
U. S. Food and Drug Administration
Center for Food Safety and Applied Nutrition
Office of Seafood
November 3, 2000

A more recent version of this document
issued in November 2004. Below is an earlier version.
NATIONAL SHELLFISH SANITATION PROGRAM
MODEL ORDINANCE
IV. SHELLSTOCK GROWING AREAS
(Table of Contents)
Requirements for the Authority.
[Note: The Authority must meet the requirements of this section even if the
Authority does not formally adopt this chapter in regulation.]
@.01 Sanitary Survey.
A. General.
(1) The sanitary survey is the written evaluation report of all
environmental factors, including actual and potential pollution sources, which have
a bearing on water quality in a shellfish growing area. The sanitary survey shall
include the data and results of:
(a) A shoreline survey;
(b) A survey of the bacteriological quality of the water;
(c) An evaluation of the effect of any meteorologic, hydrodynamic,
and geographic characteristics on the growing area;
(d) An analysis of the data from the shoreline survey, the
bacteriological survey, and the hydrodynamic, meteorologic and geographic
evaluations; and
(e) A determination of the appropriate growing area classification.
(2) The sanitary survey shall be periodically updated through the
triennial reevaluation and the annual review in accordance with §C. to assure that
data is current and that conditions are unchanged.
(3) The documentation supporting each sanitary survey shall be
maintained by the Authority. For each growing area, the central file shall include
all data, results, and analyses from:
(a) The sanitary survey;
(b) The triennial reevaluation; and
(c) The annual review.
(4) Wherever possible, the Authority shall provide the necessary
information to Federal, State, or local agencies which have the responsibility to
minimize or eliminate pollution sources identified in the sanitary survey.
(5) The Authority shall maintain a current comprehensive, itemized list
of all growing areas, including maps showing the boundaries and classification of
each shellstock growing area.
B. Sanitary Survey Required.
(1) A sanitary survey shall not be required to classify growing areas as
prohibited. The findings of a sanitary survey, however, may result in a growing
area being classified as prohibited.
(2) A sanitary survey, including the triennial reevaluation when
available, of each growing area shall be required prior to:
(a) The harvest of shellstock for human consumption; and
(b) The classification of a growing area as approved, conditionally
approved, restricted, or conditionally restricted.
C. Sanitary Survey Performance.
(1) A sanitary survey of each growing area shall be performed at least
once every twelve years and shall include the components in §A.(1).
(2) When a written sanitary survey report is not completed, the area
shall be placed in the closed status.
(3) The growing area classification and the supporting data from the
sanitary survey shall be reviewed at least every three years.
(a) This triennial reevaluation shall include:
(i) A review in accordance with §C.(5) and (6) of the water quality samples;
(ii) Documentation of any new pollution sources and an evaluation of their effect on the growing area;
(iii) Reevaluation of all pollution sources, including the sources previously identified in the
sanitary survey, as necessary to fully evaluate any changes in the sanitary conditions of the
growing area. The reevaluation may or may not include a site visit;
(iv) A comprehensive report which analyzes the sanitary survey data and makes a determination that
the existing growing area classification is correct or needs to be revised; and
(v) If the triennial reevaluation determines that conditions have changed based on the information
and data collected during the triennial review and that the growing area classification is incorrect,
immediate action shall be initiated to reclassify the area. If it is determined that an emergency
condition or situation exists, then the growing area will be immediately (within 24 hours) placed
in the closed status.
(b) When a written triennial reevaluation report is not completed,
the Authority shall place the growing area in the closed status.
(4) The triennial reevaluation may include:
(a) Inspection of wastewater treatment plants or collection of
additional effluent samples to determine their impact on the growing area;
(b) Hydrodynamic studies;
(c) Additional field work to determine the actual impact of
pollution sources; and
(d) Collection of additional water samples.
(5) On an annual basis, the sanitary survey shall be updated to reflect
changes in the conditions in the growing area. The annual reevaluation shall
include:
(a) A field observation of the pollution sources which may include:
(i) A drive-through survey;
(ii) Observations made during sample collection; and
(iii) Information from other sources.
