Cal. Code Regs. Tit. 22, § 64554 - New and Existing Source Capacity
(a) At all times, a public water system's
water source(s) shall have the capacity to meet the system's maximum day demand
(MDD). MDD shall be determined pursuant to subsection (b).
(1) For systems with 1,000 or more service
connections, the system shall be able to meet four hours of peak hourly demand
(PHD) with source capacity, storage capacity, and/or emergency source
connections.
(2) For systems with
less than 1,000 service connections, the system shall have storage capacity
equal to or greater than MDD, unless the system can demonstrate that it has an
additional source of supply or has an emergency source connection that can meet
the MDD requirement.
(3) Both the
MDD and PHD requirements shall be met in the system as a whole and in each
individual pressure zone.
(b) A system shall estimate MDD and PHD for
the water system as a whole (total source capacity and number of service
connections) and for each pressure zone within the system (total water supply
available from the water sources and interzonal transfers directly supplying
the zone and number of service connections within the zone), as follows:
(1) If daily water usage data are available,
identify the day with the highest usage during the past ten years to obtain
MDD; determine the average hourly flow during MDD and multiply by a peaking
factor of at least 1.5 to obtain the PHD.
(2) If no daily water usage data are
available and monthly water usage data are available:
(A) Identify the month with the highest water
usage (maximum month) during at least the most recent ten years of operation
or, if the system has been operating for less than ten years, during its period
of operation;
(B) To calculate
average daily usage during maximum month, divide the total water usage during
the maximum month by the number of days in that month; and
(C) To calculate the MDD, multiply the
average daily usage by a peaking factor that is a minimum of 1.5; and
(D) To calculate the PHD, determine the
average hourly flow during MDD and multiply by a peaking factor that is a
minimum of 1.5.
(3) If
only annual water usage data are available:
(A) Identify the year with the highest water
usage during at least the most recent ten years of operation or, if the system
has been operating for less than ten years, during its years of
operation;
(B) To calculate the
average daily use, divide the total annual water usage for the year with the
highest use by 365 days; and
(C) To
calculate the MDD, multiply the average daily usage by a peaking factor of
2.25.
(D) To calculate the PHD,
determine the average hourly flow during MDD and multiply by a peaking factor
that is a minimum of 1.5.
(4) If no water usage data are available,
utilize records from a system that is similar in size, elevation, climate,
demography, residential property size, and metering to determine the average
water usage per service connection. From the average water usage per service
connection, calculate the average daily demand and follow the steps in
paragraph (3) to calculate the MDD and PHD.
(c) Community water systems using only
groundwater shall have a minimum of two approved sources before being granted
an initial permit The system shall be capable of meeting MDD with the
highest-capacity source off line.
(d) A public water system shall determine the
total capacity of its groundwater sources by summing the capacity of its
individual active sources. If a source is influenced by concurrent operation of
another source, the total capacity shall be reduced to account for such
influence. Where the capacity of a source varies seasonally, it shall be
determined at the time of MDD.
(e)
The capacity of a well shall be determined from pumping data existing prior to
March 9, 2008 or in accordance with subsection (f) or (g). Prior to conducting
a well capacity test pursuant to subsection (g), a system shall submit the
information listed below to the State Board for review and approval. For well
capacity tests conducted pursuant to subsection (f), the information shall be
submitted to the State Board if requested by the State Board.
(1) The name and qualifications of the person
who will be conducting the test;
(2) The proposed test's pump discharge rate,
based on the design rate determined during well development and/or a
step-drawdown test.
(3) A copy of a
United States Geological Survey 7 1/2 -minute topographic map of the site at a
scale of 1:24,000 or larger (1 inch equals 2,000 feet or 1 inch equals less
than 2,000 feet) or, if necessary, a site sketch at a scale providing more
detail, that clearly indicates;
(A) The well
discharge location(s) during the test, and
(B) The location of surface waters, water
staff gauges, and other production wells within a radius of 1000
feet;
(4) A well
construction drawing, geologic log, and electric log, if available;
(5) Dates of well completion and well
development, if known;
(6)
Specifications for the pump that will be used for the test and the depth at
which it will draw water from the well;
(7) A description of the methods and
equipment that will be used to measure and maintain a constant pumping
rate;
(8) A description of the
water level measurement method and measurement schedule;
(9) For wells located in or having an
influence on the aquifer from which the new well will draw water, a description
of the wells' operating schedules and the estimated amount of groundwater to be
extracted, while the new well is tested and during normal operations prior to
and after the new well is in operation;
(10) A description of the surface waters,
water staff gauges, and production wells-shown in (3)(B);
(11) A description of how the well discharge
will be managed to ensure the discharge doesn't interfere with the
test;
(12) A description of how the
initial volume of water in the well's casing, or bore hole if there is no
casing at the time, will be addressed to ensure it has no impact on the test
results; and
(13) A written
description of the aquifer's annual recharge.
