Code of Massachusetts Regulations
310 CMR - DEPARTMENT OF ENVIRONMENTAL PROTECTION
Title 310 CMR 22.00 - Drinking Water
Section 22.20F - Long Term 1 Enhanced Surface Water Treatment Rule
Universal Citation: 310 CMR 22.00 MA Code of Regs 22.20F
Current through Register 1531, September 27, 2024
(1) General Requirements.
(a) 310 CMR 22.20F
establishes requirements for filtration and disinfection that are in addition
to criteria under 310 CMR 22.20A. The requirements of 310 CMR 22.20F apply to
public water systems serving fewer than 10,000 people using a surface water
source or ground water source under the direct influence of surface water,
beginning January 1, 2005 unless otherwise specified. 310 CMR 22.20F
establishes or extends treatment technique requirements in
lieu of maximum contaminant levels for the following
contaminants:
1.
Giardia
lamblia;
2.
Viruses;
3. Heterotrophic plate
count bacteria;
4.
Legionella;
5.
Cryptosporidium; and
6. Turbidity.
(b) Each supplier of water serving fewer than
10,000 people using a surface water source or ground water source under the
direct influence of surface water shall provide treatment of its source water
that complies with the treatment technique requirements set forth in 310 CMR
22.20F in addition to the requirements identified in 310 CMR 22.20A. The
treatment technique requirements set out in 310 CMR 22.20F consist of
installing and properly operating water treatment processes that reliably
achieve:
1. At least 99% (2-log) removal of
Cryptosporidium between a point where water is not subject to
recontamination by surface water runoff and a point downstream before or at the
first customer for filtered systems, or Cryptosporidium
control under the watershed control plan for unfiltered systems.
2. Compliance with the profiling and
benchmark requirements in 310 CMR 22.20F(4)(a) through (5)(e).
(c) A public water system subject
to the requirements of 310 CMR 22.20F shall also meet the following
requirements:
1. It shall cover any finished
water reservoir that started construction on or after March 15, 2002 as
described in 310 CMR 22.20F(2)(a) and (b).
2. If it is an unfiltered system, it shall
comply with the updated watershed control requirements described in 310 CMR
22.20F(3)(a) through (c).
3. If it
is a community or non-transient non-community water systems, it shall develop a
disinfection profile as described in 310 CMR 22.20F(4)(a) through
(g).
4. If it is considering making
a significant change to its disinfection practices, it shall develop a
disinfection benchmark and consult with the Department for approval of the
change as described in 310 CMR 22.20F(5)(a) through (e).
5. If it is a filtered system, it shall
comply with the combined filter effluent requirements as described in 310 CMR
22.20F(6)(a) through (d).
6. If it
is a filtered system that uses conventional or direct filtration, it shall
comply with the individual filter turbidity requirements as described in 310
CMR 22.20F(7)(a) through (e).
7. It
shall comply with the applicable reporting and record keeping requirements as
described in 310 CMR 22.20F(8)(a) and (b).
(2) Finished Water Reservoirs.
(a) Each supplier of
water serving fewer than 10,000 people using a surface water source or ground
water source under the direct influence of surface water is subject to 310 CMR
22.20F(2)(b).
(b) If the supplier
of water begins construction of a finished water reservoir on or after March
15, 2002 the reservoir shall be covered. Finished water reservoirs for which
the supplier of water began construction prior to March 15, 2002 are not
subject to 310 CMR 22.20F(2), but are subject to 310 CMR 22.20A.
(3) Additional Watershed Control Requirements for Unfiltered Systems.
(a) Each supplier of water serving fewer than
10,000 people using a surface water source or ground water source under the
direct influence of surface water which does not provide filtration shall
continue to comply with all of the filtration avoidance criteria in 310 CMR
22.20A(2), as well as the additional watershed control requirements in 310 CMR
22.20F(3)(b).
(b) The supplier of
water must take any additional steps necessary to minimize the potential for
contamination by Cryptosporidium oocysts in the source water.
The supplier of water's watershed control program shall, for
Cryptosporidium:
1. Identify
watershed characteristics and activities which may have an adverse effect on
source water quality; and
2.