(b) Review, at a minimum, of the past year's water quality sample
results by adding the year's sample results to the data base collected in accordance
with the requirements for the bacteriological standards and sample collection
required in §.02;
(c) Review of available inspection reports and effluent samples
collected from pollution sources;
(d) Review of available performance standards for various types of
discharges that impact the growing area; and
(e) A brief report which documents the findings of the annual
reevaluation.
(6) If the annual reevaluation determines that conditions have changed
based on the information and data collected during the annual review and that the
growing area classification is incorrect, immediate action shall be initiated to
reclassify the area. If it is determined that an emergency condition or situation
exists, then the growing area will be immediately (within 24 hours) placed in the
closed status.
D. Shoreline Survey Requirements.
(1) In the shoreline survey for each growing area, the Authority shall:
(a) Identify and evaluate all actual and potential sources of
pollution which may affect the growing area;
(b) Determine the distance from the pollution sources to the
growing area and the impact of each source on the growing area;
(c) Assess the reliability and effectiveness of sewage or other
waste treatment systems;
(d) Determine if poisonous or deleterious substances adversely
affect the growing area; and
(e) Consider the presence of domestic, wild animal or resident and
migrating bird populations for possible adverse effects on growing areas.
(2) The Authority shall assure that the shoreline survey meets the
following minimum requirements:
(a) The boundaries, based on the area topography, of each
shoreline survey area are determined by an in-field investigation which identifies only the
properties with the potential to impact the shellfish waters;
(b) Each shoreline survey area is identified by a unique designation
which results in identification of all data associated with each shoreline survey by
the unique designation;
(c) Each shoreline survey area is investigated and pollution sources
evaluated by qualified, trained personnel; and
(d) Documentation for each pollution source identified by the
Authority as affecting a growing area includes:
(i) The location of the site on a comprehensive map of the
survey area; and
(ii) The determination that the pollution source has a direct
or indirect impact on shellfish waters: and
(e) A written summary of the survey findings.
@.02 Bacteriological Standards.
Note: The NSSP allows for a growing area to be classified using either a total or fecal
coliform standard. The NSSP further allows the application of either standard to
different water bodies within the state. The NSSP also allows for two sample
collection strategies for the application of the total or fecal coliform standard:
adverse pollution condition and systematic random sampling. The 1992 Task Force
II recommended that this portion of the Ordinance be codified in two ways: a total
coliform strategy and a fecal coliform strategy so that the state may choose sampling
plans on a growing area basis. Within each strategy, provisions would appear for use
of both systematic and adverse pollution condition sample collection. The Ordinance
has been recodified in this manner. For maximum flexibility, a state may wish to
adopt the use of both standards and both sampling strategies for each standard.
This codification represents the fecal coliform standards. The total coliform
standards are outlined in Guidance Document A. 1.
A. General. Either the total coliform or fecal coliform standard shall be
applied to a growing area.
B. Water Sample Stations. The Authority shall assure that the number and
location of sampling stations is adequate to effectively evaluate all pollution
sources.
C. Exceptions.
(1) Except for growing areas classified as prohibited, in growing areas
where there are pollution sources having an impact on the water quality, a
minimum of 30 samples, collected under various environmental conditions, shall be
required to classify any growing area not previously classified under §.03.
(2) Except for growing areas classified as prohibited or when the
systematic random sampling standard is applied, in growing areas where there are
no pollution sources having an impact on the water quality, a minimum of 15
samples shall be required to classify any growing area not previously classified
under §.03.
D. Standard for the Approved Classification of Growing Areas in the
Remote Status.
(1) Water Quality. The bacteriological quality of every station in the
growing area shall meet the fecal coliform standard below.
(2) Fecal Coliform Standard for the Remote Status. The fecal coliform
median or geometric mean MPN of the water sample results shall not exceed 14
per 100 ml, and not more than 10 percent of the samples shall exceed an MPN of:
(a) 43 MPN per 100 ml for a 5 tube decimal dilution test; or
(b) 49 MPN per 100 ml for a 3 tube decimal dilution test.
(3) Required Sample Collection.
