N.J. Admin. Code § 7:18-7.6 - Calculating, analyzing, and reporting of quantal test results
(a) A toxicity
test is invalid if any of the conditions listed in (a)1 through 5 below occurs.
When a toxicity test is invalidated, the laboratory shall clearly mark the test
results accordingly. The laboratory shall submit the results to the Department,
along with a written explanation as to the reason for the invalidation and the
expected date that the test will be repeated. If a toxicity test is
invalidated, the laboratory shall repeat the test as soon as possible within
the monitoring period specified in the permit. A toxicity test is invalid if:
1. In an N.M.A.T. or N.O.A.E.C. test,
mortality of the control test organisms exceeds 10 percent;
2. In tests determining either an EC[50] or
an LC[50], greater than 10 percent of the control test organisms either show
the effect or exhibit mortality;
3.
In definitive tests determining an LC[50] or an EC[50], after pooling replicate
test chamber responses two or more test concentrations deviate significantly
from the expected trend of increasing effluent concentrations exhibiting
increasing levels of toxicity. Deviation in response from the expected trend of
greater than 10 percent (mortality for an LC[50], or effect for an EC[50])
shall be considered to be significant;
4. The 95 percent confidence limits cannot be
calculated for a test which results in an LC[50] or EC[50] that is either less
than the highest effluent concentration tested, or greater than the lowest
effluent concentration tested. However, the test need not be invalidated if the
calculated LC[50] or EC[50] lower confidence limit is ≥30 percent of the
highest effluent concentration tested and the upper confidence limit is a
positive infinity; or
5. The
laboratory is unable to calculate 95 percent confidence limits when required
under (b)4ii below.
(b)
A laboratory shall satisfy the requirements of (b)1 through 6 below when
calculating toxicity test results.
1. The
laboratory shall not use biological test results from N.M.A.T. definitive acute
toxicity tests to calculate an LC[50] or EC[50]. For all effluent
concentrations and the control, the laboratory shall report the number and
percentage of dead test organisms or those showing the effect.
2. The laboratory shall express the
biological test results from range-finding acute toxicity tests in terms of an
LC[50] or EC[50] whenever the data support the estimation. The laboratory shall
estimate the LC[50] or EC[50] by the graphical method described in EPA Acute
Methods #027F-1993.
i. When the highest
effluent concentration kills or affects less than 50 percent of the test
organisms, the laboratory shall record the number of organisms showing the
response in each treatment; and
ii.
When the lowest concentration kills or affects more than 80 percent of the test
organisms, the laboratory shall repeat the range-finding test with a lower set
of effluent concentrations, before conducting the definitive toxicity
test.
3. The laboratory
shall express the biological test results from definitive acute toxicity tests
in terms of an estimated LC[50] or EC[50], except when no toxicity is observed.
The laboratory shall report the numbers and percentages of test organisms dying
(for LC[50]) or showing the effect (for EC[50]) for each test chamber.
i. When more than 50 percent of the test
organisms die (for LC[50]) or show the effect (for EC[50]) in the lowest
effluent concentration, the laboratory shall report an LC[50] or EC[50] of less
than the lowest concentration;
ii.
When less than 50 percent of the test organisms die (for LC[50]) or show the
effect (for EC[50]) in the highest effluent concentration, the laboratory shall
report an LC[50] or EC[50] of greater than the highest concentration;
4. When the results of a
definitive acute toxicity test falls between the two extremes given in (b)3i
and ii above, the laboratory shall calculate LC[50] or EC[50] values using the
following methods and procedures.
i. The
laboratory shall calculate LC[50] or EC[50] for at least the final exposure
time and each 24 hour exposure time between the beginning and the end of the
test. For example, in a test with a 96-hour duration, the laboratory would
calculate LC[50] or EC[50] 24, 48, 72 and 96 hours after the beginning of the
test;
ii. The laboratory shall
calculate 95 percent confidence limits for each definitive acute toxicity test
LC[50] or EC[50]. If the laboratory cannot do so, the test shall be invalid in
accordance with (a)5 above. This requirement does not apply to any toxicity
test that results in an LC[50] or EC[50] that has:
(1) Greater than or equal to the highest
effluent concentration tested; or
(2) Less than or equal to the lowest effluent
concentration tested; or
(3) No
partial mortalities.
iii. If any acute toxicity test results in no
partial mortalities, the LC[50] or EC[50] is determined using the Graphical
Method as described in EPA Acute Methods #027F-1993;
iv. If any acute toxicity test results in two
or more partial mortalities and a non-significant Chi Square Test, the LC[50]
or EC[50] and corresponding 95% confidence intervals are determined using the
Probit Method as described in EPA Acute Methods #027F-1993.
v. The Spearman-Karber Method, as described
in EPA Acute Methods #027F-1993, is used to determine the LC[50] or EC[50] and
corresponding 95 percent confidence intervals for any acute toxicity test if
the following conditions apply:
(1) Zero
mortality in the lowest effluent concentration and 100 percent mortality in the
highest effluent concentration, and;
(2) One partial mortality, or;
(3) Two or more partial mortalities and a
significant Chi Square Test;
vi. If the conditions in (b)4iii, iv, or v do
not apply, the LC[50] or EC[50] and corresponding 95 percent confidence
intervals for any acute toxicity test are determined using the Trimmed
Spearman-Karber Method as described in EPA Acute Methods #027F-1993.
