## METHOD 524.4 MEASUREMENT OF PURGEABLE

ORGANIC COMPOUNDS IN WATER

BY GAS CHROMATOGRAPHY/MASS

SPECTROMETRY USING NITROGEN

PURGE GASQuestions concerning this document should be addressed to:

Steven C. Wendelken, PhD
U.S. EPA, OGWDW/SRMD/TSC

, 26 W. Martin Luther King Dr. Cincinnati, OH 45219 Phone: (513) 569

- 7491 wendelken.steve@epa.gov

Office of Water (MS

- 140)

EPA 815

- R

- 13

- 002 May 2013Foreword

This method was prepared under the direction of David J. Munch and Steven C. Wendelken

, PhD of the Technical Support Center within the U.S. EPA Office of Water

. Shaw Environmental Inc. provided

support under EPA contracts EP

- C

- 06

- 031and EP

- C

- 12

- 013. The following are acknowle dged for their support in development of this method:

Tom Hartlein

, Tekmar (Teledyne Technologies, Inc.) Roger Bardsley

, Tekmar (Teled yne Technologies, Inc.) Laura Chambers, OI Analytical John George, Bruker Corporation Yongtao Li, Underwriters Laboratories, Inc. Bill Davis, Underwriters Laboratories, Inc. Dr. Andrew Eaton, Eurofins Eaton Analtyical Kipp Phelan, Eurofins Eaton Analytical524.4

- 1 METHOD 5 24. 4

MEASUREMENT OF PURGEABLE ORGANIC COMPOUNDS IN WATER BY GAS

CHROMATOGRAPHY/MASS SPECTROMETRY USING NITROGEN PURGE GAS

1. SCOPE AND APPLICATION

1.1 This is a gas chromatography/mass spectrometry (GC/MS) method for the determination of

pu rg e able organic compounds in finished drink ing waters. Discontinuous scanning modes

such as selected ion monitoring (SIM) and selected ion storage (SIS) are permitted for determining selected analytes that are monitored at levels too low for the full scan detection

mode. Precision and accu racy data have been generated for the method analytes in reagent

water

, drinking water from a groundwater source and drinking water from a surface water

source . The single laboratory Lowest Concentration Minimum Reporting Level (LCMRL)

has also been determined in reagent water . The following compounds can be determined using this method:

Analyte Chemical Abstract Services Regi stry Number (CASRN)
1,1,1,2

- tetrachloroethane 630

- 20

- 6

1,1,1

- trichloroethane 71

- 55

- 6

1,1,2,2

- tetrachloroethane 79

- 34

- 5

1,1,2

- trichloroethane 79

- 00

- 5

1,1

- dichloroethane 75

- 34

- 3

1,1

- dichloroethene 75

- 35

- 4

1,1

- dichloropropene 563

- 58

- 6

1,2,3

- trichlorobenzene 87

- 61

- 6

1,2,3

- trichloropropane 96

- 18

- 4

1,2,4

- trichlorobenzene 120

- 82

- 1

1,2,4

- trimethylbenzene 95

- 63

- 6

1,2

- dibromo

- 3

- chloropropane 96

- 12

- 8

1,2

- dibromoethane 106

- 93

- 4

1,2

- dichlorobenzene 95

- 50

- 1

1,2

- dichloroethane 107

- 06

- 2

1,2

- dichloropropane 78

- 87

- 5

1,3,5

- trimethylbenzene 108

- 67

- 8

1,3

- butadiene 106

- 99

- 0

1,3

- dichlorobenzene 541

- 73

- 1

1,3

- dichloropropane 142

- 28

- 9

1,4

- dichlorobenzene 106

- 46

- 7

1

- chlorobutane 109

- 69

- 3

2

- chlorotoluene 95

- 49

- 8

4

- chlorotoluene 106

- 43

- 4524.4

- 2 Analyte Chemical Abstract Services Regi stry Number (CASRN)

4

- isopropyltoluene 99

- 87

- 6
allyl chloride 107

- 05

- 1

be nzene 71

- 43

- 2

b romobenzene 108

- 86

- 1

b romochloromethane 74

- 97

- 5

b romodichloromethane 75

- 27

- 4

b romoform 75

- 25

- 2

b romomethane 74

- 83

- 9

carbon disulfide 75

- 15

- 0

carbon tetrachloride 56

- 23

- 5

c hlorobenzene 108

- 90

- 7

c hlorodifluoromethane 75

- 45

- 6

c hloroform 67

- 66

- 3

c hloromethane 74

- 87

- 3

cis

- 1,2

- dichloroethene 156

- 59

- 2

cis

- 1,3

- dichloropropene 10061

- 01

- 5

dibromochloromethane 124

- 48

- 1

d ibromomethane 74

- 95

- 3

dichlorodifluoromethane 75

- 71

- 8
diethyl ether 60

- 29

- 7
diisopropyl ether (DIPE) 108

- 20

- 3
ethyl methacrylate 97

- 63

- 2

e thylbenzene 100

- 41

- 4

h exachlorobutadiene 87

- 68

- 3

h exachloroethane 67

- 72

- 1

i sopropylbenzene 98

- 82

- 8
methyl acetate 79

- 20

- 9
methyl iodide 74

- 88

- 4
methylene chloride 75

- 09

- 2
methyl

- t

- butyl ether (MtBE) 1634

- 04

- 4

m

- xylene 108

- 38

- 3

n aphthalene 91

- 20

- 3

n

- butylbenzene 104

- 51

- 8

n

- propylbenzene 103

- 65

- 1

o

- xylene 95

- 47

- 6

p entachloroethane 76

- 01

- 7

p

- xylene 106

- 42

- 3

sec

- butylbenzene 135

- 98

- 8

s tyrene 100

- 42

- 5

t

- amyl ethyl ether (TAEE) 919

- 94

- 8524.4

- 3 Analyte Chemical Abstract Services Regi stry Number (CASRN)