(a) A minimum of 2 samples shall be collected annually.
(b) A minimum of the most recent 15 samples collected shall be
used to calculate the median or geometric mean and percentage to determine
compliance with the standard established for the approved classification of remote
growing areas.
E. Standard for the Approved Classification of Growing Areas Affected By
Point Sources.
(1) Water Quality. The bacteriological quality of every station in the
growing area shall meet the fecal coliform standard in §E.(2).
(2) Fecal Coliform Standard for Adverse Pollution Conditions. The
fecal coliform median or geometric mean MPN of the water sample results shall
not exceed 14 per 100 ml, and not more than 10 percent of the samples shall
exceed an MPN of;
(a) 43 MPN per 100 ml for a 5 tube decimal dilution test; or
(b) 49 MPN per 100 ml for a 3 tube decimal dilution test.
(3) Required Sample Collection.
(a) A minimum of 5 samples shall be collected annually under
adverse pollution conditions from each sample station in the growing area.
(b) A minimum of the most recent 15 samples collected under
adverse pollution conditions from each sample station shall be used to calculate the
median or geometric mean and percentage to determine compliance with this standard.
(c) Sample station locations shall be adjacent to actual or potential sources of pollution.
F. Standard for the Approved Classification of Growing Areas Affected by Nonpoint Sources.
(1) Exception. If the tidal stage increases the fecal coliform
concentration, the Authority shall use sample results collected during that tidal
stage to classify the area.
(2) Pollution Sources. Growing areas shall be:
(a) Impacted only by randomly occurring, intermittent events; and
(b) Not impacted by discharges from sewage treatment facilities or
combined sewer overflows.
(3) Water Quality. The bacteriological quality of every station
in the growing area shall meet the fecal coliform standard in §E.(2) or §F.(4).
(4) Fecal Coliform Standard for Systematic Random Sampling. The
fecal coliform median or geometric mean MPN of the water sample results shall
not exceed 14 per 100 ml and the estimated 90th percentile shall not exceed an MPN of:
(a) 43 MPN per 100 ml for a 5 tube decimal dilution test; or
(b) 49 MPN per 100 ml for a 3 tube decimal dilution test.
(5) Estimated 90th Percentile. The estimated 90th percentile shall be calculated by:
(a) Calculating the arithmetic mean and standard deviation of the sample
result logarithms (base 10);
(b) Multiplying the standard deviation in (a) by 1.28;
(c) Adding the product from (b) to the arithmetic mean;
(d) Taking the antilog (base 10) of the results in (c) to get the
estimated 90th percentile; and
(e) The MPN values that signify the upper or lower range of
sensitivity of the MPN tests in the 90th percentile calculation shall be increased or
decreased by one significant number.
(6) Required Sample Collection.
(a) Adverse Pollution Condition Standard. The Authority shall
collect samples in the same intensity and frequency as described in §E.(3)for
application of the standard under §E.(2).
(b) Systematic Random Sampling Standard. The requirement for
systematic random sample collection shall be met when:
(i) Sample station locations are adequate to produce the
data to effectively evaluate all nonpoint sources of pollution;
(ii) Sample collection is scheduled sufficiently far in
advance to support random collection with respect to environmental conditions.
Compliance requires that, prior to implementation, the schedule for random sampling
shall be documented in the master file for the growing area, and if conditions at the time
of scheduled sample collection are believed to be hazardous to the safety of the
individuals assigned to collect samples, sample collection shall be rescheduled at a
later date as soon as practical;
(iii) A minimum of 6 random samples shall be collected
annually from each sample station in the growing area; and
(iv) A minimum of the 30 most recent randomly collected
samples from each sample station shall be used to calculate the median or
geometric mean and 90th percentile to determine compliance with this standard.
(c) Transition from Adverse Pollution Condition Standard to
Systematic Random Sampling Standard. If the Authority:
(i) Does not have 30 recent randomly collected sample
results from each station, then the previous 15 samples collected under adverse pollution
conditions may be used with the most recent random samples to meet the minimum
30 sample requirement for a transition period not to exceed three years; and
(ii) Uses the transition period described in (i), as additional
random samples are collected, the random samples shall replace chronologically
the samples collected under adverse pollution conditions (e. g. sample 31 replaces
sample 1).
