Current through Reg. 50, No. 187; September 24, 2024
(1)
Depuration Water Treatment Standards.
(a) All
controlled processes require quality tests to determine if standards are being
met and if controls are effective. The depuration treatment of shellfish is a
controlled process designed to reduce bacterial contamination to an acceptable
level, as defined in subsection
5L-1.004(5),
F.A.C. Wet storage is designed to enhance the product quality without
degradation of market standards as defined in Rule
5L-1.004, F.A.C. To insure the
continuing effectiveness of the shellfish depuration treatment process, the
minimum sampling procedure as described below shall be followed.
(b) Incoming seawater.
1. Type of test - temperature, turbidity,
salinity, dissolved oxygen.
2.
Frequency - each time seawater is withdrawn.
(c) Effluent from UV light treatment unit.
1. Type of test - bacteriological.
2. Frequency - once per day per
unit.
(d) Bacteriological
- All water to be used in shellfish treatment tanks shall be subjected to UV
light treatment. The water discharged from the UV unit shall have no detectable
levels of the coliform group as measured by the recognized multi-tube MPN test
per 100 ml for potable water and acceptable for use with marine water and
follow the protocol of the Decision Tree (Section IV. Guidance Documents
Chapter III .05), as stated in Section II Chapter VII .04 C (1)(f), of the NSSP
Model Ordinance as incorporated in Rule
5L-1.001, F.A.C.
(e) Dissolved oxygen - The amount of
dissolved oxygen in the water in the treatment tanks shall be at least 5 mg/l
and shall be measured daily.
(f)
Temperature - Treatment tank water temperature shall be measured daily during
the treatment process. Temperature of seawater used in the treatment process
shall be suitable for depuration.
(g) Turbidity - Turbidity in the treatment
process water shall not exceed 20 N.T.U. (Nephelos Turbidity Units) and shall
be measured daily.
(h) Salinity -
Salinity of the treatment process water shall be suitable for depuration and
shall be measured daily.
(i) pH -
pH of the treatment process water shall range from greater than or equal to 7.0
to less than or equal to 8.4 and shall be measured daily.
(j) Metallic ions and compounds - Levels of
metallic ions and compounds shall not exceed levels found in approved shellfish
harvesting areas and shall be measured if required by the Department.
(k) Pesticides, detergents, and radionuclides
- Levels of pesticides, detergents, and radionuclides shall not exceed levels
found in approved shellfish harvesting areas and shall be measured if required
by the Department.
(l) Marine
toxins (
Karenia brevis) - Levels of
Karenia
brevis in the incoming seawater and in the source water shall not
exceed 1, 000 cells/liter. Only Department personnel, or personnel approved by
the Department, shall determine levels of
Karenia brevis.
The following table provides a summary of the depuration
treatment process water standards:
Table 1. DEPURATION TREATMENT PROCESS
WATER STANDARDS
|
Parameter
|
Minimum
|
Maximum
|
Bacteriological
|
0
|
Less than 1
|
Dissolved Oxygen (Milligrams/liter)
|
5.0
|
Saturation
|
Temperature
|
Suitable
|
Suitable
|
Turbidity (Nephelos Turbidity Units)
|
0
|
20 units
|
Salinity
|
Suitable
|
Suitable
|
Parameter
|
Minimum
|
Maximum
|
pH
|
7.0
|
8.4
|
Metallic Ions and Compounds
|
Not exceeding levels found in approved shellfish
harvesting areas.
|
|
Pesticides, Detergents and Radionuclides
|
Not exceeding levels found in approved shellfish
harvesting areas.
|
|
Marine Toxins (Karenia
brevis)
|
0 cells/liter
|
1, 000 cells/liter
|
(2) Wet Storage Treatment Standards.
(a) Wet storage of shellfish is done to
enhance product quality of shellfish that have been harvested from Approved or
Conditionally Approved shellfish harvest areas in the open status. Inland wet
storage systems are classified by the Department as continuous flow through or
recirculating systems. Continuous flow through systems have a continuous flow
of new water passing through and exiting the wet storage system before being
permanently discharged. Recirculating systems recirculate system water for wet
storage cycle. All inland wet storage requires the minimum sampling procedure
as described below.
(b) Incoming
seawater must be from an Approved or Conditionally Approved shellfish
harvesting area in the open status.
(c) Bacteriological Standards - Source water
shall be from a shellfish harvest area classified as Approved or Conditionally
Approved and in the open status and any well water used as source water shall
meet the requirements of Chapter XI .02 of the NSSP Model Ordinance as
incorporated in Rule 5L-1.001, F.A.C., with the
exception of salt content for salt water wells. Any source water meeting above
standards and used in continuous flow through systems do not require the use of
additional UV sterilization. Well water from salt water wells must be sampled
semi-annually at a minimum. Water used in shellfish treatment tanks for
recirculating wet storage systems shall be subjected to disinfection as
provided by Department approved disinfection treatment. Systems using one or
more UV light units must be rated for both the volume and flow used by the
recirculating system. The water discharged from the disinfection treatment
system shall have no detectable levels of the coliform group as measured by the
recognized multi-tube MPN test per 100 ml for potable water and acceptable for
use with marine water and follow the protocol of the Decision Tree (Section IV.
Guidance Documents Chapter III .05).
(d) Turbidity - Water that is disinfected by
UV light shall not exceed 20 N.T.U. (Nephelos Turbidity Units).
(e) Wet storage using recirculating systems
requires the effluent from the disinfection treatment unit to be tested for
coliform while in operation but not to exceed once per week.
(f) Other disinfection treatment such as the
addition of salt shall not leave residues unless they are Generally Recognized
as Safe (GRAS) and do not interfere with the shellstock's survival, quality or
activity during wet storage, as stated in Section II, Chapter VII .04 C (1)(e)
of the NSSP Model Ordinance as incorporated in Rule
5L-1.001,
F.A.C.
Rulemaking Authority 597.020 FS. Law Implemented 597.020
FS.
New 1-4-87, Amended 8-10-88, Formerly 16R-7.024, Amended
7-3-95, 5-8-96, 2-6-97, Formerly 62R-7.024, Amended 8-9-00, 3-23-17,
4-2-19.