Fla. Admin. Code Ann. R. 62-160.120 - Definitions and Standards
For purposes of this chapter:
(1) "Alternative method" is a field procedure
or analytical laboratory method that is intended to be used in place of an
existing Department-approved laboratory method or field procedure that is
specified in a Department rule, permit, order, or contract, as further
discussed in Rules 62-160.220 and
62-160.330, F.A.C.
(2) "Audit" is a systematic review of
laboratory and field protocols to determine if proper procedures are being used
and supporting documentation is present. An audit shall consist of an on-site
assessment of sample collection, field sampling procedures, laboratory
procedures and/or a review, assessment and/or validation of data associated
with a Department program activity. If necessary, an audit shall include the
submission of performance samples (for example, blind, split and/or performance
check samples) to an organization for subsequent use in the evaluation of that
organization's technical performance associated with a specific Department
project or program activity.
(3)
"Commercial Vendor" is a retail or wholesale company whose business is to sell
commodities to customers and who is not a part of the process that generates
environmental data. These businesses do not include organizations that purchase
commodities with the intent of providing the commodities as a service to
clients.
(4) "Common Carrier" is a
business or agency that is available to the general public for the
transportation of goods over a definite route and according to a regular
schedule.
(5) "Data quality
objectives" are a set of qualitative and quantitative statements derived from a
systematic planning process that clarify the purpose of the study, define the
most appropriate type of information to collect, determine the most appropriate
conditions from which to collect that information, and specify tolerable levels
of potential decision errors.
(6)
"Data validation" is an evaluation of the technical usability of the verified
data with respect to the planned objectives or intention of a
project.
(7) "Data verification" is
a consistent, systematic process that determines whether the data have been
collected in accordance with project specifications with respect to compliance,
correctness, consistency and completeness as compared to a method standard or
contract specification.
(8)
"Department" is the Florida Department of Environmental Protection.
(9) "Department-approved method" is a field
procedure or laboratory analytical method specified as acceptable for use in
this chapter and in any other Department contract, order, permit or Title 62
rules.
(10) "Department of Health
(DOH) Environmental Laboratory Certification Program (ELCP)" is the state of
Florida's environmental laboratory certification program, authorized by Section
381.00591, F.S., and recognized
by the National Environmental Laboratory Accreditation Program (NELAP)
Acceditation Council as an authority with responsibility and accountability for
granting accreditation for specified fields of laboratory testing through
Chapter 64E-1, F.A.C.
(11)
"Electronic signature" means an electronic sound, symbol, or process attached
to or logically associated with a record and executed or adopted by a person
with the intent to sign the record.
(12) "Holding time" is the storage time
allowed between sample collection and sample preparation and/or analysis as
specified by regulatory requirements or by the field sample collection protocol
or laboratory method.
(13)
"Limited-use method" is an alternative or modified field or laboratory
procedure that is approved by the Department for the collection or testing of
environmental samples by a single field sampling organization or analytical
laboratory for purposes specified in the scope of the approval (e.g., for
specified analytes, facility or site locations or types, or sample matrices,
such as effluent, groundwater, drinking water, fresh or marine surface waters,
soils, sediments, or chemical wastes). A limited-use method that is validated
and approved by the Department for a field sampling organization or analytical
laboratory may not be used by another field sampling organization or analytical
laboratory. The criteria for the validation and approval of a limited-use
method are further outlined in subparts FA 2100 and FA 2200 of DEP SOP FA 1000,
which is incorporated by reference in subparagraph
62-160.800(1)(a)
1., F.A.C., and outlined in DEP-QA-001/01, which is incorporated by reference
in subsection 62-160.800(5),
F.A.C. Requirements for limited-use methods are further discussed in Rules
62-160.220 and
62-160.330, F.A.C., and must be
met for Department approval.
(14)
"Matrix" is the predominant material in which an analyte of interest is
contained. For example, soil, groundwater and drinking water are three
environmental matrices.
(15)
"Method-defined analyte" is defined by the U.S. Environmental Protection Agency
as an analyte whose result is totally dependent on how the measurement is made.
Any changes or modifications in the preparation or determinative techniques of
these methods have the potential of changing the result, and are not approved
by the Department, as indicated in paragraph
62-160.330(2)(a),
F.A.C. Examples are: Carbonaceous Biological Oxygen Demand, Oil and Grease, and
Toxicity Characteristic Leaching Procedure (TCLP).