t

- amyl methyl ether (TAME) 994

- 05

- 8

t

- butyl alcohol (TBA) 75

- 65

- 0

t

- butyl ethyl ether (ETBE) 637

- 92

- 3

t

- butylbenzene 98

- 06

- 6

tetrachloroethene 127

- 18

- 4
tetrahydrofuran 109

- 99

- 9

t oluene 108

- 88

- 3

trans

- 1,2

- dichloroethene 156

- 60

- 5

trans

- 1,3

- dichloropropene 10061

- 02

- 6

trichloroethene 79

- 01

- 6

trichlorofluoromethane 75

- 69

- 4
vinyl chloride 75

- 01

- 4

1.2 The ranges for purge

- and

- trap parameters specified in Section 9.1 are applicable to the use of nitrogen purge gas; helium may not be used

. The mass spectrometry conditions described in this method were developed using a gas chromatograph (GC) interfaced to a quadrupole mass spectrometer (MS).

1.3 The single laboratory LCMRL is the lowest spiking concentration such that the probability of spike recovery in the 50 % to 150% range is at least 99% . Single laboratory LCMRLs for the

ana lytes in this method range d from 0.10 to 0.62 microgram per liter ( μ g/L ) in the full scan

mode ( Table 6 )

. Single laboratory LCMRLs were also determined for selected analytes in the selected ion monitoring (SIM) mode (Table 10 ). The procedure used to determine the

LCMRL is described elsewhere. 1

1.4 Laboratories using this method are not required to determine LCMRL s , but they must
demonstrate that the minimum reporting level ( MRL ) for each analyte meets the requirements

described in Section 9.2.4.

1.5 Detection limit (DL) is defined as the statistically calculated minimum concentration that can be measured with 99% confidence that the reported value is greater than zero

. 2 The DL is dependent on sample matrix, fortification concentration and instru ment performance. Deter

mining the DL for analytes in this method is optional (Sect. 9.2. 6 ). DLs for method analytes

fortified into reagent water range d from 0. 026 to 0. 1 8 μ g/L in the full scan mode

. These

values are presented in Table 6

. DLs were also determined for selected analytes in SIM mode (Table 10 ).

1.6 This method is intended for use by analysts skilled in the technique of purge

- and

- trap
concentration , the operation of GC/MS instrumentation and the interpretation of the

associated data

.

1.7 METHOD FLEXIBILITY

– To accommodate technological advances in analytical instrumentation and techniques, the labora tory is permitted to modify purge

- and

- trap
parameters and the GC/ MS conditions. Because the purge

- and

- trap technique has a significant numb er of analyst

- chosen parameters and because it employs a procedural524.4

- 4 calibration, the authors have determined an acceptable range of purge

- and

- trap conditions that may be used (Sect. 9.1) and a means by which to evaluate method modifications (Sect. 9.4 )

. Changes may not be made to sample collection and preservation (Sect. 8) or to the quality control (QC) requirements (Sect. 9) . Modifications that are introduced solely in the interest of reducing cost or sample processing time, but result in poorer method performance, may not be used. The option to operate the MS in SIM or SIS mode is restricted to analytes that cannot be effectively analyzed in full scan mode, e.g., 1,2

- dibromoethane and 1,2

- dibromo

- 3

- chloropropane. The SIM detection mode should not be used to enhance analyte signal for instrumentation that is not properly optimized and maintained. Compliance monitoring for trihalomethanes (THMs) must be condu cted in the full scan detection mode.

In all cases where allowed method modifications are made , the analyst must perform the procedures outlined in the Initial Demonstration o f Capability (IDC, Sect. 9.2), verify that all QC acceptance criteria i n this method (Tables 1 2 and 1 3 ) are met and verify method

p erformance in real sample matri ces (Sect. 9.4 .4 )

.

N OTE: This description of method flexibility is a brief summary . Additional specific detail is provided throughout the method, which supersedes the above general guidance

.

2. SUMMARY OF METHOD

Headspace

- free samples are collected in amber, glass vials with polytetrafluoroethylene ( P TF E )

- faced septa. Samples are dechlorinated with ascorbic acid and the pH is adjusted with maleic acid

. A 5.0

- milliliter ( mL ) aliquot of the s ample is transferred to a glass sparging vessel along with appropriate amounts of internal standard and quality control compounds . The method analytes are purged from the water using nitrogen and trapped on a sorbent material

. After purging, the trap may be dry purged for a short period to remove water

. The trap is then heated and backflushed with GC carrier gas to trans fer the analytes directly into the gas chromatographic inlet

. T he inlet is operated in the split mode in order to achieve the desired desorb flow rate s and furth e r reduce water

transmission

. A nalyte s are transferred onto a capillary GC column, which is temperature programmed to optimize the separation of method analy tes . Compounds eluting from the GC are directed into a mass spectrometer for detection and quantitation

. The method analytes are identified by comparing the acquired mass spectra and retention times to reference spectra and retention

times

. The concentration of each analyte is calculated using the internal standard technique and

response curves obtained via procedural calibration (Sect. 3.1 8 )

.