Monitor the occurrence of activities, which may have an adverse effect on
source water quality.
(c) During an onsite inspection conducted
under the provisions of 310 CMR 22.20A(2)(b)5., the Department will determine
whether the watershed control program is adequate to limit potential
contamination by Cryptosporidium oocysts. The adequacy of the
program will be based on the comprehensiveness of the watershed review; the
effectiveness of the program to monitor and control detrimental activities
occurring in the watershed; and the extent to which the supplier of water has
maximized land ownership and/or controlled land use within the
watershed.
(4) Disinfection Profiling.
(a) Each supplier of water, community or
non-transient non-community water system, serving fewer than 10,000 people
using a surface water source or ground water source under the direct influence
of surface water shall develop a disinfection profile unless the Department
determines that the system's profile is unnecessary. The Department may approve
the use of a more representative data set for disinfection profiling than the
data set required in 310 CMR 22.20F(4)(c) through (g).
(b) The Department may only determine that a
system's profile is unnecessary if a system's TTHM and HAA5 levels are below
0.064 mg/L and 0.048 mg/L, respectively. To determine these levels, TTHM and
HAA5 samples must be collected after January 1, 1998, during the month with the
warmest water temperature, and at the point of maximum residence time in the
distribution system.
(c) A
disinfection profile shall be developed using the following three steps:
1. The supplier of water shall collect data
for several parameters from the plant as required in 310 CMR 22.20F(4)(d) over
the course of 12 months. If the system serves between 500 and 9,999 persons the
supplier of water must begin to collect data no later than July 1, 2003. If the
system serves fewer than 500 persons the supplier of water must begin to
collect data no later than January 1, 2004;
2. The supplier of water shall use the data
to calculate weekly log inactivation as required in 310 CMR 22.20F(4)(e) and
(f); and
3. The supplier of water
shall use these weekly log inactivations to develop a disinfection profile as
specified in 310 CMR 22.20F(4)(g).
(d) The supplier of water shall monitor the
following parameters to determine the total log inactivation using the
analytical methods in 310 CMR 22.20A(5)(a), once per week on the same calendar
day, over 12 consecutive months:
1. The
temperature of the disinfected water at each residual disinfectant
concentration sampling point during peak hourly flow;
2. If the system uses chlorine, the pH of the
disinfected water at each residual disinfectant concentration sampling point
during peak hourly flow;
3. The
disinfectant contact time(s) ("T") during peak hourly flow; and
4. The residual disinfectant concentration(s)
("C") of the water before or at the first customer and prior to each additional
point of disinfection during peak hourly flow.
(e) Use the tables in 310 CMR
22.20A(5)(b)3.e. to determine the appropriate CT99.9
value. The supplier of water shall calculate the total inactivation ratio as
follows, and multiply the value by 3.0 to determine the log inactivation of
Giardia lamblia:
1. If the
supplier of water uses only one point of disinfectant application, the supplier
of water shall determine the total inactivation ratio for the disinfection
segment based on either of the following methods:
a. Determine one inactivation ratio
(CTcalc/CT99.9) before or at the first customer during
peak hourly flow; or
b. Determine
successive CTcalc/CT99.9 values, representing sequential
inactivation ratios, between the point of disinfectant application and a point
before or at the first customer during peak hourly flow. Under this
alternative, the system must calculate the total inactivation ratio by
determining (CTcalc/CT99.9) for each sequence and then
add the (CTcalc/CT99.9) values together to determine
(3CTcalc/CT99.9).
2. If the supplier of water uses more than
one point of disinfectant application before the first customer, the supplier
of water shall determine the (CTcalc/CT99.9) value of
each disinfection segment immediately prior to the next point of disinfectant
application, or for the final segment, before or at the first customer, during
peak hourly flow using the procedure specified in 310 CMR
22.20F(4)(e)1.b.
(f) If
the supplier of water uses chloramines, ozone, or chlorine dioxide for primary
disinfection, the supplier of water shall also calculate the logs of
inactivation for Viruses and develop an additional disinfection profile for
Viruses using methods approved by the Department.
