Public water systems shall be designed and constructed to
provide sufficient drinking water of a quality that will meet all applicable
standards in Chapters 62-550, F.A.C., and requirements in this chapter. This
section addresses the design and construction of all public water system
components other than wells (but including well pumping equipment and
appurtenances). Public water system wells are addressed in Chapters 62-524 and
62-532, and Rule 62-555.315, F.A.C.
(1) Sound Engineering Practice. New or
altered public water system components shall be designed in accordance with
sound engineering practice. Engineering references are listed in Rule
62-555.330, F.A.C.
(2) Innovative or Alternative Processes and
Equipment. The Department encourages the development of new treatment processes
and equipment. However,
construction permits for innovative or alternative
treatment processes or equipment (i.e., treatment processes or equipment not
covered in the engineering references listed in Rule
62-555.330, F.A.C.) shall
not be issued unless
construction permit applicants include in the preliminary
design report or design data accompanying their permit application supporting
information demonstrating to the Department that the process or equipment is
capable of consistently and reliably producing drinking water meeting
applicable standards in Chapter 62-550, F.A.C., and requirements in this
chapter. Supporting information shall include the following:
(a) The manufacturer's technical
information;
(b) Data and reports
from full-scale or pilot-plant installations that are operated under conditions
comparable to those for which the process or equipment is being proposed and
that are operated for a sufficient time to verify satisfactory performance of
the process or equipment; and,
(c)
Operation and maintenance requirements and availability of technical
support.
(3) Direct or
Indirect Drinking Water Additives.
(a)
Drinking water additives and treatment chemicals, including chemicals used to
regenerate ion-exchange resins or generate disinfectants on site at treatment
plants, shall conform to one of the following:
1. NSF International Standard 60 as adopted
in Rule
62-555.335, F.A.C.,
2. The standards in
Water Chemicals
Codex as adopted in Rule
62-555.335, F.A.C., or
3. The standards in
Food Chemicals
Codex as adopted in Rule
62-555.335, F.A.C.
(b) Newly installed or constructed public
water system (PWS) components that come into contact with advanced treated
water, drinking water or drinking water treatment chemicals shall conform to
the applicable standards, regulations, or requirements referenced in
subparagraphs 1. through 3., below. Fire hydrants are not covered by this
paragraph; and mechanical devices that were previously installed in a PWS and
then are removed, repaired or refurbished, and reinstalled in the same PWS are
not covered by this paragraph. In addition, this paragraph does not apply to
PWS components that either come into contact with drinking water prior to its
treatment by reverse osmosis or come into contact with drinking water treatment
chemicals and that are installed or constructed under a
construction permit for
which the Department received a complete application before August 28, 2003.
1. Except for ion-exchange resins, precast or
cast-in-place concrete structures, and cement mortar, which are addressed in
subparagraphs 2. and 3., below, newly installed or constructed PWS components
that come into contact with advanced treated water, drinking water or drinking
water treatment chemicals shall conform to one of the following:
a. NSF International Standard 61 as adopted
in Rule
62-555.335, F.A.C.,
b. NSF
International Standard 42, 44, 53, 55, 58, or 62 as adopted in Rule
62-555.335,
F.A.C.,
c. Section 6 of NSF
International Standard 14 as adopted in Rule
62-555.335, F.A.C., or
d. The Food and Drug Administration's
regulations for indirect food additives as contained in the April 1, 2002,
revision of 21 C.F.R. Parts
174 through
189, which are incorporated herein by
reference.
2. Newly
installed ion-exchange resins that come into contact with advanced treated
water or drinking water shall be part of an ion-exchange water softener that
conforms to NSF International Standard 44 as adopted in Rule
62-555.335,
F.A.C., or shall conform to one of the following:
a. NSF International Standard 61 as adopted
in Rule
62-555.335, F.A.C., or
b.
The Food and Drug Administration's regulations for secondary direct food
additives from ion-exchange resins as contained in the April 1, 2002, revision
of 21 CFR
173.25, which is incorporated herein by
reference.
3. Any newly
installed or constructed precast or cast-in-place concrete structure or newly
installed cement mortar that is not coated by a barrier material meeting the
requirements of subparagraph 1., above, and that comes into contact with
advanced treated water, drinking water or drinking water treatment chemicals
shall meet the following requirements:
a. All
cement, admixtures, form release agents, curing compounds, and sealers used in
or on the concrete or mortar shall conform to NSF International Standard 61 as
adopted in Rule
62-555.335, F.A.C.
b. Aggregate used in the concrete or mortar
shall be clean (i.e., free of excess clay, silt, mica, organic matter, chemical
salts, and coated grains) and shall be essentially free of those metals and
radionuclides regulated under applicable primary drinking water
standards.
c. Water used in the
concrete or mortar shall meet applicable primary drinking water standards for
inorganics, organics, and radionuclides.
(c) To determine or document whether drinking
water additives or treatment chemicals or public water system components
conform to the standards, regulations, or requirements listed in paragraph (a)
or (b), above, suppliers of water or construction permit applicants may conduct
their own evaluations or may rely upon third-party or manufacturer
certifications.
(d) The Department
shall allow exceptions to the requirements in paragraph (b), above, if
suppliers of water or
construction permit applicants provide the following:
1. Documentation that components conforming
to the applicable standards, regulations, or requirements in paragraph (b), are
not readily available; and,
2.
Assurance that the components being provided will not impart into advanced
treated water, drinking water or drinking water treatment chemicals any
contaminant in an amount that could cause adverse human health
effects.