3. DEFINITIONS

3.1 A NALYSIS BATCH

– A sequence of samples, analyzed within a 24

- hour period

, including no more than 20 field samples. Each Analysis Batch must also include all re quired QC samples, which do not contribute to the maximum field sample total of 20. The required QC samples include:

Laboratory Reagent Blank (LRB)

, Continuing Calibration Check (CCC) Standards

, Laboratory Fortified Sample Matrix (LFSM) and Laboratory Fortified Sample Matrix Duplicate or Field Duplicate (LFSMD or FD )

.524.4

- 5 3.2 CALIBRATION STANDARD

– A n aqueous solution of the method analyte s prepared from

the Primary Dilution Standard solution . The calibration standard solutions are used to calibrate the instrument response with respect to analyte concentration.

3.3 CONTINUING CALIBRATION CHECK (CCC)

– A calibration standard containing the method analyte s, internal standard s and s urrogate a nalytes, which is analyzed periodically to verify the accuracy of the existing calibration.

3.4 DESORB FLOW RATE

– The rate at which gas is passed through the sorbent trap during the desorb cycle. The desorb flow rate is app roximately equal to the total flow rate through the

GC inlet (mL/min).

3.5 DETECTION LIMIT (DL)

– The minimum concentration of an analyte that can be identi fied,

measured and reported with 99% confidence that the analyte concentration is greater than

ze ro. This is a statistical determination (Sect. 9.2. 6 ) and accurate quantitation is not expected

at this level.

3.6 DRY PURGE VOLUME

– The total volume of purge gas (mL) bypassing the sparging vessel and passing through the sorbent trap during the dry purge cycle (used as a moisture control

measure )

.

3.7 FIELD DUPLICATE (FD)

– Separate samples collected at the same time

, shipped and stored

under identical c onditions

. Method precision, including the contribution from sample collection procedures, is estima ted from the analysis of FDs. Fo r the purposes of this method,

FD s are necessary to conduct repeat analyses if the original field sample is lost or to conduct repeat analyses in the case of QC failures associated with the analysis of the original field sample. FD s are used to prepare Laboratory Fortified Sample Matrix (Sect. 3.1 1 ) and Laboratory For tified Sample Matrix Duplicate ( Sect. 3.1 2 ) QC samples.

3.8 FIELD REAGENT BLANK (FRB)

– An aliquot of reagent water that is placed in a sample container in the laboratory and treated as a sample in all respects, including shipment to the sampling site, exposure to sampling site conditions, storage, preservation and all analytical procedures. The purpose of the FRB is to de termine if method analytes or other interferences

are introduced into the samples during transport and storage

.

3.9 INTERNAL STANDARD (IS)

– A pure compound added to all standard solutions

, field samples and QC samples in a known amount. Each internal standa rd is assigned to a specific analyte or multiple analytes and is used to measure relative response.

3.10 LABORATORY FORTIFIED BLANK (LFB)

– An aliquot of reagent water to which known quantities of the method analytes are added. The LFB is analyzed in the sam e manner as a sample

, including the preservation procedures in Section 8. The LFB is used during the I nitial

D emonstration of Capability to verify method performance for precision and accuracy.

3.11 LABORATORY FORTIFIED SAMPLE MATRIX (LFSM)

– A FD to which known quantities of the method analyte s are added. The LFSM is processed and analyzed as a sample and its purpose is to de termine whether the sample matrix contributes b ias to the analytical results. For this method, separate f ield samples are required for preparing fortified matrix so that sampling error is included in the accuracy estimate.524.4

- 6 3.12 LABORATORY FORTIFIED SAMPLE MATRIX DUPLICATE (LFSMD)

– A second FD

, of the same sample used to prepare the LFSM

, which is fortified identi cally to the LFSM.

The LFSMD is used instead of the FD to assess method pre cision and accuracy when the

occurrence of the method analyte s is infrequent. For this method, separate field samples are required for pr eparing fortified matrix so that sampling error is included in the precision

estimate.

3.13 LABORATORY REAGENT BLANK (LRB)

– An aliquot of reagent water containing the preservatives

, internal standard s and surrogate analyte s

. The LRB is used to determine if the method analytes or interferences are introduced from the laboratory environ ment, the reagents or glassware. The LRB is also used to test for cross contamination in the purge

- and

- trap
system

.

3.14 LOWEST CONCENTRATION MINIMUM REPORTING LEVEL (LCMRL)

– The single laboratory LCMRL is the lowest spiking concentration such that the probability of spike recovery in the 50% to 150% range is at least 99%

. 1

3.15 MATERIAL SAFETY DATA SHEETS (MSDS)

– W ritten information provided by vendors concerning a chemical’s tox icity, health haza rds, physical properties, fire and reactivity data,

storage instructions , spill response procedures and handling precautions.

3.16 MINIMUM REPORTING LEVEL (MRL)

– The minimum concentration that can be report ed by a laboratory as a quant ified value for the method analyte in a sample following analysis.