(g) Each supplier of water will use each log
inactivation as a data point in the disinfection profile. The supplier of water
will have obtained 52 measurements (one for every week of the year). This will
allow the supplier of water and the Department the opportunity to evaluate how
microbial inactivation varied over the course of the year by looking at all 52
measurements (the Disinfection Profile). The supplier of water shall retain the
Disinfection Profile data in graphic form, such as a spreadsheet, which must be
available for review by the Department as part of a sanitary survey. The
supplier of water shall use this data to calculate a benchmark if they are
considering changes to disinfection practices.
(5) Disinfection Benchmark.
(a) A supplier of
water serving fewer than 10,000 people using a surface water source or ground
water source under the direct influence of surface water required to develop a
disinfection profile under 310 CMR 22.20F(4), shall develop a Disinfection
Benchmark if the supplier of water decides to make a significant change to the
disinfection practice. The supplier of water shall consult with the Department
for approval before implementing a significant disinfection practice
change.
(b) Significant changes to
disinfection practice include:
1. Changes to
the point of disinfection;
2.
Changes to the disinfectant(s) used in the treatment plant;
3. Changes to the disinfection process;
or
4. Any other modification
identified by the Department.
(c) If the supplier of water is considering a
significant change to its disinfection practice, the supplier of water shall
calculate a disinfection benchmark(s) as described in 310 CMR 22.20F(5)(d) and
(e) and provide the benchmark(s) to the Department. The supplier of water may
only make a significant disinfection practice change after consulting with and
obtaining the approval of the Department. The system shall submit the following
information to the Department as part of the consultation and approval process:
1. A description of the proposed
change,
2. The disinfection profile
for Giardia lamblia (and, if necessary, Viruses) and
disinfection benchmark,
3. An
analysis of how the proposed change will affect the current levels of
disinfection, and
4. Any additional
information requested by the Department.
(d) If the supplier of water is making a
significant change to its disinfection practice, the supplier of water shall
calculate a disinfection benchmark using the following procedure:
1. Using the data the supplier of water
collected to develop the Disinfection Profile, determine the average
Giardia lamblia inactivation for each calendar month by
dividing the sum of all Giardia lamblia inactivations for that
month by the number of values calculated for that month.
2. Determine the lowest monthly average value
out of the twelve values. This value becomes the disinfection
benchmark.
(e) If the
supplier of water uses chloramines, ozone or chlorine dioxide for primary
disinfection, the supplier of water shall calculate the disinfection benchmark
from the data the system collected for Viruses to develop the disinfection
profile in addition to the Giardia lamblia disinfection
benchmark calculated under 310 CMR 22.20F(5)(d). This viral benchmark shall be
calculated in the same manner used to calculate the Giardia lamblia
disinfection benchmark in 310 CMR 22.20F(5)(d).
(6) Combined Filter Effluent Requirements.
(a) Each supplier
of water that serves fewer than 10,000 people using a surface water source or
ground water source under the direct influence of surface water is required to
filter, and each supplier of water that utilizes filtration other than slow
sand filtration or diatomaceous earth filtration shall meet the combined filter
effluent (CFE) turbidity requirements of 310 CMR 22.20F(6)(b) through (d). If
the supplier of water uses slow sand or diatomaceous earth filtration the
supplier of water is not required to meet the CFE turbidity limits of 310 CMR
22.20F, but such supplier of water shall continue to meet the CFE turbidity
limits in 310 CMR 22.20A(4).
(b)
Each supplier of water that serves fewer than 10,000 people using a surface
water source or ground water source under the direct influence of surface water
is required to filter, and each supplier of water that utilizes filtration
other than slow sand filtration or diatomaceous earth filtration shall meet two
strengthened CFE turbidity limits as follows:
1. The first CFE turbidity limit is a
"95th percentile" turbidity limit that the system
shall meet in at least 95% of the turbidity measurements taken each month.