G. Standard for the Restricted Classification of Growing Areas Affected by
Point Sources and Used as a Shellstock Source for Shellstock Depuration.
(1) Water Quality. The bacteriological quality of every station in the
growing area shall meet the fecal coliform standard in §G.(2).
(2) Fecal Coliform Standard for Adverse Pollution Conditions. The
fecal coliform median or geometric mean MPN of the water sample results shall
not exceed 88 per 100 ml and not more than 10 percent of the samples shall
exceed an MPN of:
(a) 260 MPN per 100 ml for a 5 tube decimal dilution test; or
(b) 300 MPN per 100 ml for a 3 tube decimal dilution test.
(3) Required Sample Collection. Samples shall be collected in
accordance with §E.(3).
H. Standard for the Restricted Classification of Growing Areas Affected by
Nonpoint Sources and Used as a Shellstock Source for Shellstock Depuration.
(1) Exception. If the tidal stage increases the fecal coliform
concentration, the Authority shall use samples collected under that tidal stage to
classify the area.
(2) Pollution Sources. Growing areas shall meet the requirements in
§F.(2).
(3) Water Quality. The bacteriological quality of every sample station
in the growing area shall meet the fecal coliform standard in §G.(2) or §H.(4).
(4) Fecal Coliform Standard for Systematic Random Sampling. The
fecal coliform median or geometric mean MPN of the water sample results shall
not exceed 88 per 100 ml and the estimated 90th percentile shall not exceed a MPN of:
(a) 260 MPN per 100 ml for a five tube decimal dilution test; or
(b) 300 MPN per 100 ml for a three tube decimal dilution test.
(5) Estimated 90th Percentile. The estimated 90th percentile shall be
calculated by the same method described in §F.(5).
(6) Required Sample Collection.
(a) Adverse Pollution Condition Standard. The Authority shall
collect samples in the same intensity and frequency as described in §E.(3) for
application of the standard under §G.(2).
(b) Systematic Random Sampling Standard. The Authority shall collect samples in the same
intensity and frequency, and shall apply the sample results in the manner described
in §F.(6) for the application of the standard under §H.(4).
@.03 Growing Area Classification.
A. General. Each growing area shall be correctly classified as approved,
conditionally approved, restricted, conditionally restricted, or prohibited, as
provided by this Ordinance.
(1) Emergency Conditions. A growing area shall be placed in the closed
status under §.03A.(5) when pollution conditions exist which were not included in
the data base used to classify the area.
(2) Classification of All Growing Areas. All growing areas which:
(a) Are not subjected to a sanitary survey every twelve years shall
be classified as prohibited;
(b) Have a sewage treatment plant outfall or other point source
outfall of public health significance within or adjacent to the growing area shall
have an area in the prohibited classification established adjacent to the outfall in
accordance with §E. Prohibited Classification; and
(c) Are subjected to a sanitary survey shall be correctly classified
based on the twelve year sanitary survey, and its most recent triennial or annual
reevaluation when available, as only one of the following:
(i) Approved;
(ii) Conditionally Approved;
(iii) Restricted;
(iv) Conditionally Restricted; or
(v) Prohibited.
(3) Boundaries. The boundaries of each classified growing area shall
be delineated on charts which are:
(a) Of sufficient scale and detail so as to adequately describe the
boundaries; and
(b) Maintained in the central file by the Authority.
(4) Revision of Classifications.
(a) Any upward revision of a growing area classification shall be
supported by an adequate sanitary survey.
(b) The appropriate FDA regional office shall be notified of any
revision in growing area classification.
(5) Status of Growing Areas. The status of a growing area is separate
and distinct from its classification and may be either open or closed for the
harvesting of shellstock.
(a) Open Status. Except for an area in the prohibited classification,
any correctly classified growing area, is normally open for the purposes of
harvesting shellstock, subject to the limitations of its classification.