This concentration must meet the criteria defined in Section 9.2.4 and must be no lower than

the concentration of the lowest calibration standard for each method analyte.

3.17 PRIMARY DILUTION STANDARD (PDS)

– A solution containing the method analytes (or internal standards and surrogate analytes) prepared in the laboratory from Stock Standard

Solution s and diluted as needed to prepare calibration standards and sample fortification

solutions.

3.18 PROCEDURAL CALIBRATION

– A calibration technique in which calibration standards are processed through the entire method, including sample preparation, addition of preservatives

, extraction and concentration.

3.19 PURGE FLOW RATE

– The rate (mL/min) that the pu rge gas fl ows through the sparging vessel during the purge cycle.

3.20 PURGE VOLUME

– The total volume of purge gas (mL) that flows through the sparg ing vessel during the purge cycle.

3.21 QUALITY CONTROL SAMPLE (QCS)

– A solution containing the method analytes at a known concentration that is obtained from a source external to the laboratory and different

from the source of calibration standards

. The purpose of the QCS is to verify the accuracy of the primary calibration standards

.

3.22 REAGENT WATER

– Purified water that does not contain any measurable quantity of the

method analytes or interfering compounds at or above 1⁄2 the MRL.524.4

- 7 3.23 STOCK STANDARD SOLUTION (SSS)

– A concentrated solution containing one or more of the method analytes that is prepared in the laboratory using assayed reference materials or purchased from a reputable commercial source, so that the concentration and purity of analytes are traceable to certificates of analysis.

3.24 SUR ROGATE ANALYTE

– A pure analyte which is extremely unlikely to be found in any sample and which is added to a sample aliquot in a known amount befo re analysis

. Surrogates

are measured with the same procedures used to measure other sample components. Because surrogates are present in every sample, they provide a means o f assessing method performance for a specific purge

- and

- trap analysis cycle.

4. INTERFERENCES

4.1 SAMPLE CONTAINERS, SHIPPING AND STORAGE

– Volatile organic compounds (VOCs) present in ambient air, shipping containers and in the laboratory environment m ay permeate the PTFE

- lined septa of the sample vials or be present at high concentrations in the headspac e of the vial ( especially if the vials were prepared in a laboratory )

. Contamination

from these sources is evaluated by analyzing FRB s as described in Section 9. 3

. 9

.

4.2 PURGE

- AND

- TRAP SYSTEM

– Commercially available purge

- and

- trap concentrators and autosamplers have complex sample paths that are subject to cross contamination, which is commonly referred to as “ carryover. ” Carryover is controlled by minimizin g the transfer line length from the au tosampler to the sparg ing vessel and optimizing the bake cycle and rinse cycle parameters. The potential for c arryover in the purge

- and

- trap system is evaluated during

the Initial Demonstration of Capability by analyzing the highest concentration calibration

standard followed by a LRB

.

4.3 REAGENTS

– All laboratory reagents must be routinely demonstrated to be free of

interferences under the conditions of the analysis. This ma y be accomplished by analyzing

LRBs and meeting the acceptance criterion as described in Section 9.3.1.

4.3.1 REAGENT WATER

– Analysts may observe common laboratory contaminants, such

as methylene chloride, in reagent wat er. B oiling and/or sparging reagent water with nitrogen is recommended

. If possible, prepare aqueous standards and blanks in a laboratory environment isolated from ambient sourc es of VOCs

.

4.3.2 METHANOL

– Traces of ketone s, methylene chloride and other organic solvents

could be present in methanol

. Use purge

- and

- trap

- grade methanol with this method.

4.3.3 PRESERVATION RE AGENTS

– The potential exists for trace

- level organic

contaminants in the preservation reagents. Interfer ences from these sources must be monitored by analysis of LRBs when new lots of reagents are acquired.

4.3.4 SORBENT MATERIALS

– Sorbent traps must be carefully evaluated because some traps

, when heated, have been reported to produce small amounts of VOCs

, particularly with extended use. For example, toluene may be detec ted the first time a trap is desorbed during a work shift. For this reason, a short bake cycle prior to beginning an analysis sequence is recommended. In addition, carbon

- based traps,524.4

- 8 recommended for use with nitrogen purge by this method (Section 6.8.2) , commonly produce chloromethane and bromomethane when heated. This phenomenon is caused by the reaction of methanol with the adsorbent materials when the trap is heated in

the desorb mode

. The quantity of methanol used to prepare aqueous samples should

be minimized and background levels of chloromethane and bromomethane shoul d be carefully monitored in LRB s analyzed with each Analysis Batch. Background levels may preclude quantitation of these two analytes in SIM mode.

4.3.5 PURGE GAS SUPPLY

– Nitrogen used to purge samples is a potential source of

contamination. Trace VOCs i n the purge gas, supply lines or the gas supply system ( including the regulator ) can concentrate on the sorbent trap. H igh

- purity gas supplies and high

- purity gas regulators are re comme nded to minimize contamination

from these sources. Purge gas filters should be regenerated or replaced at the intervals specified by the manufacturers.

4.4 MATRIX INTERFERENCES

– Matrix interferences are caused by contaminants that are present in the sa mple. The extent of matrix interferences will vary considerably from source to source depending upon the nature of the water. The analysis of LFSM (Sect. 9.3.7) provides evidence for the presence (or absence) of matrix effects.