Measurements must continue to be taken as described in 310 CMR 22.20A(5)(b)1.
and 3. Monthly reporting shall be completed according to 310 CMR 22.20F(8).
a. If the supplier of water uses conventional
filtration or direct filtration, the turbidity level of representative samples
of a system's filtered water shall be less than or equal to 0.3 NTU in at least
95% of the measurements taken each month, measured as specified in 310 CMR
22.20A(5)(a) and (c).
b. If the
supplier of water uses "alternative filtration" the turbidity level of
representative samples of the system's filtered water shall be less than or
equal to 0.3 NTU in at least 95% of the measurements taken each month, measured
as specified in 310 CMR 22.20A(5)(a) and (c).
2. The second CFE turbidity limit is a
"maximum" turbidity limit that the system may not exceed at any time during the
month. Measurements shall continue to be taken as described in 310 CMR
22.20A(5)(b)1. and 3. Monthly reporting shall be completed according to 310 CMR
22.20F(8)(a). The following is a description of the required limits for
specific filtration technologies:
a. If the
supplier of water uses conventional filtration or direct filtration, the
"maximum" turbidity level is one NTU.
b. If the supplier of water uses "alternative
filtration" the "maximum" turbidity level is one NTU.
(c) Each supplier of water that
serves fewer than 10,000 people using a surface water source or ground water
source under the direct influence of surface water that uses a system that
consists of alternative filtration (filtration other than slow sand filtration,
diatomaceous earth filtration, conventional filtration, or direct filtration)
is required to conduct a demonstration. The supplier of water shall demonstrate
to the Department, using pilot plant studies or other means, that the system's
filtration, in combination with disinfection treatment, consistently achieves:
1. 99% removal of Cryptosporidium
oocysts;
2. 99.9% removal
and/or inactivation of Giardia lamblia cysts; and
3. 99.99% removal and/or inactivation of
Viruses.
(d) Each
supplier of water serving fewer than 10,000 people using a surface water source
or ground water source under the direct influence of surface water that
practices lime softening, may acidify representative CFE turbidity samples
prior to analysis using a protocol approved by the Department.
(7) Individual Filter Turbidity Requirements.
(a) Each
supplier of water serving fewer than 10,000 people using a surface water source
or ground water source under the direct influence of surface water that
utilizes conventional filtration or direct filtration, shall conduct continuous
monitoring of turbidity for each individual filter at the filtration facility.
The following requirements apply to continuous turbidity monitoring:
1. Monitoring must be conducted using an
approved method in 310 CMR 22.20A(5)(a);
2. Calibration of turbidimeters shall be
conducted using procedures specified by the manufacturer;
3. Results of turbidity monitoring shall be
recorded at least every 15 minutes;
4. Monthly reporting must be completed
according to 310 CMR 22.20F(8)(a); and
5. Records shall be maintained according to
310 CMR 22.20F(8)(b).
(b) If there is a failure in the continuous
turbidity monitoring equipment, the supplier of water shall conduct grab
sampling every four hours in lieu of continuous monitoring until the
turbidimeter is back on-line. The system has 14 days to resume continuous
monitoring before a violation is incurred.
(c) If the system only consists of one or
two, the supplier of water may conduct continuous monitoring of the CFE
turbidity in lieu of individual filter effluent turbidity monitoring.
Continuous monitoring shall meet the same requirements set forth in 310 CMR
22.20F(7)(a)1. through 4. and (b).
(d) If the supplier of water conducts
continuous turbidity monitoring, follow-up action is required as follows:
1. If the turbidity of an individual filter
or the turbidity of the CFE for systems with two filters that monitor CFE in
lieu of individual filters exceeds 1.0 NTU in two consecutive
recordings 15 minutes apart, the supplier of water shall report to the
Department by the tenth day of the following month and include the filter
number(s), corresponding date(s), turbidity value(s) which exceeded 1.0 NTU,
and the cause (if known) for the exceedance(s).