(4)
Flood Protection. Community water systems (CWSs) shall be designed and
constructed so that structures, and electrical or mechanical equipment, used to
treat, pump, or store advanced treated water or drinking water, apply drinking
water treatment chemicals, or handle drinking water treatment residuals are
protected from physical damage by the 100-year flood and, in coastal areas
subject to flooding by wave action, from physical damage by the 100-year wave
action. Additionally, CWSs shall be designed and constructed so that the
aforementioned structures and equipment remain fully operational and accessible
during the 25-year flood and, in coastal areas subject to flooding by wave
action, the 25-year wave action; a lesser flood or wave action may be used if
suppliers of water or construction permit applicants provide justification for
using a lesser flood or wave action, but in no case shall less than the
ten-year flood or wave action be used.
(5) Security. Drinking water treatment or
pumping facilities shall be enclosed by fences with lockable access gates,
housed in lockable buildings or enclosures, or otherwise protected to prevent
tampering, vandalism, and sabotage. Advanced treated water and
finished-drinking-water storage facilities shall be enclosed by fences with
lockable access gates, shall have lockable access openings and lockable cages
or enclosures obstructing access to ladders, or shall be otherwise protected to
prevent tampering, vandalism, and sabotage.
(6) Capacity of Drinking Water Source and
Treatment Facilities. The total capacity of all water source and treatment
facilities connected to a water system shall at least equal the water system's
design maximum-day water demand (including design fire-flow demand if fire
protection is being provided). Applicants for a permit to construct or alter a
drinking water treatment plant's source water or treatment facilities shall
establish in the preliminary design report or drawings, specifications, and
design data accompanying their permit application the design maximum-day
capacity of the plant's source water facilities and the plant's treatment
facilities and, if the plant is being designed to meet peak water demand or to
supplement finished-drinking-water storage facilities in meeting peak water
demand, the design peak capacity of the plant's source water facilities and the
plant's treatment facilities. In turn, the Department shall specify in its
construction permit for the plant's new or altered source water or treatment
facilities the permitted maximum-day operating capacity of the plant and, if
the plant is being designed to meet peak water demand or to supplement
finished-water storage facilities in meeting peak water demand, the permitted
peak operating capacity of the plant. The Department shall not specify a
permitted plant operating capacity greater than the design capacity of the
plant's treatment facilities as established by the applicant. However, the
Department shall specify a permitted plant operating capacity less than the
design capacity of the plant's treatment facilities if the actual design
capacity of the plant's source water facilities, regardless of any water use
permit limitations set by the water management district, is less than the
design capacity of the plant's treatment facilities; in such a case:
(a) The construction permit for the plant's
new or altered source water or treatment facilities shall indicate the design
capacity of the plant's treatment facilities, shall state that permitted plant
operating capacity is being limited because of the actual design capacity of
the plant's source water facilities, and shall specify a permitted plant
operating capacity equal to the actual design capacity of the plant's source
water facilities.
(b) Each
subsequent construction permit for new or altered source water facilities for
the plant shall update the permitted plant operating capacity as
appropriate.
(7) Raw
Surface Water Pumping Stations. At each raw surface water pumping station that
is constructed or altered under a construction permit for which the Department
receives a complete application on or after August 28, 2003, and that is
connected to a community water system (CWS) serving, or designed to serve, 350
or more persons or 150 or more service connections, the supplier of water shall
provide an installed or uninstalled standby pump of sufficient capacity to
replace the largest pump. However, for CWSs that have multiple pumping stations
subject to this requirement, the supplier of water may provide one uninstalled
standby pump for each size of raw surface water pump installed in the water
system instead of providing a standby pump on site at each raw surface water
pumping station; and for CWSs that have only one pumping station subject to
this requirement and that are designed to serve 10,000 or fewer persons, as
many as three water systems located in the same county, or within 50 miles of
one another, may enter into a mutual aid agreement to share one appropriately
sized, uninstalled standby pump instead of providing a standby pump on site at
each water system's raw surface water pumping station.
(8) Well Pump Housing, Well Pump Discharge
Piping, and Well Pump Appurtenances.
(a)
Housing of Well Pumps.
1. Well pumps shall be
housed in a weatherproof building, room, or pit unless the pumps are
submersible or completely weatherproof, in which case the pumps need only be
protected against tampering, vandalism, and sabotage in accordance with
subsection (5), above.
2. Well
pumphouses (i.e., buildings or rooms) for which the Department receives a
complete construction permit application on or after August 28, 2003, shall
have a concrete floor that is elevated above the adjacent finished ground
surface and that is sloped to drain away from wells and well pumps. In
addition, such well pumphouses shall have an access opening or removable roof
or walls as necessary to provide full access for servicing wells and well
pumps.
3. Well pump pits are
allowed only where the finished ground surface is above the 100-year flood
elevation and, in coastal areas subject to flooding by wave action, the
100-year wave-action elevation. All pump pit access openings shall have
watertight covers or shall be flanged upward and provided with overlapping
covers, and all pump pits shall be drained by gravity or by dual sump pumps
with an alarm system that is activated in the event either sump pump fails.
Sump pump alarm systems shall include an audio-visual alarm near the pump pit,
and if the pump pit is not at a site staffed 24 hours per day and seven days
per week, the alarm also shall be telemetered to a place staffed 24 hours per
day and seven days per week, or shall trigger an automatic telephone dialing or
paging device, to enable notification of an authorized representative of the
supplier of water. Pump pits for which the Department receives a complete
construction permit application on or after August 28, 2003, shall have an
opening as necessary to provide full access for servicing wells and well pumps
and shall have a concrete floor sloped to drain away from wells and well
pumps.
(b) Well Pump
Discharge Piping.
1. New or altered discharge
piping shall be designed and constructed in accordance with Section 3.2.7.3 in
Recommended Standards for Water Works as incorporated into
rule
62-555.330, F.A.C., except that a check valve is not required in the
discharge piping from a jet pump and except that the required smooth-nosed
sampling tap shall be located as specified in subparagraph 2., below.