(16) "Method detection limit (MDL)" is an
estimate of the minimum amount of a substance that an analytical process can
reliably detect, the minimum measured concentration of a substance that can be
reported with 99% confidence that the measured concentration is distinguishable
from method blank results, or the minimum result that can be reliably
discriminated from a blank with a predetermined confidence level (Limit of
Detection [LOD] as defined in the 2016 TNI Standards, which are incorporated by
reference in paragraph
62-160.800(3)(b),
F.A.C.). The Department accepts any of the preceding definitions of the MDL. An
MDL is analyte-specific and matrix-specific and is laboratory-dependent. The
MDL for an analyte is determined from the preparation and analysis of a sample
in a given matrix containing the analyte. MDLs shall be determined for each
matrix/analytical technology/analyte combination reported by the laboratory,
except for those tests where determination of the MDL is not appropriate for
the analytical technique, such as biochemical oxygen demand, chlorophyll or
microbiological tests. When required according to Department rules, MDLs shall
be calculated following the procedure specified in those rules. If not
specified in Department rules, MDLs may be determined and verified by any
technically justifiable and scientifically sound method appropriate for the
test. For the purposes of data usability evaluation, the DEP-defined MDL is
equivalent to the Limit of Detection (LOD) as defined in the 2016 TNI
Standards, which are incorporated by reference in paragraph
62-160.800(3)(b),
F.A.C.
(17) "Method modification"
is any change that alters the scope, applicability, specifications, steps,
performance criteria, or any other requirements described in a published field
procedure or laboratory analytical method, as further specified in subsections
62-160.220(3)
and 62-160.330(3),
F.A.C. The resultant method is defined by the Department as a "modified
method."
(18) "Field of
Accreditation Matrix" is defined in the Glossary of the 2003 NELAC Standards,
which is incorporated by reference in paragraph
62-160.800(3)(a),
F.A.C., and shall be used to determine matrices under which a laboratory must
be certified by the DOH ELCP for reporting data to be used by the Department:
(a) Drinking Water: any aqueous sample that
has been collected from a water source designated by the Department as a
potable or potential potable water source.
(b) Non-potable Water: any aqueous sample
excluded from the definition of drinking water matrix including surface water,
groundwater, effluents, water treatment chemicals, or samples derived from
synthetic precipitation leaching procedures (SPLP), toxicity characteristic
leaching procedures (TCLP) or other extracts. To be considered as non-potable
water, water treatment chemicals must be in an aqueous solution. If the
laboratory receives the original environmental sample as a solid or chemical
material for SPLP or TCLP extraction, the laboratory must be certified for the
SPLP or TCLP extraction in the Solid and Chemical Material matrix. For the
analytical tests to be performed on the SPLP or TCLP extract, the laboratory
must be certified in the non-potable water matrix for at least one method for
each analytical technology/analyte combination for each reported
analyte.
(c) Solid and Chemical
Materials: includes soils, sediments, sludges, products and by-products of an
industrial process that results in a matrix not previously defined. For
purposes of accreditation, biosolids are considered a solid, unless the sample
matrix comprises liquid biosolids as defined in Chapter 62-640, F.A.C. All
other sample matrices not previously defined and comprising <= 15%
settleable solids are liquids, and may require laboratory certification for
analysis using techniques for non-potable water or liquid chemical
materials.
(d) Biological Tissue:
any sample of a biological origin, such as fish, shellfish, macroinvertebrates,
algae, or plant material.
(19) "National Environmental Laboratory
Accreditation Program (NELAP)" is a program that implements standards that have
been found to be acceptable to the NELAP Accreditation Council.
(20) "NELAP accreditation" is an
accreditation status applied to a laboratory's field(s) of testing upon
satisfying all requirements for certification as provided in Chapter 64E-1,
F.A.C.
(21) "Percent relative
standard deviation (% RSD)" is a calculated measure of precision from results
of replicate sample analyses. It is calculated as specified in DEP-QA-001/01
(January 2017), which is incorporated by reference in Rule
62-160.800, F.A.C.
(22) "Permit" is any permit or license issued
by the Department pursuant to its lawful authority, or by another government
agency under delegation of authority from the Department.