(b) Closed Status. Any classified growing area may be closed for a
limited or temporary period because of:
(i) An emergency condition or situation;
(ii) The presence of biotoxins in concentrations of public
health significance; or
(iii) Conditions stipulated in the management plan of
conditionally approved or conditionally restricted areas; or
(iv) Failure of the Authority to complete a written sanitary
survey or triennial review evaluation report.
(c) Reopened Status. A growing area temporarily placed in the
closed status as provided in (b) above, shall be returned to the open status only when:
(i) The emergency situation or condition has returned to
normal and sufficient time has elapsed to allow the shellstock to reduce pathogens or
poisonous or deleterious substances that may be present in the shellstock to
acceptable levels. Studies establishing sufficient elapsed time shall document the
interval necessary for reduction of contaminant levels in the shellstock to pre-closure
levels. In addressing pathogen concerns, the study may establish criteria
for reopening based on colifiorm levels in the water; or
(ii) The requirements for biotoxins or conditional area
management plans as established in §.04 and §.03, respectively, are met; and
(iii) Supporting information is documented by a written
record in the central file.
(d) Remote Status. A growing area may be placed in the remote
status if:
(i) A sanitary survey determines that the area has no human
habitation, and is not impacted by any actual or potential pollution sources; and
(ii) The area is in the approved classification.
(e) Seasonally Remote/ Approved Status. A growing area may be
placed in a seasonally remote/ approved status requiring two water samples per
year if the following criteria are met:
(i) The area is initially classified as approved;
(ii) The closure time period is defined; and
(iii) At least one sample be taken upon reopening the area.
B. Approved Classification. Growing areas shall be classified as approved
when the following criteria are met.
(1) Survey Required. A sanitary survey finds that the area is:
(a) Safe for the direct marketing of shellfish;
(b) Not subject to contamination from human or animal fecal matter at levels that, in the judgement
of the Authority, presents an actual or potential public health hazard; and
(c) Not contaminated with:
(i) Pathogenic organisms;
(ii) Poisonous or deleterious substances;
(iii) Marine biotoxins; or
(iv) Bacteria concentrations exceeding the bacteriological
standards for a growing area in this classification.
(2) Water Quality. The water quality in the growing area shall meet the
bacteriological standards for an approved classification in §.02.
C. Conditional Classifications. Growing areas may be classified as
conditional when the following criteria are met:
(1) Survey Required. The sanitary survey meets the following criteria:
(a) The area will be in the open status of the conditional
classification for a reasonable period of time. The factors determining this period
are known, are predictable, and are not so complex as to preclude a reasonable
management approach;
(b) Each potential source of pollution that may adversely affect the
growing area is evaluated;
(c) Bacteriological water quality correlates with environmental
conditions or other factors affecting the distribution of pollutants into the growing
area.
(2) Management Plan Required. For each growing area, a written
management plan shall be developed and shall include:
(a) For management plans based on wastewater treatment plant
function, performance standards that include:
(i) Peak effluent flow, average flow, and infiltration flow;
(ii) Bacteriological quality of the effluent;
(iii) Physical and chemical quality of the effluent;
(iv) Conditions which cause plant failure;
(v) Plant or collection system bypasses;
(vi) Design, construction, and maintenance to minimize
mechanical failure or overloading;
(vii) Provisions for monitoring and inspecting the waste
water treatment plant; and
(viii) Establishment of an area in the prohibited classification adjacent
to a wastewater treatment plant outfall in accordance with §E.
Prohibited Classification;
(b) For management plans based on pollution sources other than
waste water treatment plants:
(i) Performance standards that reliably predict when criteria
for conditional classification are met; and
(ii) Discussion and data supporting the performance
standards.
(c) For management plans based on wastewater treatment plant
function or pollution sources other than wastewater treatment plants, criteria that
reliably predict when an area that was placed in the closed status because of failure
to comply with its conditional management plan can be returned to the open status.
The minimum criteria are:
(i) Performance standards of the plan are fully met;
(ii) Sufficient time has elapsed to allow the water quality in
the growing area to return to acceptable levels;
(iii) Sufficient time has elapsed to allow the shellstock to
reduce pathogens that might be present to acceptable levels. Studies establishing
sufficient elapsed time shall document the interval necessary for reduction of coliform
levels in the shellstock to pre-closure levels. The study may establish criteria for
reopening based on coliform levels in the water; and
(iv) Shellstock feeding activity is sufficient to achieve
coliform reduction.