2. The discharge piping from each well pump
shall include a smooth-nosed tap for sampling raw well water. All such sampling
taps shall be located upstream of the check valve in the discharge piping if
possible and upstream of all treatment facilities and chemical application
points; shall be located at least 12 inches above the finished floor, pad, or
ground surface below the tap; and shall be conveniently accessible and
downward-opening. Raw well water sampling taps installed on or after August 28,
2003, except those installed under a construction permit for which the
Department received a complete application before August 28, 2003, shall have
no interior or exterior threads.
(c) Well Vents. Well pumps installed on or
after August 28, 2003, except those installed under a
construction permit for
which the Department received a complete application before August 28, 2003,
shall pump from a well that is vented to the atmosphere unless the well pump is
a packer-type jet pump, the well casing also serves as well pump suction
piping, the well is a flowing artesian well, there is no appreciable drawdown
in the well, or the supplier of water provides justification for not venting
the well to the atmosphere. All well vents shall terminate at least 12 inches
above the 100-year flood elevation and, in coastal areas subject to flooding by
wave action, at least 12 inches above the 100-year wave-action elevation. New
or altered well vents shall be designed and constructed in accordance with
Section 3.2.7.5 in
Recommended Standards for Water Works as
incorporated into Rule
62-555.330, F.A.C.
(9) Odor Control at Drinking Water Treatment
Plants. Drinking water treatment plants shall comply with the objectionable
odor prohibition under subsection
62-296.320(2),
F.A.C. ("Objectionable odor" is defined in Rule
62-210.200, F.A.C.) Applicants
for a permit to construct or alter drinking water treatment facilities, except
those applicants who have submitted a complete application to the Department
before August 28, 2003, shall provide in the preliminary design report or
drawings, specifications, and design data accompanying their permit application
assurance of compliance with subsection
62-296.320(2),
F.A.C. Assurance of compliance may be based upon water quality data; use of
appropriate water treatment processes and chemicals; proper treatment of vented
gases; use of mitigative measures such as buffer zones owned or under the
control of the supplier of water; etc.
(10) Color Coding of Piping.
(a) Drinking Water Treatment Plants. All new
or altered, aboveground piping at drinking water treatment plants shall be
color coded and labeled as recommended in Section 2.14 of
Recommended
Standards for Water Works as incorporated into Rule
62-555.330, F.A.C.
In addition, all underground water main pipe that is installed at drinking
water treatment plants on or after August 28, 2003, and that is conveying
finished drinking water shall be color coded as required under subparagraph
62-555.320(21)(b)
3., F.A.C. This subsection does not apply to drinking water treatment plant
piping installed or altered under a
construction permit for which the
Department received a complete application before August 28, 2003.
(b) Advanced Treated Water Received by a PWS.
All valves and outlets shall be appropriately tagged or labeled (bearing the
words in English and Spanish: "Do not drink" together with the equivalent
standard international symbol) to warn the public and employees that the water
is not intended for drinking. All piping, pipelines, valves, and outlets shall
be color coded, or otherwise marked, to differentiate advanced treated water
from potable water, domestic wastewater, or other water. Underground piping,
which is not manufactured of metal or concrete, shall be color coded for
advanced treated water using blue as a dominant color, with purple banding
around the pipe. The pipe and band colors shall be easily differentiated to
ensure proper identification of the pipe. For pipes greater than 6 inches in
diameter, bands shall be four inches wide, and spaced no more than 24 inches
apart, measured center-to-center. For pipes 6 inches in diameter or smaller,
bands shall be two inches wide, and spaced no more than 18 inches apart,
measured center-to-center. Underground metal and concrete pipe shall be color
coded or marked using blue and purple banding predominantly. If tape is used to
mark the pipe, the tape shall be permanently affixed to the pipe. Visible,
above-ground portions of the advanced treated water system shall be clearly
color coded or marked. New systems and expansions of existing systems shall
comply with this color-coding standard. It is recommended, but shall not be
required, that distribution and application facilities located on private
properties, including residential properties, be color coded using blue and
purple banding.
(11)
Alarms for Nitrate/Nitrite Removal Equipment. An alarm system shall be provided
for any drinking water treatment plant equipment that is installed or altered
under a construction permit for which the Department receives a complete
application on or after August 28, 2003, and that is necessary to achieve
compliance with the primary drinking water standard for nitrate or nitrite. The
alarm system shall be activated in the event of equipment failure and shall
include an audio-visual alarm at the plant. If the plant is not staffed during
all hours the plant is in operation, the alarm also shall be telemetered to a
place staffed during all hours the plant is in operation, or shall trigger an
automatic telephone dialing or paging device, to enable notification of an
appropriately licensed water treatment plant operator.
(12) Disinfection of Drinking Water. All
suppliers of water shall provide continuous disinfection of the drinking water
they distribute. The necessary equipment and tanks shall be designed to comply
with the applicable requirements in paragraphs (a) through (d), below, and
subsections
62-555.350(5) and
(6), F.A.C. Applicants for a permit to
construct or alter disinfection facilities at a drinking water treatment plant
where the requirements in paragraph (a) or (b), below, apply shall establish in
the preliminary design report or drawings, specifications, and design data
accompanying their permit application the following: the design level of
Cryptosporidium, Giardia lamblia, or virus inactivation to be
achieved by disinfection; if chemical disinfection is being used to achieve
Giardia lamblia or virus inactivation, the design minimum
residual disinfectant concentration (C) before, or at the first customer and
the corresponding design minimum disinfectant contact time (T); and if
ultraviolet disinfection is being used to achieve
Cryptosporidium,
Giardia lamblia, or virus inactivation, the design minimum ultraviolet
dose.
(a) Suppliers of water using surface
water or ground water under the direct influence of surface water, or advanced
treated water shall comply with applicable requirements under Rules
62-550.817 and
62-550.305,
F.A.C.