5. SAFETY

5.1 The toxicity or carcinogenicity of each reagent used in this method has not been precisely

defined. Each chemical should be treate d as a potential health hazard and exposure to these chemicals should be minimized. Each laboratory is responsible for maintaining an awareness of OSHA regulations regarding safe handling of chemicals used in this method. 3 A reference file of MSDSs should be made available to all pe rsonnel involved in the analysis

.

5.2 Pure standard materials and Stock Standard Solution s of the method compounds should be

handled with suitable personal protection equipment

. 4

6. EQUIPMENT AND SUPPLIES

References to specific brands or catalog numbers are included as examples only and do not imply endorsement of the product . These references do not preclude the us e of other vendors or supplies.

6.1 SAMPLE CONTAINERS

– Clean, amber volatile organic analysis (VOA) vials fitted with

PTFE

- faced silicone septa and polypropylene screw caps (I

- Chem Cat. No. S146

– 0040 or equivalent).

6.2 MICRO SYRINGES

– Suggested sizes include 2.0, 5.0, 10 and 25 μL

.

6.3 PURGE

- AND

- TRAP SYRINGES

– 5

- mL glass syringes with PTFE Luer

- Lok fitting (Hamilton Model No. 1005 TLL or equivalent) for manual loading of samples into a sparging

vessel

.

6.4 SYRING E VALVE

– two

- position syring e valves with Luer ends ( Supelco Cat. No. 20926 or equivalent) for use in sealing purge

- and

- trap syringes (Sect. 6.3).524.4

- 9 6.5 VOLUMETRIC FLASKS

– Class A, suggested sizes include 50, 100 and 200 mL for preparation of calibration standards

.

6.6 ANALYTICAL BALANCE

– Capable of weighing to the nearest 0.0001 gram ( g )

.

6.7 MICRO

- REACTION VESSEL

– 0.3

- , 1.0

- , 2.0

- , 5.0

- mL sizes (Supelco Cat No s

. 33291, 33293, 33295, 33299 or equivalent) equipped with Mininert Valves [Supelco Cat No. 33301 (15 millimeter ( mm ) fo r 0.3

- , 1.0

- and 2.0

- mL vials) and Cat No. 33303 (20 mm for 5.0

- mL vials) ] . These vials are recommended for storage of Stock Standard Solutions and Primary

Dilution Standards (PDS) prepared in methanol

.

6.8 PURGE

- AND

- TRAP SYSTEM

– Any purge

- and

- trap unit that is capable of being electronically interfaced to the GC and that is capable of meeting the method QC requirements outlined in Section 9 is permitted . The concent rator(s) may be equipped with an

auto sampler. Mois ture control modules are permitted but not required.

6.8.1 SPARGING VESSEL

– Instruments must be equipped with a sparging vessel specifically designed for purging a 5

- mL sample volume. A glass frit should be

installed at the base of the sample chamber so the purge gas passes through the water column as finely divided bubbles with a diameter of less than 3 mm at the origin.

NOTE: Larger sparging vessels are not allowed. While the larger sample volume

could result in the transfer of more analyte to the tr ap, purging efficiency decreases

unless the purge volume is increased proportionally . While the procedural calibration technique corrects for this, lower purging efficiency decreases method precision. In addition, la rger purge volumes could result in the transfer of more water vapor to the

trap

, placing increased demand on mo isture control strategies

.

6.8.2 SORBENT TRAP

– Purge

- and

- trap manufacturers typically recommend specific sorbent traps for use with their instrume nts. Any trap design is acceptable provided the data acquired meet all QC criteria described in Section 9.

Durin g method development studies using nitrogen purge

, trap s containing Tenax, silica gel and co conut charcoal in series yielded lower recoveries for most of the method analytes when compared directly to the recoveries obtained using a helium

purge . A trap containing Tenax, silica gel and carbon molecular sieve (CMS)

exhibited similar poor performance

. Thus, t raps containing Tenax, silica gel and

coconut charcoal or Tenax, silica gel and CMS may not be used in this method

. Traps containing s ynthetic carbon adsorbent media (Supelco Vocarb ® 3000 or equivalent) are recommended for use with this method.

6.8.3 TRANSFER LINE

– Silcosteel ® or equivalent heated transfer line used to transfer the desorbed analytes from the purge

- and

- trap concentrator to the injection port of the

GC.

6.8.4 SAMPLE HEATER

– A spa rging vessel heater is optional. Resistance or infrared

heater s may be used.524.4

- 10 6.8.5 REFRIGE RATED AUTOSAMPLER

– Vial autosamplers must be capable of maintaining samples at a temperature of 10 ° C or low e r

. Verify t he temperature of field samples placed in the autosampler using an external thermocouple or thermometer (inserted into a vial containing water ) during the IDC and at least quarterly. This temperature must not be altered after collecting the initial calibration

because it may change analyte purging efficiencies.

6.8.6 STANDARD ADDITION MODULE

– Automated device incorporated into vial autosamplers capable of fortifying internal standard s and surrogate analyte s directly

into the sparging vessel. A standard addition module is recommende d when vial autosamplers are used in the method.

