Current through Register Vol. 56, No. 18, September 16, 2024
(a) The laboratory shall
develop and keep current a quality assurance/quality control manual. The laboratory
shall not perform analyses of regulatory samples without having a current quality
assurance/quality control manual covering the analysis in question. In the manual,
the laboratory shall describe the following:
1.
The procedures that the laboratory will use in meeting the quality control
requirements of this subchapter, N.J.A.C. 7:18-3, and all applicable DSAMs,
including, but not limited to, requirements pertaining to laboratory equipment,
instrumentation and supplies; and
2. The
frequency with which the laboratory will perform the procedures listed pursuant to
(a)1 above.
(b) The
laboratory shall develop and implement a written methods manual containing a
standard operating procedure (SOP) for each DSAM, in accordance with the criteria
and procedures of the DSAM and this chapter. A laboratory shall not perform analyses
using a DSAM unless it has developed and implemented such an SOP for the DSAM.
1. The laboratory shall update the manual to
reflect any changes in the procedures practiced by the laboratory.
2. The laboratory shall keep copies of the methods
manual in the immediate bench area of personnel engaged in the analysis of samples
and related procedures within the chemical testing Categories.
3. In the manual, the laboratory shall properly
designate by revision number and date the standard operating procedure (SOP) for a
specified analytical method for a particular type of analysis.
4. Changes to SOPs are effective only if:
i. The change is made by the manager, supervisor
or quality assurance officer of the laboratory; and
ii. The manager, supervisor or quality assurance
officer makes the change in writing, signed and dated by the manager, supervisor or
quality assurance officer.
5.
The laboratory shall make manufacturers' instruction manuals and any applicable
regulations readily available to laboratory personnel at all times. Textbooks may be
used to supplement written instructions, but shall not be used in lieu
thereof.
(c) A laboratory
performing chemical testing shall conduct the quality control checks specified in
the applicable DSAMs, and the following additional checks:
1. The laboratory shall calibrate dissolved oxygen
instruments against air or air saturated water before each use or weekly, whichever
is less frequent. The laboratory shall test dissolved oxygen instruments weekly
using the Winkler method (azide modification) 4500-OC set forth in SM-18 or ASTM
method D88-92(A), or another Winkler method promulgated by the USEPA.
2. The laboratory shall calibrate standards
incorporated in visual comparison devices at least once every six months. The
laboratory shall maintain records of the date and method of each such calibration in
accordance with 7:18-5.6. The laboratory shall prepare
visual calibration standards according to the applicable DSAM. The laboratory shall
plot concentrations of the calibration standards against those of the incorporated
standards, and calculate a correction factor. The laboratory shall document this
correction factor and apply it to all future results until the factor is
redetermined at the next six-month interval;
3. The laboratory shall check the wavelength
setting of each spectrophotometer at least annually, by comparing the wavelength
setting to the absorption maxima of colored standards or filters such as didymium
glass. For each check, the laboratory shall record in a log book the date on which
it performed the check, the wavelength observed, and the correction factor. The
record shall include the analyst's signature;
4. The laboratory shall prepare calibration curves
used in the spectrophotometric analysis and ion-selective electrode analysis of
inorganic parameters as follows:
i. When using new
calibration standards or quarterly, the laboratory shall prepare new calibration
curves consisting of at least one reagent blank and five standards. The calibration
coefficient shall be [GREATER THAN] 0.995.
ii. The laboratory shall verify the calibration
curve with the calibration check standard daily or after every 20 samples, whichever
is more frequent. For analyses under the Drinking Water Program, the laboratory
shall use a calibration check standard with a concentration at or near the maximum
contaminant level (MCL). For analyses under other regulatory programs, the
laboratory shall use a calibration check standard with a concentration at or near
the middle of the concentration range of the calibration curve. If the applicable
DSAM does not specify the permitted deviation, a verification is satisfactory only
if the concentration as determined from the calibration curve is within a percent
difference (PD) of 10 percent of the true concentration of the calibration check
standard. If the PD is greater than 10 percent, the laboratory shall prepare a new
calibration curve.