(b) Suppliers of water using
ground water that is not under the direct influence of surface water but that
is from a well considered microbially contaminated or susceptible to microbial
contamination per paragraph
62-555.315 (6)(b) or (f),
F.A.C., shall provide treatment that reliably achieves at least four-log (99.99
percent) inactivation or removal of viruses before or at the first customer at
all flow rates. Additionally, by no later than December 31, 2005, suppliers of
water using ground water that is not under the direct influence of surface
water but that is exposed during treatment to the open atmosphere and possible
microbial contamination shall provide treatment that reliably achieves at least
four-log inactivation or removal of viruses before or at the first customer at
all flow rates. For the purpose of this paragraph, aerators and other
facilities that are protected against contamination from birds, insects,
wind-borne debris, rainfall, and drainage are not considered to be exposing
water to the open atmosphere and possible microbial contamination. Direct
filtration and diatomaceous-earth filtration are considered to be achieving
one-log (90 percent) removal of viruses when properly operated, and
conventional filtration treatment and slow sand filtration are considered to be
achieving two-log (99 percent) removal of viruses when properly operated.
Chemical disinfection using free chlorine, chlorine dioxide, or ozone and
chemical disinfection using chloramines with chlorine added prior to ammonia
are considered to be achieving two-log, three-log (99.9 percent), or four-log
inactivation of viruses when meeting the applicable CT value listed in Appendix
E of the
Guidance Manual for Compliance with the Filtration and
Disinfection Requirements for Public Water Systems Using Surface Water
Sources as adopted in Rule
62-555.335, F.A.C.
(c) Disinfectant contact time shall be
calculated or determined as described in the definition of "disinfectant
contact time" under Rule
62-550.200, F.A.C.
(d) All suppliers of water shall maintain a
minimum free chlorine residual of 0.2 milligram per liter, or a minimum
combined chlorine residual of 0.6 milligram per liter or an equivalent chlorine
dioxide residual, throughout their drinking water distribution system at all
times.
(13) Chlorination
Facilities for Disinfection of Drinking Water.
(a) Gas Chlorination Facilities.
1. New chlorinators shall be the
vacuum-operated, solution-feed type.
2. Chlorinator capacity shall be such that
any applicable minimum CT value and the minimum residual disinfectant level
specified in paragraph
62-555.320(12)(d),
and subsection
62-555.350(6),
F.A.C., can be maintained when maximum chlorine demand coincides with maximum
flow rate at the point of chlorine application.
3. At each drinking water treatment plant
that is using gas chlorination facilities to achieve
Giardia
lamblia or virus inactivation in accordance with paragraph
62-555.320(12)(a) or
(b), F.A.C.; at each treatment plant that is
using gas chlorination facilities for disinfection and that is connected to a
community water system (CWS) having an actual or design average daily chlorine
consumption equaling or exceeding ten pounds per day; and at each treatment
plant that has gas chlorine disinfection facilities constructed or altered
under a
construction permit for which the Department receives a complete
application on or after August 28, 2003, and that is connected to a CWS
serving, or designed to serve, 350 or more persons or 150 or more service
connections, the supplier of water shall provide installed or uninstalled
standby gas chlorination equipment (i.e., a standby chlorinator, including a
standby vacuum regulator and a standby eductor, which is also referred to as an
injector or ejector; a standby booster pump where booster pumps are used; and a
standby evaporator where evaporators are used) of sufficient capacity to
replace the largest equipment. However, for water systems that have multiple
interconnected plants subject to this requirement, the supplier of water may
provide one uninstalled standby for each type and size of gas chlorination
equipment installed in the water system instead of providing standby gas
chlorination equipment on site at each plant; and for water systems that have
only one plant subject to this requirement and that are designed to serve
10,000 or fewer persons, as many as three water systems located in the same
county, or within 50 miles of one another, may enter into a mutual aid
agreement to share appropriately sized, uninstalled standby gas chlorination
equipment instead of providing standby gas chlorination equipment onsite at
each water system's plant.
4. At
each drinking water treatment plant that is using gas chlorination facilities
to achieve
Giardia lamblia or virus inactivation in accordance
with paragraph
62-555.320(12)(a) or
(b), F.A.C.; at each treatment plant that is
using gas chlorination facilities for disinfection and that is connected to a
community water system (CWS) having an actual or design average daily chlorine
consumption equaling or exceeding ten pounds per day; and at each treatment
plant that has gas chlorine disinfection facilities constructed or altered
under a
construction permit for which the Department receives a complete
application on or after August 28, 2003, and that is connected to a CWS
serving, or designed to serve, 350 or more persons or 150 or more service
connections, the supplier of water shall provide devices for automatic
switch-over of chlorine cylinders or containers.
5. Chlorine shall be fed into drinking water
proportional to flow. Where the flow rate is reasonably constant, this may be
accomplished by electrically interconnecting gas chlorination equipment with
well or service pumps or by otherwise designing gas chlorination equipment to
operate only when well or service pumps operate. Automatic flow proportioning
control of chlorinators shall be provided where the flow rate fluctuates
significantly. Furthermore, automatic residual control of chlorinators shall be
provided where the chlorine demand fluctuates significantly, and automatic
compound-loop control of chlorinators shall be provided where both the flow
rate and the chlorine demand fluctuate significantly.
6. Scales shall be provided to accurately
weigh chlorine cylinders or containers in use.
7. Chlorine shall be rapidly and thoroughly
mixed with all drinking water being treated.
8. Chlorine storage and feed facilities shall
be located in a room or area separate from other operating areas. If chlorine
storage or feed facilities are enclosed in a room, the room shall be located at
ground level and shall be provided with floor-level ventilation. New or altered
chlorine rooms shall be designed and constructed in accordance with Section
5.4.1 in R
ecommended Standards for Water Works as incorporated
into Rule
62-555.330, F.A.C. If chlorine
storage or feed facilities are not enclosed in a room, they shall be shielded
from direct sunlight and rain and shall be located at ground level in an area
that either has adequate natural ventilation or is equipped with a mechanical
ventilation system. For the purpose of this subparagraph, an area is considered
to have adequate natural ventilation if walls are not completely obstructing
more than one side of the perimeter of the area. New or altered mechanical
ventilation systems for chlorine storage or feed areas shall meet applicable
requirements in Section 5.4.1.c of
Recommended Standards for Water
Works as incorporated into Rule
62-555.330, F.A.C.