6.8.7 TANDEM PURGE

- AND

- TRAP OPERATION

– A t echnique allowin g use of two

purge

- and

- trap concentrators configured in tandem

. The IDC procedure (Sect. 9.2) must be conducted for each concentrator. In addition, t his option requires separate QC samples for each sample path (Sect. 9. 3 ) , separate calibrations (Sect. 10 ) and the

use of a marker compound (Sect. 10 , Note ) to uniquely identify the sample path.

6.9 GAS CHROMATOGRAPHY MASS SPECTROMETRY SYSTEM/DATA SYSTEM (GC/MS/DS)

6.9.1 GC INJECTOR AND OVEN

– The GC must be capable of temperature programming

and must be equipped with a standard split/splitless injector and a flow controller that is compatible with purge

- and

- trap analysis . In this configuration, the purge

- and

- trap effluent is plum b ed directly to the carrier gas inlet line of a split/splitless injectio n port . The injection port is operated in split mode to achieve the desired desorb flow

rate and reduce water transmission. A deactivated glass liner (Restek Cat. No. 20972 or equivalent) is recommended to minimize dead volume and active sites within the

GC inlet

.

6.9.2 FUSED SILICA CAPILLARY GC COLUMN

– Laboratories must use a column specifically designed for analysis of volatile organic compounds by purge

- and

- trap

. The column must hav e an i.d. of 0.32 mm or less to be compatible with operation in the sp l it mode (Sect. 6.9.1)

. The column must be capable of res olving the method analytes so that a unique quantitation ion is available for each analyte

.

6.9.3 GC/MS INTERFACE

– The mass spectrometer must have sufficient vacuum pumping capacity to allow the direct feed of the analytical column to the ion source.

6.9.4 MASS SPECTROMETER (MS)

– The MS must be capable of electron ionization (EI) at a nominal energy of 70 electron volts (eV) and must be operated in the positive ion mode. An ion

- trap mass spectrometer, tuned to produce mass spectra that approximate standard, library spectra obtained under EI conditions, may be used. The instrument must be capable of obtaining at least six scans during the elution of

each chromatogr aphic peak. Seven to ten scans across chromatographic peaks are recommended. The spectrometer must produce a mass spectrum that meets all

criteria in Table 1 when 4

- bromofluorobenzene (BFB) is in troduce d into the GC/MS (Sect. 10.1.1).524.4

- 11 6.9.5 DATA SYSTEM

– An i nterfaced data system is required to acquire, store, reduce and output mass spectral data. The computer software must have the capability of processing stored GC/MS data by recognizing a GC peak within any given retention time window, comparing the mass spectra from the GC peak with spectral data in a

user

- created data base and generating a list of tentatively ident ified compounds with

their retention times and scan numbers

. The software must allow integration of the ion abundance of any specific ion between specif ied time or scan number limits. The

software must also allow construction of lin ear or second

- order re gression calibration

curves and calculati on of concentrations using the internal s tandard technique.

7. REAGENTS AND STANDARDS

7.1 REAGENTS AND SOLVENTS

– Reagent grade or better chemicals must be used. Unless

otherwis e indicated , all reagents should c onform to the specifications of the Committee on Analytical Reagents of the Americ an Chemical Society (ACS), when such specifications are

avail able. Other grades may be used as long as the reagent is of sufficiently high purity to permit its use without n egatively affecting data quality.

7.1.1 HELIUM

– Ultra High Purit y (99.999%) or equivalent, for use as GC carrier gas.

7.1.2 NITROGEN

– Ultra High Purity (99.999%) or equivalent, for use as purge gas

.

7.1.3 REAGENT WATER

– Purified water which does not contain any measurable quantities of any method analytes or interfering compounds at or above 1⁄2 the MRL for each compound of interest.

7.1.4 METHANOL (CH 3 OH, CAS# 67

- 56

- 1 )

– Purge

- and

- tra p grade , demonstrated to be free of analytes and interferences ( Burdick & Jackson Brand ® f or Purge

- and

- trap Analysis Cat. No. 232 or equivalent).

7.1.5 ASCORBIC ACID (C 6 H 8 O 6 , CAS# 50

- 81

- 7)

– Dechlorinating agent , demonstrated to be free of analyte s and interferences (Alfa Aesar Cat. No. A15613 or equivalent).

7.1.6 MALEIC ACID (C 4 H 4 O 4 , CAS# 110

- 16

- 7)

– Used as a preservative and to lower pH for the purpose of preventing dehydrohalogenation of chlorinated analytes . High purity, demonstrated to be free of analytes and interferences (Sigma Cat. No. M0375

or equivalent).

7.1.7 SODIUM THIOSULFATE (Na 2 S 2 O 3 , CAS# 7772

- 98

- 7)

– Optional dechlorinating agent when sam pling only for THMs (Sigma Cat. No. 563188 or equivalent).

7.2 STOCK STANDARD SOLUTIONS

– C ertified mixes of the 524. 4 method analytes, the

internal standards and the surrogate analytes are recommended

. Users may prepare sto ck

standards of the liquid and solid analytes, if not available as certified solutions, following the guidance prov id ed in this section. Afte r opening the sealed ampoules , store commercial

mixes in micro

- reaction vials with Mininert caps (Sect. 6.7) at a temperature of

- 10 ° C or

lower

. After transfer replace v endor

- supplied stock solutions within one month.524.4

- 12 NOTE: Methyl iodide may degrade faster than other liquid analytes. Monitor the area of this compound relative to the internal standard, 1, 4

- difluorobenzene . Replace the stock standard if methyl iodide shows evidence of degradation.