iii. The laboratory
shall record all data used in determining the calibration curve, and have the record
signed by the analyst. In the record, the laboratory shall include the date of
calibration, identification and concentration standards;
5. The laboratory shall prepare calibration curves
used in the analysis of metal parameters in Categories DW06, DW07, DW13, NPW07,
NPW08, NPW16, SCM06, SCM07, SCM14, AE02, AE06, BT03, BT04, and BT08. When the
laboratory uses computer-controlled equipment, the laboratory shall follow the
requirements for calibration curves in (c)4 above, except that a minimum of one
reagent blank and three standards shall be required, and the laboratory shall follow
the manufacturer's instructions for calibrating the instrument and shall verify the
calibration curve with two calibration check standards, one at the low end of the
concentration range and the other at the high end;
6. The laboratory shall analyze blanks at the
frequencies required by the applicable DSAM. For methods used in categories AE01,
AE02, AE03, AE04, and AE06 that do not address method blank requirements, method
blanks shall be performed at a frequency of at least one per batch of 20
environmental samples or less per sample preparation method, or at least once each
day of instrument operation, whichever is more frequent. If the method blank result
is greater than the detection limit and contributes greater than 10 percent of the
total amount of analyte found in the sample, the source of contamination must be
investigated and measures taken to eliminate the source of the contamination. If
contamination is found, the data shall be qualified in the report;
7. For parameters in Categories DW03, DW05-DW07,
DW13, NPW03, NPW05, NPW07-NPW08, NPW16, SCM03-SCM04, SCM06-SCM07, SCM14, AE01-AE04,
AE06, BT01, BT03-BT04, and BT08, the laboratory shall conduct quality control (QC)
check sample analyses to verify the accuracy of the analytical system for the
parameter. For each QC check sample analysis, the laboratory shall record the
results of the analysis, the date on which the verification analysis was performed,
and the method of verification. The laboratory shall have the analyst who performed
the analysis sign the record.
i. If the laboratory
analyzes 20 or more samples in a calendar month, it shall analyze one QC sample for
every 20 samples analyzed during the month. If the laboratory analyzes fewer than 20
samples in a calendar month, it shall analyze one QC sample during the
month;
ii. The laboratory shall
calculate the percent recovery (% R) for each parameter in the QC sample. The % R
shall be within the limits listed in the applicable DSAM. If the applicable DSAM
does not list such limits, the laboratory shall calculate such limits from its
experimental data, using the procedure in (c)9 below. If the % R is not within three
standard deviations of the limits, the laboratory shall re-analyze the samples in
question; and
iii. For categories
AE01-AE04 and AE06, if a spiking solution is not available, a calibration solution,
whose concentration approximates that of the samples, shall be included in each
batch and with each lot of media. If a calibration solution must be used for the QC
sample, the client will be notified prior to the start of analysis. The
concentration of the QC sample shall be relevant to the intended use of the data and
either at a regulatory limit or below it.
8. In all cases, the laboratory shall conduct
matrix spike and matrix spike duplicate sample analyses to verify the accuracy and
precision of the DSAM for the applicable parameters in the Categories DW03, DW05-07,
DW13, NPW03, NPW05, NPW07-NPW08, NPW16, SCM03-SCM04, SCM06-SCM07, SCM14, AE01-AE04,
AE06, BT01, BT03-BT04, and BT08.
i. The laboratory
shall verify the accuracy and precision of its analyses of parameters in the above
categories. The laboratory shall maintain records of such verifications, signed by
the analyst performing the verification. In the records, the laboratory shall
include the date on which it performed the verification, the method of verification,
and the results;
ii. If the laboratory
analyzes 20 or more samples for any one parameter in a calendar month, it shall
verify the accuracy and precision of such analyses on at least one of every 20
samples analyzed during the month. If the laboratory analyzes fewer than 20 samples
for any one parameter in a calendar month, it shall verify the precision of the
analysis once a month;
iii. The
laboratory shall calculate the percent recovery (% R) for each matrix spike and the
relative percent difference (RPD) between the matrix spike and matrix spike
duplicate for each parameter. The % R and RPD shall meet requirements of the
applicable DSAM. If the method does not list limits for % R and RPD values, the
laboratory shall establish these limits from its experimental data, using the
procedure in (c)9 below;
iv. For
categories AE01-AE04, and AE06, matrix spikes and matrix spike duplicates are not
required for those air samples that are introduced directly into an analytical
instrument from SUMMA sampling canisters, sorbent tubes, or polyurethane foam (PUF)
traps.