9. At each drinking water treatment plant
that is using gas chlorination facilities to achieve
Giardia
lamblia or virus inactivation in accordance with paragraph
62-555.320(12)(a) or
(b), F.A.C., and at each treatment plant that
is using gas chlorination facilities for disinfection and that is connected to
a community water system serving, or designed to serve, 350 or more persons or
150 or more service connections, the supplier of water shall provide an
audio-visual alarm system that is activated by high- and low-vacuum switches, a
continuous chlorine residual analyzer, or a continuous oxidation-reduction
potential meter to indicate loss of chlorination capability or chlorine
residual. If the plant is not staffed during all hours the plant is in
operation, the alarm also shall be telemetered to a place staffed during all
hours the plant is in operation, or shall trigger an automatic telephone
dialing or paging device, to enable notification of an appropriately licensed
water treatment plant operator.
10.
Suppliers of water shall provide the following safety or protective equipment
at drinking water treatment plants with gas chlorination facilities.
a. At each treatment plant with gas
chlorination facilities, the supplier of water shall provide in a convenient
location, but not inside any room where chlorine is stored or handled, a
self-contained breathing apparatus (SCBA) meeting the requirements of the
National Institute for Occupational Safety and Health. However, for water
systems that have multiple interconnected plants withdrawing chlorine from only
150-pound or smaller cylinders, the supplier of water may provide an SCBA in
each vehicle used by plant operators instead of providing an SCBA at each plant
withdrawing chlorine from only 150-pound or smaller cylinders.
b. At each treatment plant with gas
chlorination facilities, the supplier of water shall provide appropriate
protective equipment in accordance with Table 15.5 in
Water Treatment
Plant Design as incorporated into Rule
62-555.330, F.A.C., except that
the supplier of water shall provide a self-contained breathing apparatus in
accordance with sub-subparagraph a., above, instead of providing a gas mask in
accordance with this sub-subparagraph and Table 15.5.
c. At each treatment plant withdrawing
chlorine from ton containers or tank cars or trucks, the supplier of water
shall provide continuous chlorine leak detection equipment that is connected to
an alarm system. The alarm system shall include an audio-visual alarm at the
plant, and if the plant is not staffed 24 hours per day and seven days per
week, the alarm also shall be telemetered to a place staffed 24 hours per day
and seven days per week, or shall trigger an automatic telephone dialing or
paging device, to enable notification of an authorized representative of the
supplier of water.
d. At each
treatment plant withdrawing chlorine from ton containers or tank cars or
trucks, the supplier of water shall provide an emergency chlorine leak repair
kit meeting the requirements of the Chlorine Institute.
(b) Hypochlorination Facilities.
1. New hypochlorinators shall be positive
displacement metering pumps or accurate vacuum-operated dosers.
2. Hypochlorinator capacity shall be such
that any applicable minimum CT value and the minimum residual disinfectant
level specified in paragraph
62-555.320(12)(d),
and subsection
62-555.350(6),
F.A.C., can be maintained when maximum chlorine demand coincides with maximum
flow rate at the point of hypochlorite application.
3. At each drinking water treatment plant
that is using hypochlorination facilities to achieve Giardia lamblia or virus
inactivation in accordance with paragraph
62-555.320(12)(a) or
(b), F.A.C.; at each treatment plant that is
using hypochlorination facilities for disinfection and that is connected to a
community water system (CWS) having an actual or design average daily chlorine
consumption equaling or exceeding ten pounds per day; and at each treatment
plant that has hypochlorite disinfection facilities constructed or altered
under a
construction permit for which the Department receives a complete
application on or after August 28, 2003, and that is connected to a CWS
serving, or designed to serve, 350 or more persons or 150 or more service
connections, the supplier of water shall provide installed or uninstalled
standby hypochlorination equipment (i.e., a standby electrolytic generator and
brine pump where sodium hypochlorite is generated on site; a standby metering
pump where metering pumps are used; a standby doser, including a standby vacuum
regulator and a standby eductor, which is also referred to as an injector or
ejector, where vacuum-operated dosers are used; and a standby booster pump
where booster pumps are used) of sufficient capacity to replace the largest
equipment. However, for water systems that have multiple interconnected plants
subject to this requirement, the supplier of water may provide one uninstalled
standby for each type and size of hypochlorination equipment installed in the
water system instead of providing standby hypochlorination equipment on site at
each plant; and for water systems that have only one plant subject to this
requirement and that are designed to serve 10,000 or fewer persons, as many as
three water systems located in the same county, or within 50 miles of one
another, may enter into a mutual aid agreement to share appropriately sized,
uninstalled standby hypochlorination equipment instead of providing standby
hypochlorination equipment on site at each water system's plant.
4. Hypochlorite shall be fed into drinking
water proportional to flow. Where the flow rate is reasonably constant, this
may be accomplished by electrically interconnecting hypochlorination equipment
with well or service pumps or by otherwise designing hypochlorination equipment
to operate only when well or service pumps operate. Automatic flow
proportioning control of hypochlorinators shall be provided where the flow rate
fluctuates significantly. Furthermore, automatic residual control of
hypochlorinators shall be provided where the chlorine demand fluctuates
significantly, and automatic compound-loop control of hypochlorinators shall be
provided where both the flow and the chlorine demand fluctuate
significantly.
5. Hypochlorite
metering pumps shall have antisiphon protection. For new or altered
hypochlorination facilities, the antisiphon protection for metering pumps shall
be in accordance with Section 5.1.5 in
Recommended Standards for Water
Works as incorporated into Rule
62-555.330, F.A.C.
