35 Ill. Adm. Code 6110.611.532
Unfiltered PWSs
Section 611
TITLE 35: ENVIRONMENTAL PROTECTION
SUBTITLE F: PUBLIC WATER SUPPLIES
CHAPTER I: POLLUTION CONTROL BOARD
PART 611 PRIMARY DRINKING WATER STANDARDS
SECTION 611.532 UNFILTERED PWSS
Section 611.532 Unfiltered
PWSs
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 = CT
calc
/CT
99.9
ii) Add
the Ai values:
B = ∑(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:
PI
=
100
-
100
10
3B
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.
BOARD NOTE: This
Section derives from 40 CFR 141.74(b).