If the Agency determines that filtration is required, it must
specify alternative monitoring requirements, as appropriate, until filtration
is in place. A supplier using a groundwater source under the direct influence
of surface water not providing filtration treatment must monitor as the Agency
directs in a SEP after determining under Section
611.212 that the supplier's
groundwater source is under the direct influence of surface water, requiring
the supplier to install and apply filtration treatment, and specifying
appropriate monitoring requirements until filtration is in place.
a) The supplier must sample and analyze for
fecal coliform or total coliform as Section
611.231(a)
requires on representative source water samples it collects immediately prior
to the first or only point of applying disinfectant. The supplier must sample
for fecal or total coliforms no less frequently than Table B specifies each
week the supplier serves water to the public. The supplier must also sample and
analyze once for fecal or total coliform density every day the supplier serves
water to the public and the turbidity of its source water exceeds 1 NTU (these
samples count towards the weekly coliform sampling requirement), unless the
Agency issues a SEP determining that the supplier cannot analyze within 30
hours after collecting the sample for logistical reasons outside the supplier's
control.
b) The supplier must
measure turbidity as Section
611.231(b)
requires on representative grab samples of source water it collects immediately
prior to the first or only point of applying disinfectant no less frequently
than every four hours when the supplier serves water to the public. A supplier
may substitute continuous turbidity monitoring for grab sample monitoring after
validating the accuracy of regular the continuous measurement for accuracy
using a protocol the Agency approved in a SEP.
c) The supplier must determine its total
inactivation ratio for each day it operates based on the appropriate
CT
99.9
values in
Appendix B. The supplier must monitor the parameters necessary to determine its
total inactivation ratio using specific procedures:
1) The supplier must measure temperature of
the disinfected water at least once per day at each RDC sampling
point.
2) If using chlorine, the
supplier must measure the pH of the disinfected water at least once per day at
each chlorine RDC sampling point.
3) The supplier must determine the
disinfectant contact times ("T") for each day during peak hourly
flow.
4) The supplier must measure
the RDCs ("C") of the water before or at the first customer each day during
peak hourly flow.
5) A supplier
using a disinfectant other than chlorine may monitor by other Agency-approved
methods under Section
611.241(a).
d) The supplier must calculate
total inactivation ratio using a specific procedure:
1) A supplier applying disinfectant at only
one point may determine the total inactivation ratio based on either of two
methods:
A) Determining one inactivation ratio
(Ai=CT
calc/CT
99.9) before or at
the first customer during peak hourly flow, so that the supplier achieves
99.9 percent Giardia lamblia
inactivation if the Ai is greater than
1.0; or
B) The supplier may determine successive Ai
values at points between where the supplier applies disinfectant and before or
at the first customer, representing sequential inactivation ratios, during peak
hourly flow. Under this alternative, the supplier must use a specific method to
calculate the total inactivation ratio:
i)
Determine Ai for each sequence:
Ai =
CTcalc/CT99.9
ii) Add the Ai values:
B = [SIGMA](Ai)
iii) If B is greater than 1.0, the supplier
achieved the required
99.9 percent Giardia lamblia
inactivation.
2) A supplier applying disinfectant at more
than one point before or at the first customer must determine the CT value of
each disinfection sequence immediately prior to the next point it applies
disinfectant during peak hourly flow. The supplier must calculate the Ai value
of each sequence and B using the method in subsection (d)(1)(B) to determine if
the supplier complies with Section 611.241.
3) A supplier monitoring RDC at one or more
points may voluntarily calculate its total percent inactivation (PI) may using
the equation:
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e) The supplier must continuously monitor the
RDC of the water entering its distribution system and record the lowest value
each day, except that the supplier may use grab sampling every four hours for
no more than five days in lieu of continuous monitoring after a failure of the
continuous monitoring equipment. A supplier serving 3,300 or fewer persons may
take grab samples on an ongoing basis at the applicable frequency in Table C in
lieu of continuous monitoring. If the RDC falls below
0.2 mg/L in a system using grab
sampling in lieu of continuous monitoring, the supplier must take a grab sample
every four hours until its RDC is equal to or greater than
0.2 mg/L.
f) Measuring Points
1) The supplier must measure the RDC at the
same points in its distribution system and at the same time it samples total
coliforms, as Sections
611.1054 through
611.1058 specify. The Agency
must allow a supplier using both a groundwater source and a surface water
source or groundwater source under direct influence of surface water to take
disinfectant residual samples at points other than the total coliform sampling
points if the Agency issues a SEP determining that those points better
represent treated (disinfected) water quality within the distribution system.
The supplier may measure HPC in lieu of RDC.
2) If the Agency determines under Section
611.213 that a supplier has no
means for having a sample analyzed for HPC as subsection (a) specifies, the
subsection (f)(1) does not apply.