(f) To determine the capacity of a well
drilled in alluvial soils when there is no existing data to determine the
capacity, a water system shall complete a constant discharge (pumping rate)
well capacity test and determine the capacity as follows:
(1) Take an initial water level measurement
(static water level) and then pump the well continuously for a minimum of eight
hours, maintaining the pump discharge rate proposed in subsection
(e)(2);
(2) While pumping the well,
take measurements of the water level drawdown and pump discharge rates for a
minimum of eight hours at a frequency no less than every hour;
(3) Plot the drawdown data versus the time
data on semi-logarithmic graph paper, with the time intervals on the horizontal
logarithm axis and the drawdown data on the vertical axis;
(4) Steady-state is indicated if the last
four hours of drawdown measurements and the elapsed time yield a straight line
in the plot developed pursuant to subsection (3). If steady-state is not
achieved, the pump discharge rate shall be continued for a longer period of
time or adjusted, with paragraphs (2) and (3) above repeated, until
steady-state is achieved.
(5)
Discontinue pumping and take measurements of the water level drawdown no less
frequently than every 15 minutes for the first two hours and every hour
thereafter for at least six hours or until the test is complete; and
(6) To complete the test, the well shall
demonstrate that, within a length of time not exceeding the duration of the
pumping time of the well capacity test, the water level has recovered to within
two feet of the static water level measured at the beginning of the test or to
a minimum of ninety-five percent of the total drawdown measured during the
test, whichever is more stringent.
(7) The capacity of the well shall be the
pump discharge rate determined by a completed test.
(g) The capacity of a well whose primary
production is from a bedrock formation, such that the water produced is yielded
by secondary permeability features (e.g., fractures or cracks), shall be
determined pursuant to either paragraph (1) or (2) below.
(1) The public water system shall submit a
report, for State Board review and approval, proposing a well capacity based on
well tests and the evaluation and management of the aquifer from which the well
draws water. The report shall be prepared and signed by a California registered
geologist with at least three years of experience with groundwater hydrology, a
California licensed engineer with at least five years of experience with
groundwater hydrology, or a California certified hydrogeologist. Acceptance of
the proposed well capacity by the State Board shall, at a minimum, be based on
the State Board's review and approval of the following information presented in
the report in support of the proposed well capacity:
(A) The rationale for the selected well test
method and the results;
(B) The
geological environment of the well;
(C) The historical use of the
aquifer;
(D) Data from monitoring
of other local wells;
(E) A
description of the health risks of contaminants identified in a source water
assessment, as defined in section
of Title
2264401.57 of Title 22, and the likelihood of
such contaminants being present in the well's discharge;
(F) Impacts on the quantity and quality of
the groundwater;
(G) How
adjustments were made to the estimated capacity based on drawdown, length of
the well test, results of the wells test, discharge options, and seasonal
variations and expected use of the well; and
(H) The well test(s) results and capacity
analysis.
(2) During the
months of August, September, or October, conduct either a 72-hour well capacity
test or a 10-day well capacity test, and determine the well capacity using the
following procedures:
(A) Procedures for a 72
hour well capacity test:
1. For the purpose
of obtaining an accurate static water level value, at least twelve hours before
initiating step 2., pump the well at the pump discharge rate proposed in
subsection (e)(2) for no more than two hours, then discontinue
pumping;
2. Measure and record the
static water level and then pump the well continuously for a minimum of 72
hours starting at the pump discharge rate proposed in (e)(2);
3. Measure and record water drawdown levels
and pump discharge rate:
a. Every thirty
minutes during the first four hours of pumping,
b. Every hour for the next four hours,
and
c. Every four hours thereafter
until the water drawdown level is constant for at least the last four remaining
measurements, and;
4.
Plot the drawdown and pump discharge rate data versus time data on
semi-logarithmic graph paper, with the time intervals on the horizontal
logarithmic axis and the drawdown and pump discharge rate data on the vertical
axis.