(d) For management plans based on a risk assessment made in
accordance with Chapter II, Risk Assessment and Risk Management, criteria that
reliably determine when the growing area may be placed in the open status and
shellfish may be harvested;
(e) For management systems based on marine biotoxins, the
procedures and criteria that reliably determine when the growing area may be
placed in the open status;
(f) Procedures for immediate notification to the Authority when
performance standards or criteria are not met;
(g) Provisions for patrol to prevent illegal harvest; and
(h) Procedures to immediately place the growing area in the closed
status in 24 hours or less when the criteria established in the management plan are
not met.
(3) Reevaluation of Conditional Classification.
(a) The classification shall be reevaluated at least once each year.
The reevaluation shall include:
(i) Evaluation of compliance with the management plan;
(ii) Determination of adequacy of reporting of failure to
meet performance standards;
(iii) Review of the cooperation of the persons involved;
(iv) Evaluation of water quality in the growing area with
respect to the bacteriological standards for its classification;
(v) Field inspection of critical pollution sources, where
necessary; and
(vi) Written findings, evaluations and recommendations.
(b) Water Sample Collection.
(i) When the conditional management plan is based on the
absence of pollution from marinas for certain times of the year, monthly water
samples are not required when the growing area is in the open status of its
conditional classification provided that at least three of the water samples collected
to satisfy the bacteriological standard for the open status are collected when the
growing area is in the open status.
(ii) When the conditional management plan is based on the
operation and performance of a wastewater treatment plant(s); combined sewer
overflow(s); or other point sources of pollution, monthly water samples are required
when the growing area is in the open status of its conditional classification.
(iii) If a monthly sample cannot be collected due to
environmental constraints, the monthly sampling requirement will be satisfied if an
additional water sampling run is conducted the following month.
(iv) When the conditional management plan is based on
the effects of non-point sources of pollution, such as rainfall events, stormwater runoff,
and seasonal variations, a minimum of five (5) sets of water samples (when the Adverse
Pollution Condition sampling regimen is used) or six (6) sets of water samples (when the
Systematic Random Sampling regimen is used) are required. The samples shall be
collected when the growing area is in the open status.
(4) Understanding of and Agreement With the Purpose of the
Conditional Classification and Conditions of Its Management Plan by All Parties
Involved.
(a) The management plan shall be developed by the Authority in
coordination with:
(i) The local shellfish industry;
(ii) The individuals responsible for the operation of any wastewater
treatment plants involved; and
(iii) Any local or State agencies; and
(b) Failure of any one party to agree shall constitute sufficient
justification to deny the application of the conditional classification to a growing
area.
(5) Conditional Area Types. There are two types of conditional areas:
(a) Conditionally approved; and
(b) Conditionally restricted.
(6) Conditionally Approved Classification. Any growing area in the
conditionally approved classification shall:
(a) Meet the requirements for:
(i) An approved area classification when the conditionally
approved classification is in the open status; and
(ii) A restricted or prohibited classification when the
conditionally approved classification is in the closed status; and
(b) If the closed status meets the criteria for the restricted
classification, designate in its management plan whether the shellstock may be
harvested for relaying or depuration.
(7) Conditionally Restricted Classification. Any growing area in the
conditionally restricted classification shall:
(a) Meet the requirements for:
(i) A restricted classification when the conditionally
restricted classification is in the open status; and
(ii) A prohibited classification when the conditionally
restricted classification is in the closed status; and
(b) Designate in its management plan whether the harvested
shellstock are to be relayed or depurated.
D. Restricted Classification.
(1) General.
(a) A growing area may be classified as restricted when:
(i) A sanitary survey indicates a limited degree of
pollution; and
(ii) Levels of fecal pollution, human pathogens, or
poisonous or deleterious substances are at such levels that shellstock
can be made safe for human consumption by either relaying, depuration
or low acid-canned food processing.