6. For sodium hypochlorite facilities that
are constructed or altered under a
construction permit for which the Department
receives a complete application on or after August 28, 2003, and that include a
metering pump:
a. The pump shall be located as
close as possible to, and lower than, the hypochlorite source with the pump
suction line sloping upward from the pump to the hypochlorite source,
or
b. The hypochlorite facilities
shall be otherwise designed to prevent gas binding of the pump.
7. For hypochlorination facilities
constructed or altered under a
construction permit for which the Department
receives a complete application on or after August 28, 2003:
a. Hypochlorinator suction lines shall be
located with the intake above the bottom of the hypochlorite container or shall
be equipped with a strainer, or
b.
The hypochlorination facilities shall be otherwise designed to avoid feeding
sediment into the drinking water.
8. Sodium hypochlorite shall not be stored or
handled together with any acid or any ammonia or organic compound, and calcium
hypochlorite shall not be stored or handled together with any acid or any
combustible, organic, or oxidizable material. The storage of sodium
hypochlorite shall be carefully managed to limit degradation of the
hypochlorite and to limit formation of chlorate; alternative approaches for
managing sodium hypochlorite storage are discussed on page 243 in
Water
Treatment Plant Design as incorporated into Rule
62-555.330, F.A.C. Tanks for
bulk storage of sodium hypochlorite shall have a liquid-level indicator, a
vent, and an overflow discharging to a basin capable of containing accidental
spills or overflows without uncontrolled discharge. Where bulk storage of
sodium hypochlorite is provided, a day tank also shall be provided unless there
is an alternative means for accurately measuring the daily amount of
hypochlorite fed and there are alternative safeguards (e.g., continuous
chlorine residual monitoring; audio-visual alarms activated by high chlorine
residual levels; and staffing at the water treatment plant, or at a monitoring
and control center for the plant, during all hours the plant is in operation)
that maintain a similar level of protection against overfeeding of
hypochlorite. Sodium hypochlorite bulk storage tanks that are installed on or
after August 28, 2003, and that cannot be completely drained to a day tank
shall be equipped with a valved drain to allow for complete drainage and
periodic cleaning of the bulk storage tank; however, this requirement does not
apply to bulk storage tanks installed under a
construction permit for which the
Department received a complete application before August 28, 2003.
9. Hypochlorite solution or day tanks shall
have a lid or cover, shall have a valved drain, and shall be scale-mounted or
have a means for measuring the liquid level in the tank. For new or altered
hypochlorination facilities, solution or day tanks shall be designed and
constructed in accordance with Sections 5.1.10 and 5.1.11 in
Recommended Standards for Water Works as incorporated into
Rule
62-555.330, F.A.C.
10.
Hypochlorite shall be rapidly and thoroughly mixed with all drinking water
being treated.
11. Housing for new
or altered hypochlorite storage or feed facilities shall be designed and
constructed in accordance with Section 5.1.14 in
Recommended Standards
for Water Works as incorporated into Rule
62-555.330, F.A.C. Waste
hydrogen from onsite sodium hypochlorite generation systems constructed or
altered under a
construction permit for which the Department receives a
complete application on or after August 28, 2003, shall be vented directly to
the outside atmosphere using a dilution air blower as necessary to ensure the
concentration of hydrogen always will be below the explosion level.
12. At each drinking water treatment plant
that is using hypochlorination facilities to achieve
Giardia
lamblia or virus inactivation in accordance with paragraph
62-555.320(12)(a) or
(b), F.A.C., and at each treatment plant that
has hypochlorite disinfection facilities constructed or altered under a
construction permit for which the Department receives a complete application on
or after August 28, 2003, and that is connected to a CWS serving, or designed
to serve, 350 or more persons or 150 or more service connections, the supplier
of water shall provide an audio-visual alarm system that is activated by high-
and low-pressure switches, a low-flow switch or flow meter, high- and
low-vacuum switches, a continuous chlorine residual analyzer, or a continuous
oxidation-reduction potential meter to indicate loss of hypochlorination
capability or chlorine residual. If the plant is not staffed during all hours
the plant is in operation, the alarm also shall be telemetered to a place
staffed during all hours the plant is in operation, or shall trigger an
automatic telephone dialing or paging device, to enable notification of an
appropriately licensed water treatment plant operator.
13. At each drinking water treatment plant
with hypochlorination facilities, the supplier of water shall provide
appropriate safety or protective equipment in accordance with Table 15.5 in
Water Treatment Plant Design as incorporated into Rule
62-555.330, F.A.C.
(14) Standby Power.
(a) By no later than December 31, 2005, each
community water system (CWS) serving, or designed to serve, 350 or more persons
or 150 or more service connections shall provide standby power for operation of
that portion of the system's water source, treatment, and pumping facilities
necessary to deliver drinking water meeting all applicable primary or secondary
standards at a rate at least equal to the average daily water demand for the
system. If a CWS interconnects with another CWS to meet this requirement, the
portion of the combined systems' components provided with standby power shall
be sufficient to deliver water at a rate at least equal to the average daily
water demand for the combined systems.
(b) Where standby power is required under
paragraph (a), above, it shall be provided through:
1. Connection to at least two independent
power feeds from separate substations, or
2. One or more auxiliary power sources (i.e.,
generators or engines).
(c) Where standby power is required under
paragraph (a), above, and is provided through connection to independent power
feeds from separate substations, the power feeds shall not be located in the
same conduit or supported from the same utility pole and, if overhead power
feeds are used, shall not cross or be located in an area where a single
plausible occurrence (e.g., a fallen tree) could disrupt both power
feeds.
(d) Where standby power is
required under paragraph (a), above, and is provided through an auxiliary power
source, an in-place auxiliary power source is preferred. A portable auxiliary
power source may be provided only if all of the following conditions are met:
1. A system to automatically start up the
auxiliary power source and transfer electrical loads is not required under
paragraph (e), below.