(B) Procedures for
a 10 day well capacity test:
1. For the
purpose of obtaining an accurate static water level value, at least twelve
hours before initiating step 2., pump the well at the pump discharge rate
proposed in subsection (e)(2) for no more than two hours, then discontinue
pumping;
2. Measure and record the
static water level and then pump the well continuously for a minimum of 10 days
starting at the pump discharge rate proposed in (e)(2);
3. Measure and record water drawdown levels
and pumping rate:
a. Every thirty minutes
during the first four hours of pumping,
b. Every hour for the next four
hours,
c. Every eight hours for the
remainder of the first four days,
d. Every 24 hours for the next five days,
and
e. Every four hours thereafter
until the water drawdown level is constant for at least the last four remaining
measurements, and;
4.
Plot the drawdown and pump discharge rate data versus time data on
semi-logarithmic graph paper, with the time intervals on the horizontal
logarithmic axis and the drawdown and pump discharge rate data on the vertical
axis.
(C) To complete
either the 72-hour or 10-day well capacity test the well shall demonstrate
that, within a length of time not exceeding the duration of the pumping time of
the well capacity test, the water level has recovered to within two feet of the
static water level measured at the beginning of the well capacity test or to a
minimum of ninety-five percent of the total drawdown measured during the test,
whichever is more stringent. If the well recovery does not meet these criteria,
the well capacity cannot be determined pursuant to subsection (g)(2) using the
proposed pump rate. To demonstrate meeting the recovery criteria, the following
water level data in the well shall be measured, recorded, and compared with the
criteria:
1. Every 30 minutes during the
first four hours after pumping stops,
2. Hourly for the next eight hours,
and
3. Every 12 hours until either
the water level in the well recovers to within two feet of the static water
level measured at the beginning of the well capacity test or to a at least
ninety-five percent of the total drawdown measured during the test, which ever
occurs first.
(D)
Following completion of a 72-hour or 10-day well capacity test, the well shall
be assigned a capacity no more than:
1. For a
72-hour test, 25 percent of the pumping rate at the end of a completed test's
pumping.
2. For a 10-day test, 50
percent of the pumping rate at the end a completed test's
pumping.
(h) The public water system shall submit a
report to the State Board that includes all data and observations associated
with a well capacity test conducted pursuant to subsection (f) or (g), as well
as the estimated capacity determination methods and calculations. The data
collected during pumping and recovery phases of the well capacity tests shall
be submitted in an electronic spreadsheet format in both tabular and graphic
files.
(i) An assigned well
capacity may be revised by the State Board if pumping data collected during
normal operations indicates that the assigned well capacity was not
representative of the actual well capacity.
(j) If directed by the State Board to do so,
based on adverse conditions that may lead or may have led to a regional
aquifer's inability to meet a water system's demand on such an aquifer, the
water system shall submit a report to the State Board that includes regional
aquifer recharge estimates and a water balance analysis. The report shall be
prepared and signed by a California registered geologist with at least three
years of experience with groundwater hydrology, a California licensed engineer
with at least five years of experience with groundwater hydrology, or a
California certified hydrogeologist.
(k) The source capacity of a surface water
supply or a spring shall be the lowest anticipated daily yield based on
adequately supported and documented data.
(l) The source capacity of a purchased water
connection between two public water systems shall be included in the total
source capacity of the purchaser if the purchaser has sufficient storage or
standby source capacity to meet user requirements during reasonable foreseeable
shutdowns by the supplier.
Notes
2. Change without regulatory effect amending subsections (e), (g)(1) and (h)-(j) and amending NOTE filed 6-2-2015 pursuant to section 100, title 1, California Code of Regulations (Register 2015, No. 23).
3. Amendment of subsection (g)(1)(E) filed 6-17-2021; operative 7-1-2021 pursuant to Government Code section 11343.4(b)(3) (Register 2021, No. 25). Transmission deadline specified in Government Code section 11346.4(b) extended 60 calendar days pursuant to Executive Order N-40-20.
Note: Authority cited: Sections 116271, 116350 and 116375, Health and Safety Code. Reference: Sections 116275, 116375, 116540 and 116555, Health and Safety Code.
2. Change without regulatory effect amending subsections (e), (g)(1) and (h)-(j) and amending Note filed 6-2-2015 pursuant to section 100, title 1, California Code of Regulations (Register 2015, No. 23).
3. Amendment of subsection (g)(1)(E) filed 6-17-2021; operative
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