphosphate-blend addition required to
reduce HPC levels depends on the type and age of the water
mains and characteristics of the biofilms and corrosion products.
Newer systems, which may contain thinner biofilms or fewer
corrosion by-products, may be able to reduce HPC concentrations
in less time. Older systems that have unlined cast-iron and
steel water mains with firmly established biofilms may require
longer than two years (Figure 2).
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