(b) The Authority shall have effective controls to assure that
shellfish are harvested from restricted areas only:
(i) By special license; and
(ii) Under the supervision of the Authority.
(2) Water Quality. Water quality in the growing area shall meet the
bacteriological standards in §.02 for a growing area in the restricted classification
if the growing area is used for depuration.
(3) Shellstock Quality Criteria. The Authority shall establish shellstock
quality criteria for use in placing an area in the restricted classification. Depending
on the treatment process to be applied to the shellstock, the criteria shall be
established in accordance with:
(a) Chapter V. Shellstock Relaying; or
(b) Chapter XV. Depuration.
E. Prohibited Classification.
(1) Exception. The prohibited classification is not required for harvest
waters within or adjacent to marinas. The Authority, however, may use the
prohibited classification for these waters.
(2) General. Except for the harvest of shellstock for the gathering of
seed for aquaculture or the depletion of the areas classified as prohibited, the
Authority shall:
(a) Not permit the harvest of shellstock from any area classified as
prohibited; and
(b) Ensure that shellstock removed from any growing area
classified as prohibited is effectively excluded from human consumption.
(3) Sanitary Survey. A growing area shall be classified as prohibited if:
(a) No current sanitary survey exists;
(b) A sanitary survey determines:
(i) The growing area is adjacent to a sewage treatment plant
outfall or other point source outfall with public health significance;
(ii) Pollution sources may unpredictably contaminate the
growing area;
(iii) The growing area is contaminated with fecal waste so
that the shellfish may be vectors for disease microorganisms;
(iv) The concentration of biotoxin is sufficient to cause a
public health risk as identified in §.04. or
(v) The area is contaminated with poisonous or deleterious
substances causing the shellfish to be adulterated.
(4) Risk Assessment. A growing area shall be classified as prohibited if
a risk assessment performed in accordance with Chapter II, Risk Assessment and
Risk Management indicates the shellstock are not safe for human consumption.
(5) Wastewater Discharges.
(a) An area classified as prohibited shall be established adjacent to
each sewage treatment plant outfall or any other point source outfall of public
health significance.
(b) The determination of the size of the area to be classified as
prohibited adjacent to each outfall shall include the following minimum criteria:
(i) The volume flow rate, location of discharge,
performance of the wastewater treatment plant and the bacteriological quality of the effluent;
(ii) The decay rate of the contaminants of public health
significance in the wastewater discharged;
(iii) The wastewater's dispersion and dilution, and the time
of waste transport to the area where shellstock may be harvested; and
(iv) The location of the shellfish resources, classification of
adjacent waters and identifiable landmarks or boundaries.
@.04 Marine Biotoxin Control.
A. Contingency Plan.
(1) The Authority shall develop and adopt a marine biotoxin
contingency plan for all marine and estuarine shellfish growing areas.
(2) The plan shall define the administrative procedures and resources
necessary to accomplish the following:
(a) Initiate an emergency shellfish sampling and assay program;
(b) Close growing areas and embargo shellfish;
(c) Prevent harvesting of contaminated species;
(d) Provide for product recall;
(e) Disseminate information on the occurrences of toxic algal
blooms and/ or toxicity in shellfish meats to adjacent states, shellfish
industry, and local health agencies; and
(f) Coordinate control actions taken by Authorities and federal agencies.
(3) Except that the Authority shall classify as prohibited any growing
areas where shellfish are so highly or frequently affected by marine biotoxins that
the situation cannot be safety managed, the presence of marine biotoxins shall not
affect the classification of the shellfish growing area under §.03. The Authority
may use the conditionally approved classification for areas affected by marine
biotoxins.
(4) The plan may include agreements or memoranda of understanding,
between the Authority and individual shellfish harvesters, to allow harvesting in
designated parts of a growing area while other parts of the growing area are placed
in the closed status. Such controlled harvesting shall be conducted with strict
assurances of safety, such as by batch release of shellfish lots only after samples of
each lot are tested and found to be below the action levels specified in §C.