7.2.1 INTERNAL STANDARD STOCK SOLUTIONS (ISSS) ( 1 000 to 2500 μ g/mL)

– This m ethod uses three internal standards : 1,4

- difluorobenzene (CAS# 540

- 36

- 3),

chlorobenzene

- d 5 (CAS# 3114

- 55

- 4) and 1, 4

- dichlorobenzene

- d 4 (CAS# 3855

- 82

- 1)

.

7.2.2 SURROGATE STOCK STANDARDS (SURSS) ( 1000 to 2 5 00 μ g/mL)

– This

method uses three surrogate a nalytes: methyl

- t

- butyl

- ether

- d 3 (C AS# 29366

- 08

- 3 )

, bromofluorobenzene ( BFB ) ( CAS# 460

- 00

- 4 ) and 1,2

- dichlorobenzene

- d 4 (CAS#

2199

- 69

- 1)

.

7.2.3 ANALYTE STOCK STANDARD SOLUTIONS

– Obtain the analytes listed in the

table in S ection 1.1 as certified mixes in methanol or as neat standards if necessary.

7.2.4 PREPARATION INSTRUCTIONS FOR LIQUID ANALYTES

– Prepare the stock standards individually a t 10 mg/mL

. Using an analytical balance, obtain a tare weight for a VOA vial containing 20

- mL of purge

- and

- trap

- grade methanol. To achieve the

10 m g/L nominal concentration, calculate the volume of the liquid analyte

c orresponding to 200 mg. Carefully measure this volume with a 250

- μ L syringe and inject the entire quantity under the surface of the methanol. Subtract the tare weight

from the final w eight to calculate the exact solution co ncentration. W hen a compound’s purity is assayed to be 96 percent or greater, the weight can be used

without correction to calculate the concentration of the stock standard.

7.2.5 PREPARATION INSTRUCTIONS FOR SOLID ANALYTES

- Prepare the stock standards individually at 10 mg/mL by weighing 200 mg of each solid analyte into a

40

- mL VOA vial and diluting to 20 mL with purge

- and

- trap

- grade methanol . For

semi

- solid and other difficult to transfer materials, insert the entire weigh boat into a VOA vial containing 20

- mL of methanol. If the measured mass of analyte is not exactly 200 mg, adjust the volume of methanol to achieve a nominal con centration of 10 mg/mL. W hen a compound’s purity is assayed to be 96 percent or greater, the weight can be used without correction to calculate the concentration of the stock

standard.

7.2.6 STORAGE OF INDIVIDUAL STOCK STANDARDS

- S tore stock standards in the VOA vials in which they were prepared . Stock standard solutions of liquid and s olid analytes prepared in

- house are estimated to be stable for at least six months if stored at

- 10 °C or colder. However, such solutions may be stable for longer periods depending on the analyte. Laboratories must use accepted QC practices to determine when stock standards need to be replaced.

7.3 PRIMARY DILUTION STANDARDS (PDS)

– Prepare Primary Dilution Standards by combining and diluting appropriate volumes of the stock standards with purge

- and

- trap

- grade

methanol.

7.3.1 INTERNAL STANDARD AND SURROGATE PRI MARY DILUTION

STANDA RD ( IS/ s urrogate PDS)

– Prepare a combined internal standard and524.4

- 13 s urrogate PDS from the ISSS and SURSS

. F ield samples and calibration standards

must contain the same concentration of internal standards and surrogate s and the quantity of methanol added should be minimized. B etween one and 5 μL per 5

- mL sample is recommended

. An IS/surrogate PDS concentration that results in the aqueous concentration falling in the mid

- range of the initial calibration, e.g., 5 μg/L in

full sca n mode and 0.5 μg/L in SIM mode is recommended. Store the IS/ s urrogate
PDS in a glass vi al with Teflon

- lined septa at a temperature of

- 10 ° C or colder

. However, if the autosampler has a sealed reservoi r on the standard addition module IS/surrogate PDS may be held at room temperature for extended periods (several months)

.

7.3.2 ANALYTE PRIMARY DILUTION STANDARD ( analyte PDS)

– The analyte PDS is used to prepare the calibration standards and to fortify LFBs, LFSMs and LFSMDs

with the method analytes. The analyte PDS is prepared by combining appropriate

volumes of the analyte s t ock s tandard s olutions to achieve concentrations appropriate for preparing aqueous calibrat ion standards and fortifying samples. Choose

conc entrations such that at least 2 μL of the PDS is transferred to achieve the desired aqueous concentration in the standard or QC samples ; however, minimize the volume of methanol used. Methanol reacts to pr oduce chloromethane and bromomethane when traps containing synthetic

- carbon a dsorbent materials are heated (Sect. 4.3.4)

. During method development, PDS solutions ranged in concentration from 10 μg/mL to 400 μg/mL. Lower concentrations of the analyte PDS may be necessary when conducting analyses in SIM mode. S tore analyte PDS solutions in micro

- reaction vials with Mininert caps at a temperature of

- 10 ° C or colder. PDS solutions which contain

gas es must be replaced after one week; those which do not contain gases may be stored for up to one month.