5. Upon completing a definitive
acute toxicity test for which LC[50 ]or EC[50] can be calculated, the
laboratory shall plot a toxicity curve. The laboratory shall plot the curve
using the LC[50] or EC[50] for each observation time, following the methodology
presented in "Standard Methods, 16th Edition" p. 717. The laboratory shall
report any threshold or incipient LC[50] that it can estimate from the curve.
If the laboratory finds no threshold or incipient LC[50], the laboratory shall
report this fact. In either case the laboratory shall include the toxicity
curve graph in the report of results whenever the data permit it to be
plotted.
6. For all effluent
concentrations and the control, the laboratory shall determine the N.O.A.E.C.
using the hypothesis testing as described in section 11.3 of EPA Acute Methods
#027F-1993.
(c) The
laboratory shall follow the following requirements when reporting results of
acute toxicity tests:
1. The laboratory shall
complete a sample report immediately after collecting either dilution water or
effluent samples. The laboratory shall make the report either as a separate
form or as an entry in a bound logbook. The laboratory shall include the sample
report data in its report of the toxicity test results to the Department. The
laboratory shall include the following information in the sample report:
i. The sampling location;
ii. Date and time of collection;
iii. Total residual chlorine level in the
sample;
iv. The type of sample
(composite or grab);
v. The
material sampled;
vi. The
collector's name; and
vii. Any
pertinent comments.
2.
The laboratory shall include the following types of information when reporting
results of an acute toxicity test:
i. The
name of the test, the investigator(s), and the laboratory;
ii. The date on which the test
began;
iii. The name of NJPDES
permittee, its location, its NJPDES permit number, and the Discharge Serial
Number;
iv. The name of the
receiving water body;
v. A detailed
description of the effluent, including the sampling point, date and time of
collection, known physical and chemical properties, and variability;
vi. A detailed description of the dilution
water source, the sample location, the date and time of sample collection, the
tide stage (if applicable), the dilution water chemical characteristics, and
any pretreatment;
vii. A
description of acute toxicity test method(s) used, including:
(1) The test protocol, a definition of the
adverse effect (death, immobility, etc.) used in the test, a description of the
test chambers used (including the depth and volume of test solution), the
number of test organisms per replicate treatment, the number of replicate
treatments, and the loading rate of the test organisms. In flow-through
toxicity tests the report shall also include the number of water volume
exchanges per 24 hours in each test chamber;
(2) Detailed information about the test
organisms, including the scientific name, mean and ranges of length and weight
(where appropriate), age, life stage, source, previous history (if known),
observed disease, treatments (if any), record of acclimation procedure, and
observations on behavior during the test;
(3) A description of any aeration or salinity
adjustments performed on test solutions before or during the test;
(4) The methods used for all chemical
analyses;
(5) The mean and range of
the acclimation temperature, test temperature, and salinity; and
(6) Any deviations from the test
method(s);
viii. The
test results, including the following:
(1) The
results of all chemical analyses of the effluent and dilution water;
(2) A daily record of the number and
percentages of organisms in each test chamber, including the control
treatments, that died or showed the selected effect;
(3) A summary of general observations of
other effects of symptoms of toxicity observed during the test;
(4) The LC[50] or EC[50] value with specified
exposure time and the 95 percent confidence limits. If the highest effluent
concentration did not kill or affect 50 percent or more of the test organisms,
report the LC[50] or EC[50] as greater than the highest concentration and the
percentage of test organisms killed or affected in each experimental treatment.
If the lowest effluent concentration killed or affected more than 50 percent of
the test organisms, report the LC[50] or EC[50] as less than the lowest
concentration and the percentage of test organisms killed or affected in each
experimental treatment. Report the method(s) used to calculate the LC[50] or
EC[50], and its 95 percent confidence limits. Include a graph of the toxicity
curve;
(5) Any deviations from
approved methodology, along with a summary of the reason(s) for the
deviation(s); and
(6) Any other
relevant information; and
ix. Upon completing the toxicity test, the
laboratory shall send the original or true duplicate of the results to the
client. The original or true duplicate shall be signed by the laboratory
manager or a designee identified under
N.J.A.C.
7:18-2.11(a)1
iii.
Notes
See: 28 New Jersey Register 4098(a).
Amended by R.1997 d.192, effective
See: 28 New Jersey Register 4149(a), 29 New Jersey Register 2275(a).
In (a)1, inserted "or N.O.A.E.C."; and added (b)6.
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