B. Marine Biotoxin Monitoring. In those areas where marine biotoxins are
likely to occur in shellfish, representative samples of shellfish shall be collected
during all harvest periods. Samples shall be collected from indicator stations at
intervals determined by the Authority, and assayed for the presence of toxins in
accordance with §C.
C. Closed Status of Growing Areas.
(1) A growing area, or portion(s) thereof as provided in §A.(4), shall
be placed in the closed status for the taking of shellstock when the Authority
determines that the level of biotoxin present in shellfish meats is sufficient to cause
a health risk. The closed status shall be established based on the following criteria:
(a) The concentration of paralytic shellfish poison (PSP) equals or
exceeds 80 micrograms per 100 grams of edible portion of raw shellfish; or
(b) For neurotoxic shellfish poisoning (NSP), the harvesting of
shellstock shall not be allowed when:
(i) Any NSP toxin is found in shellfish meats; or
(ii) The cell counts for Gymnodinium breve organisms in
the water column exceed 5,000 per liter; or
(c) For domoic acid, the toxin concentration shall not be equal to
or exceed 20 ppm in the edible portion of raw shellfish.
(2) For any marine biotoxin producing organism for which criteria have
not been established under this Ordinance, either cell counts in the water column
or biotoxin meat concentrations may be used by the Authority as the criteria for
not allowing the harvest of shellstock.
(3) When sufficient data exist to establish that certain shellfish species
can be safely exempted from the marine biotoxin contingency plan, the closed
status for harvesting may be applied selectively to some shellfish species and not
others.
(4) The closed status shall remain in effect until the Authority has data
to show that the toxin content of the shellfish in the growing area is below the level
established for closing the area.
(5) The determination to return a growing area to the open status shall
consider whether toxin levels in the shellfish from adjacent areas are declining.
(6) The analysis upon which a decision to return a growing area to the
open status is based shall be adequately documented.
D. Heat Processing. If heat processing is practiced, a control procedure
shall be developed. This procedure shall define the following:
(1) Toxicity limits for processing;
(2) Controls for harvesting and transporting the shellstock to
processor;
(3) Special marking for unprocessed shellstock;
(4) Scheduled processes; and
(5) End product controls on the processed shellfish.
E. Records. The Authority shall maintain a copy of all of the following
records:
(1) All information, including monitoring data, relating to the levels of
marine biotoxins in the shellfish growing areas;
(2) Copies of notices placing growing areas in the closed status;
(3) Evaluation reports; and
(4) Copies of notices returning growing areas to the open status.
@.05 Marinas.
A. Marina Proper. The area within any marina which is in or adjacent to a
shellstock growing area shall be classified as:
(1) Conditionally approved;
(2) Conditionally restricted; or
(3) Prohibited.
B. Adjacent Waters. Waters adjacent to marina waters classified under §A.
may be impacted by pollution associated with the marina.
(1) A dilution analysis shall be used to determine if there is any impact to
adjacent waters.
(2) The dilution analysis shall be based on the volume of water in the
vicinity of the marina.
(3) The dilution analysis shall incorporate the following:
(a) A slip occupancy rate for the marina;
(b) An actual or assumed rate of boats which will discharge
untreated waste;
(c) An occupancy per boat rate (i.e., number of persons per boat);
(d) A fecal coliform discharge rate of 2 x 10 fecal coliform per 9
person per day; and
(e) The assumption that the wastes are completely mixed in the
volume of water in and around the marina.
(4) If the dilution analysis predicts a theoretical fecal coliform loading
greater than 14 fecal coliform MPN per 100 ml, the waters adjacent to the marina
shall be classified as:
(a) Conditionally approved;
(b) Restricted;
(c) Conditionally restricted; or
(d) Prohibited.
(5) If the dilution analyses predicts a theoretical fecal coliform loading
less than or equal to 14 fecal coliform MPN per 100 ml, the waters adjacent to the marina
may be classified as:
(a) Approved; or
(b) Conditionally approved.
(6) If the Authority chooses not to determine a specific occupancy per
boat rate by investigation in specific areas or sites, the Authority shall assume a
minimum occupancy rate of two persons per boat.
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Hypertext updated by dav/ear 2006-OCT-05