9. In all cases, the
laboratory shall calculate and document standard deviations for all applicable
measurements conducted in Categories DW03, DW05-07, DW13, NPW03, NPW05, NPW07-NPW08,
NPW16, SCM03-SCM04, SCM06-SCM07, SCM14, AE01-AE04, AE06, BT01, BT03-BT04, and BT08,
in accordance with the following requirements:
i.
The laboratory shall calculate standard deviations for n-1 degrees of freedom (n
samples - 1) for all % R and RPD measurements in (c)7 and 8 above. For this
calculation in connection with (c)7 above, the laboratory shall use ongoing data
collected from the analysis of 10 QC samples; for this calculation in connection
with (c)8 above, the laboratory shall use ongoing data collected from the analysis
of 10 matrix, matrix spike pairs. For parameters in Category DW03 and DW05-DW07, the
laboratory shall use samples that have been prepared at the MCL. For other
parameters, the laboratory shall use samples that have been prepared to approximate
the middle of the concentration range normally encountered in the analysis. The
laboratory shall record the theoretical or true value. The laboratory shall
calculate and plot the mean value, the warning limits (two standard deviations), and
the corrective action limits (three standard deviations); and
ii. The laboratory shall record subsequent quality
control results for each parameter, and compare the results against its control
limits. The control limits shall be updated after a batch of 20 new
measurements.
10. A certified
environmental laboratory or a laboratory that is applying for certification shall
determine its own MDLs in reagent water. MDL data are required for all DSAMs
containing reference MDL data for which the laboratory possesses or is applying for
certification. The laboratory shall make the MDL determinations in accordance with
40 CFR 136 Appendix B. The Office of Quality Assurance may require the laboratory to
determine MDLs for any DSAMs for which it possesses certification. This data is
required to support Water Technical Programs N.J.A.C. 7:9-4 and 6:
i. For analyses in the Clean Air Program, the
laboratory shall utilize a test method that provides a detection limit that is
appropriate and relevant for the intended use of the data. Detection limits shall be
determined by the protocol in the mandated test method or in accordance with 40 CFR
Part 136, Appendix B. If the protocol for determining detection limits is not
specified, the selection of the procedure shall reflect instrument limitations and
the intended application of the test method. A detection limit study is not required
for any component for which spiking solutions are not available. All procedures
shall be documented. Documentation shall include the matrix type. All supporting
data shall be retained. The laboratory shall have established procedures to tie
detection limits with quantitation limits.
11. A certified environmental laboratory shall
determine its MDL data (as stated in (c)10 above) annually. All regulatory sample
data except CERCLA CLP shall include the most recent MDL values determined by the
laboratory;
12. The laboratory shall
maintain a permanent maintenance record containing the following information for
each instrument:
i. The date of instrument
installation;
ii. The date and a
description of repairs, modifications, and preventive maintenance;
iii. The signature of the person performing the
maintenance; and
iv. Chromatographic
column information and installation date.
13. The laboratory shall maintain a bound notebook
containing records of the preparation of standards. The laboratory shall include the
following information in the records:
i. The
manufacturer's name and lot number of reagent, date received, percent purity, name
of chemical, concentrations if a solution;
ii. The identification number of the concentrated
stock standard solution, date of preparation, expiration date, signature of the
analyst who prepared the solution, all chemical compounds in the solution, purity,
gross weight, tare weight, net weight, adjusted net weight (corrected for purity of
primary standard) (only net weight and adjusted net weight are required when using
balances with automatic tare features), dilution volume, and concentration in
specified units;
iii. The identification
number of the intermediate concentration standard solution (if needed), date of
preparation, expiration date, signature of the analyst who prepared the solution,
all chemical compounds in the solution, identification number of the concentrated
stock, strength of concentrated stock, aliquot of concentrated stock, dilution
volume, and final concentration in specified units; and
iv. The identification number of the working
standard solution, date of preparation, expiration date, signature of the analyst
who prepared the solution, all chemical compounds in the solution, identification
number of the intermediate concentration standards, concentration of intermediate
standards, aliquot volumes, dilution volumes, and final concentrations in specified
units.