2. The
supplier of water demonstrates that the water system has first priority for use
of the portable auxiliary power source.
3. The supplier of water demonstrates that
the portable auxiliary power source will at all times be in reasonably close
proximity to (i.e., within 25 miles of) the water system components for which
standby power is required.
(e) Where standby power is required under
paragraph (a), above, and the time delay required to manually transfer
electrical loads from one power source to another could result in failure to
maintain the minimum water distribution system pressure required under
subsection
62-555.350(7),
F.A.C., the supplier of water shall provide a system to automatically start up
the auxiliary power source if an auxiliary power source is provided and to
automatically transfer electrical loads.
(f) At each site where standby power is
required under paragraph (a), above, the supplier of water shall provide by
December 31, 2005, an audio-visual alarm system that is activated in the event
any power source fails. If the site is not staffed during all hours the
standby-powered water system components are in operation, the alarm also shall
be telemetered to a place staffed during all hours the standby-powered water
system components are in operation, or shall trigger an automatic telephone
dialing or paging device, to enable notification of an authorized
representative of the supplier of water.
(15) High-Service or Booster Pumps. For
purposes of this subsection, well pump installations shall be considered
high-service pumping stations if the well pumps serve as high-service pumps.
(a) Unless elevated finished-drinking-water
storage is provided, the total capacity of all high-service pumping stations
connected to a water system, or the capacity of a booster pumping station,
shall be sufficient to:
1. Meet at least the
water system's, or the booster station service area's, peak-hour water demand
(and if fire protection is being provided, meet at least the water system's, or
the booster station service area's, design fire-flow rate plus a background
water demand equivalent to the maximum-day demand other than fire-flow demand);
and,
2. Maintain a minimum gauge
pressure of 20 pounds per square inch throughout the water system's, or the
booster station service area's, distribution system up to each customer's point
of connection to the distribution system.
(b) Where elevated finished-drinking-water
storage is provided, the total capacity of all high-service pumping stations
connected to a water system, or the capacity of a booster pumping station,
shall be sufficient to at least meet the water system's, or the booster station
service area's, maximum-day water demand (including design fire-flow demand if
fire protection is being provided) and to maintain distribution system pressure
as specified in subparagraph
62-555.320(15)(a)
2., F.A.C. In addition, the total capacity of the high-service pumping
stations, or the capacity of the booster pumping station, combined with the
useful elevated finished-water storage capacity shall be sufficient to meet the
water system's, or the booster station service area's, peak-hour water demand
for at least four consecutive hours (and if fire protection is being provided,
shall be sufficient to meet the water system's, or the booster station service
area's, design fire-flow rate plus a background water demand equivalent to the
maximum-day demand other than fire-flow demand for the design fire-flow
duration).
(c) At each high-service
or booster pumping station that is constructed or altered under a construction
permit for which the Department receives a complete application on or after
August 28, 2003, and that is connected to a community water system (CWS)
serving, or designed to serve, 350 or more persons or 150 or more service
connections, the supplier of water shall provide an installed or uninstalled
standby pump of sufficient capacity to replace the largest pump. However, for
CWSs that have multiple interconnected pumping stations subject to this
requirement, the supplier of water may provide one uninstalled standby pump for
each size of high-service or booster pump installed in the water system instead
of providing a standby pump on site at each high-service or booster pumping
station; and for water systems that have only one pumping station subject to
this requirement and that are designed to serve 10,000 or fewer persons, as
many as three water systems located in the same county, or within 50 miles of
one another, may enter into a mutual aid agreement to share one appropriately
sized, uninstalled standby pump instead of providing a standby pump on site at
each water system's high-service or booster pumping station.
(16) Finished-Drinking-Water
Meters. All water treatment plants that are connected to a community water
system and water treatment plants that are connected to a non-community water
system and that are constructed or altered under a construction permit for
which the Department receives a complete application on or after August 28,
2003, shall be equipped with a totalizing flow meter to measure the net
quantity of finished drinking water, excluding any filter backwash water,
produced at the plant each day. All other drinking water treatment plants shall
be equipped with at least elapsed time meters that can be used in conjunction
with calibrated pumps to measure the net quantity of finished drinking water
produced at the plant each day.
(17) Finished-Drinking-Water Sampling Taps. A
conveniently accessible sampling tap shall be provided at each entry point to a
drinking water distribution system (i.e., at each point where drinking water
source and treatment facilities discharge to a drinking water distribution
system), so that samples of finished drinking water may be taken in accordance
with subsection
62-550.500(5),
F.A.C. Each such sampling tap shall be located downstream from all water
treatment processes at a point where all treatment chemicals have been
thoroughly mixed with the water and shall be located upstream from all water
customers. If a water system draws water from more than one source and combines
the sources before distribution, a single finished-water sampling tap may be
provided downstream from where all of the sources are combined at a point where
all of the sources have been thoroughly mixed together.
(18) Pump Suction Piping. All pump suction
piping that is conveying raw, partially treated, advanced treated water or
finished drinking water shall be protected against infiltration. Pump suction
piping that is conveying raw, partially treated, advanced treated water, or
finished drinking water and that is constructed or altered under a construction
permit for which the Department receives a complete application on or after
August 28, 2003, must be located aboveground or, if located underground, must
be constantly under positive gauge pressure.
(19) Finished-Drinking-Water Storage
Capacity. This subsection addresses finished-water storage capacity necessary
for operational equalization to meet peak water demand. (If fire protection is
being provided, additional finished-water storage capacity shall be provided as
necessary to meet the design fire-flow rate for the design fire-flow duration.)
The finished-water storage capacity necessary to meet the peak water demand for
a consecutive system may be provided by the consecutive system or by a
wholesale system delivering water to the consecutive system.