2. If the supplier of water was required to
report to the Department for three months in a row and turbidity exceeded 1.0
NTU in two consecutive recordings 15 minutes apart at the same filter or CFE
for systems with two filters that monitor CFE in lieu of
individual filters, the supplier of water shall conduct a self-assessment of
the filter(s) within 14 days of the day the filter exceeded 1.0 NTU in two
consecutive measurements for the third straight month unless a Comprehensive
Performance Evaluation (CPE) as specified in 310 CMR 22.20F(7)(d)3. was
required. Systems with two filters that monitor CFE in lieu of
individual filters shall conduct a self-assessment on both filters. The
self-assessment must consist of at least the following components: assessment
of filter performance; development of a filter profile; identification and
prioritization of factors limiting filter performance; assessment of the
applicability of corrections; and preparation of a filter self-assessment
report. If a self-assessment is required, the date that it was triggered and
the date that it was completed shall be included.
3. If the supplier of water was required to
report to the Department for two months in a row and turbidity exceeded 2.0 NTU
in two consecutive recordings 15 minutes apart at the same filter or CFE for
systems with two filters that monitor CFE in lieu of
individual filters, the supplier of water shall arrange to have a CPE conducted
by the Department no later than 60 days following the day the filter exceeded
2.0 NTU in two consecutive measurements for the second straight month. If a CPE
has been completed by the Department within the 12 prior months or the supplier
of water and the Department are jointly participating in an ongoing
Comprehensive Technical Assistance (CTA) project at the system, a new CPE is
not required. If conducted, a CPE must be completed and submitted to the
Department no later than 120 days following the day the filter exceeded 2.0 NTU
in two consecutive measurements for the second straight month.
(e) If the supplier of water
practices lime softening, the supplier of water may apply to the Department for
alternative turbidity exceedance levels for the levels specified in 310 CMR
22.20F(7)(d). The supplier of water shall be able to demonstrate to the
Department that higher turbidity levels are due to lime carryover only, and not
due to degraded filter performance.
(8) Reporting and Recordkeeping.
(a) In addition to
the reporting and recordkeeping requirements in 310 CMR 22.20A, each supplier
of water who is subject to the requirements of 310 CMR 22.20F shall report the
following information to the Department at the frequency specified, if the
supplier of water is subject to the specific requirement.
1. Combined filter requirements that shall be
reported within ten days after the end of each month shall include:
a. The total number of filtered water
turbidity measurements taken during the month.
b. The number and percentage of filtered
water turbidity measurements taken during the month which are less than or
equal to the turbidity limits specified in 310 CMR 22.20F(7).
c. The date and value of any turbidity
measurements taken during the month which exceed 1.0 NTU for systems using
conventional filtration treatment or direct filtration, or exceed the maximum
level set by the Department 310 CMR 22.20F(7).
2. The individual turbidity requirements that
shall be reported within ten days after the end of each month, except as
otherwise provided in 310 CMR 22.20F(8)2.c. and 310 CMR 22.20F(8)2.e., shall
include:
a. That the supplier of water
conducted individual filter turbidity monitoring during the month.
b. The filter number(s), corresponding
date(s), and turbidity value(s) that exceeded 1.0 NTU during the month, and the
cause (if known) for the exceedance(s) but only in if two consecutive
measurements exceeded 1.0 NTU.
c.
If a self-assessment is required, the date that it was triggered and the date
that it was completed. If the self-assessment was triggered during the last
four days of the month, the date that it was triggered and the date that it was
completed shall be reported within 14 days after the date the self-assessment
was triggered.
d. If a CPE is
required and the date that it was triggered.
e. Copy of completed CPE report within 120
days after the CPE was triggered.
3. Disinfection Profiling shall include:
a. Results of optional monitoring that show
TTHM levels <0.064 mg/l and HAA5 levels <0.048 mg/l (only if the system
wishes to forgo profiling) or that the system has begun disinfection profiling.
i. For systems serving 500-9,999 by July 1,
2003;
ii. For systems serving fewer
than 500 by January 1, 2004.
4. Disinfection Benchmarking shall include: A
description of the proposed change in disinfection, the system's disinfection
profile for Giardia lamblia (and, if necessary, Viruses) and
disinfection benchmark, and an analysis of how the proposed change will affect
the current levels of disinfection anytime a significant change in disinfection
practices is being considered.
(b) Each supplier of water who is subject to
the requirements of 310 CMR 22.20F shall, in addition to recordkeeping
requirements under 310 CMR 22.20A(6), maintain records in accordance with 310
CMR 22.17(12).
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