(23) "Practical quantitation limit (PQL)" is
the lowest level of measurement that can be reliably achieved during routine
laboratory operating conditions within specified limits of precision and
accuracy. The value of the PQL shall be greater that the MDL value except when
analytical quality control problems necessitate raising the MDL value equal to
or above the PQL value for a specific sample, or when determination of the MDL
is not appropriate for an analytical technique, as indicated below. A
laboratory may determine and verify the PQL by any technically justifiable d
scientifically sound method appropriate for the test, unless otherwise required
by Department rule, contract, order, or permit. For Departmental use, if a
laboratory fails to report a PQL, the PQL shall be calculated as four times the
MDL, except for those tests where determination of the MDL is not appropriate
for the analytical technique (e.g., biochemical oxygen demand, chlorophyll or
microbiological tests). In such cases, the Department shall use all available
information about the technique to determine the PQL. For the purposes of data
usability evaluation, the DEP-defined PQL is equivalent to the Limit of
Quantitation (LOQ) as defined in the 2016 TNI Standards, which are incorporated
by reference in paragraph
62-160.800(3)(b),
F.A.C.
(24) "Quality assurance" is
an integrated system of management activities involving planning,
implementation, documentation, assessment, reporting and quality improvement to
ensure that a process, product or service meets defined standards of
quality.
(25) "Quality assurance
project plan (QAPP)" is a document required by the EPA for certain activities
conducted for or funded by the EPA. The plan outlines the quality assurance
criteria, as well as all protocols and quality control measures needed to meet
the project data quality objectives. These plans are prepared in accordance
with "EPA Requirements for Quality Assurance Project Plans, EPA QA/R-5, "
(EPA/240/B-01/003 March 2001), which is incorporated by reference in subsection
62-160.800(4),
F.A.C. These QAPPs are reviewed and approved by the appropriate EPA office or
the Department, when delegated to the Department by EPA for specific
activities.
(26) "Quality control"
is the overall system of technical activities that measures the attributes and
performance of a process, product or service against defined standards to
verify that they meet the established data quality objectives.
(27) "Relative percent difference (RPD)" is a
calculated measure used to compare results from duplicate sample analyses. It
is calculated as specified in DEP-QA-001/01 (January 2017), which is
incorporated by reference in Rule
62-160.800, F.A.C.
(28) "Research method" is a field procedure
or analytical laboratory method that involves the evaluation or use of a new,
innovative technology, or as otherwise defined in Rule
62-160.600, F.A.C., and approved
by the Department for research purposes.
(29) "Secondary Use Data" means data that are
being considered for use by the Department for purposes other than that for
which the data were originally generated.
(30) "Spike" is an environmental sample that
has been fortified with a known chemical of interest, at a known concentration.
The purpose of a spike is to determine the method recovery efficiency for the
chemical of interest, at the fortified concentration level, in the particular
environmental sample of interest.
(31) "Statewide-use method" is a modified or
alternative field or laboratory procedure or method that is submitted to and
approved by the Department for the collection or testing of environmental
samples by any field sampling organization or laboratory, as applicable,
according to Rules 62-160.220 and
62-160.330, F.A.C. The criteria
for the validation and approval of a statewide-use method are further outlined
in subparts FA 2100 and FA 2200 of DEP SOP FA 1000, which is incorporated by
reference in subparagraph
62-160.800(1)(a)
1., F.A.C., and outlined in DEP-QA-001/01, which is incorporated by reference
in subsection 62-160.800(5),
F.A.C.
(32) "Surrogate spikes" are
samples fortified at known concentration(s) with one or more compounds having
similar chemical characteristics to the compounds of interest, but which are
not normally found in environmental samples.
Notes
Rulemaking Authority 403.061, 403.0623 FS. Law Implemented 373.026, 373.309, 373.409, 373.413, 373.414, 373.416, 373.4592, 376.303, 376.305, 376.3071, 403.0623, 403.0625, 403.087, 403.088, 403.0881, 403.504, 403.704, 403.707, 403.722, 403.853 FS.
New 1-1-91, Amended 2-4-93, 2-27-94, Formerly 17-160.120, Amended 3-24-96, 4-9-02, 6-8-04, 12-3-08, 7-30-14, 4-16-18.
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