(a) Except as noted in paragraph (b), below,
the total useful finished-water storage capacity (excluding any storage
capacity for fire protection) connected to a water system shall at least equal
25 percent of the system's maximum-day water demand, excluding any design
fire-flow demand.
(b) A total
useful finished-water storage capacity less than that specified in paragraph
(a), above, is acceptable if the supplier of water or
construction permit
applicant makes one of the following demonstrations:
1. A demonstration consistent with Section
10.6.3 in
Water Distribution Systems Handbook as incorporated
into Rule
62-555.330, F.A.C., showing that
the water system's total useful finished-water storage capacity (excluding any
storage capacity for fire protection) is sufficient for operational
equalization.
2. A demonstration
showing that, in conjunction with the capacity of the water system's source,
treatment, and finished-water pumping facilities, the water system's total
useful finished-water storage capacity (excluding any storage capacity for fire
protection) is sufficient to meet the water system's peak-hour water demand for
at least four consecutive hours. For small water systems with hydropneumatic
tanks that are installed under a construction permit for which the Department
receives a complete application on or after August 28, 2003, the supplier of
water or construction permit applicant also shall demonstrate that, in
conjunction with the capacity of the water system's source, treatment, and
finished-water pumping facilities, the water system's total useful
finished-water storage capacity (i.e., the water system's total effective
hydropneumatic tank volume) is sufficient to meet the water system's peak
instantaneous water demand for at least 20 consecutive minutes.
(20) Hydropneumatic
Tanks. New hydropneumatic tanks, including bladder- or diaphragm-type tanks,
shall be designed and constructed in accordance with Section 7.2 in
Recommended Standards for Water Works as incorporated into
Rule
62-555.330, F.A.C., except that:
(a) The tanks need not be housed.
(b) Tanks installed on or after August 28,
2003, except those installed under a construction permit for which the
Department received a complete application before August 28, 2003, shall have
an automatic air or pressure relief valve.
(c) Bladder- or diaphragm-type tanks need not
have an access manhole, water sight glass, or means for adding air other than a
recharging valve.
(21)
Drinking Water Piping and Appurtenances.
(a)
All new or altered mains, including treatment plant process piping, and
appurtenances conveying raw, or partially treated drinking water, or advanced
treated water, shall be designed and constructed in accordance with Sections
8.0, 8.4, 8.5, and 8.7 in
Recommended Standards for Water
Works as incorporated into Rule
62-555.330, F.A.C., except that:
1. Asbestos-cement water mains shall be
pressure and leakage tested in accordance with American Water Works Association
(AWWA) Standard C603 as incorporated into Rule
62-555.330, F.A.C., and
polyvinyl chloride water mains shall be pressure and leakage tested in
accordance with AWWA Standard C605 as incorporated into Rule
62-555.330, F.A.C., while all
other types of water mains shall be pressure and leakage tested in accordance
with AWWA Standard C600 as incorporated into Rule
62-555.330, F.A.C.
2. Water mains and appurtenances that
normally convey surface water, or ground water under the direct influence of
surface water, and that are located upstream of all filtration and disinfection
treatment facilities need not be disinfected.
3. All water mains and appurtenances other
than those described in subparagraph 2., above, shall be disinfected and
bacteriologically evaluated in accordance with Rule
62-555.340, F.A.C.
(b) All new or altered piping,
including treatment plant process piping, and appurtenances conveying finished
drinking water shall be designed and constructed in accordance with Sections
8.0 through 8.5 and 8.7 through 8.11 in
Recommended Standards for Water
Works as incorporated into Rule
62-555.330, F.A.C., except that:
1. Asbestos-cement water mains shall be
pressure and leakage tested in accordance with American Water Works Association
(AWWA) Standard C603 as incorporated into Rule
62-555.330, F.A.C., and
polyvinyl chloride water mains shall be pressure and leakage tested in
accordance with AWWA Standard C605 as incorporated into Rule
62-555.330, F.A.C., while all
other types of water mains shall be pressure and leakage tested in accordance
with AWWA Standard C600 as incorporated into Rule
62-555.330, F.A.C.
2. All water mains and appurtenances shall be
disinfected and bacteriologically evaluated in accordance with Rule
62-555.340,
F.A.C.
3. All water main pipe,
including fittings, installed on or after August 28, 2003, except pipe
installed under a
construction permit for which the Department received a
complete application before August 28, 2003, shall be color coded or marked
using blue as a predominant color to differentiate drinking water from
reclaimed or other water. Underground plastic pipe shall be solid-wall blue
pipe, shall have a co-extruded blue external skin, or shall be white or black
pipe with blue stripes incorporated into, or applied to, the pipe wall; and
underground metal or concrete pipe shall have blue stripes applied to the pipe
wall. Pipe striped during manufacturing of the pipe shall have continuous
stripes that run parallel to the axis of the pipe, that are located at no
greater than 90-degree intervals around the pipe, and that will remain intact
during and after installation of the pipe. If tape or paint is used to stripe
pipe during installation of the pipe, the tape or paint shall be applied in a
continuous line that runs parallel to the axis of the pipe and that is located
along the top of the pipe; for pipes with an internal diameter of 24 inches or
greater, tape or paint shall be applied in continuous lines along each side of
the pipe as well as along the top of the pipe. Aboveground pipe at drinking
water treatment plants shall be color coded and labeled in accordance with
subsection
62-555.320(10),
F.A.C., and all other aboveground pipe shall be painted blue or shall be color
coded or marked like underground pipe.
(c) The Department shall allow the use of
pipe and appurtenances that do not conform to applicable American Water Works
Association (AWWA) standards as incorporated into Rule
62-555.330, F.A.C., only if
suppliers of water or
construction permit applicants provide documentation
showing that the alternate pipe and appurtenances provide strength, durability,
reliability, and public health protection at least equal to that provided by
pipe and appurtenances that conform to applicable AWWA standards.