7.4 CALIBRATION STANDARDS

– Prepare procedural calibration standards by diluting the analyte PDS into reagent water containing the method preservatives (Sect . 8.1)

. A constant

concentration of each internal standard and surrogate analyte is added to each calibration

standard , either manually or by use of an automated standard addition module (Sect. 6.8.6 ).

The lowest concentration calibration standard mus t b e at or below the MRL

. Additionally,

t h es e calibration standards may be used as CCCs. The dilution factors for calibration

standards used to collect method performance data in Section 17 are provided in the tables

below.

Typical concentrations for aqueous calibration standards used during method development in

full scan mode

CAL a Level An a lyte PDS Conc. (μg/mL) Analyte PDS Volume (μL) Final CAL Std. Volume (L) Final CAL Std. Conc. (μg/L)

1 10 5.0 0.100 0.50

2 10 10 0.100 1.0

3 100 2.0 0.100 2.0

4 100 5.0 0.100 5.0

5 400 2.5 0.100 10

6 400 5.0 0.100 20

7 400 10 0.100 40

a CAL = calibration standard

.524.4

- 14 Typical concentrations for aqueous calibration standards used during method development in

SIM mode

CAL Level Analyte PDS Conc. (μg/mL) Analyte PDS

Volume (μL) Final CAL Std. Volume (L) Final CAL Std. Conc. (ng/L)

1 0.1 10 0.100 10

2 1.0 2.5 0.100 25

3 1.0 5.0 0.100 50

4 1.0 10 0.100 100

5 10 2.0 0.100 200

6 10 5.0 0.100 500

7 10 10 0.100 1,000

7.5 GC/MS TUNE CHECK SOLUTION, BFB (CAS# 460

- 00

- 4)

– Use the IS/surrogate analyte PDS (Sect. 7.3.1).

8. SAMPLE COLLECTION, PRESERVATION and STORAGE

8.1 SAMPLE COLLECTION

8.1.1 Prior to shipment to the field, ascorbic acid and maleic acid must be added to each sample bottle. Cap the vials tightly to avoid spillage of the preservation reagents. If using a 40

- mL vial , add 25 mg of ascorbic a cid and 200 mg of maleic acid. If other collection volumes are used, adjust the amount of the preservation reagen t s so that the

final concentrations of ascorbic acid and maleic acid in the sample containers are 0.625 g/L and 5 g/L, resp ectively. Using narrow

- range pH paper, periodically verify that sample pH is ~2 for each sample source.

8.1.2 If a sample foams vigorousl y when added to a VOA vial containing maleic and ascorbic acids, discard the sample. Collect another sample for that location, but do

not add the method preservatives

. Document these samples as “not acidified.” Unpreserved s amples must be analyzed within 24 hours of collection.

8.1.3 If sampling only for t he THMs

, samples may be preserved with sodium thiosulfate

. Add 3 mg to each 40

- mL VOA vial prior to sample collection. Do not add ascorbic or maleic acid when employing this preservation option.

NOTE: If the residual chlorine is likely to be present at greater than 5 mg/L, a

det ermination of the chlorine concentration may be necessary. Add an additional 25 mg of ascorbic acid or 3 mg of sodium thiosulfate per each 5 mg/L of residual

chlorine for each 40

- mL of sample.

8.1.4 Grab samples must be collected in accordance with standard sampling practices. 5

When sampling from a cold water tap , remove the aerator , open the tap and allow the system to flush until the water temp erature has stabilized ( approxi mately 3 to 5 minutes). Fill sample bottles to overflowing, but take care not to flush out the rapidly dissolving solid preservatives . No air bubbles should pass through the sample as the

bottle is filled or be trapped in the sample when the bottle is sealed.524.4

- 15 8.1.5 When sampling from an open body of water, fill a beaker with water collecte d from a

representa tive area. Use this bulk sample to generate individual samples and Field

re plicates as needed.

8.2 FIELD REAGE NT BLANK (FRB)

8.2.1 A FRB must accompany each sample set unless only THMs are being analyzed. At the laboratory, add the sample preservatives to the FRB sample bottle , fill with

reagent water and ship the FRB with the sampling kits

. Do not open the FRB in the field; the FRB must remain sealed until analysis. Since total THMs would be expected to be present in nearly all disinfected drinking water samples, field blank analysis is not required when reporting positive resu lts for total THMs . This exception to the analysis of field blanks only applies to the analysis of total THMs as disinfection byproducts (DBPs) . Positive results for all other chemicals observed must be accompanied by the an alysis of a field b lank to confirm that the positive result was not the result of contamination during sample handling or shipment.

8.2.2 Add the sample preservatives at the laboratory to pr epare sample containers for the field samples. T he same lots of ascorbic acid and maleic acid must be used for the

FRB and the field samples.

8.3 FIELD DUPLICATES

– At a minimum

, collect all samples in duplicate. Adequate replicate sample s in the analytical batch will need to be collected to fulfill QC requirements for LFSMs

and LFSMDs or FD s.

8.4 SAMPLE SHIPMENT AND STORAGE

– Samples must be chilled during shipment and must not exceed 10 °C during the first 48 hours after co llection. Samples must be confirmed to be at or below 10 °C when they are received at the laboratory. In the laboratory, samples

must be stored at or below 6 °C, protected from light and isolated from ambient sources of

VOCs

. When resident in the a utosampler, samples must be held at 10 °C or lower

. Samples

must not be frozen.

8.5 SAMPLE HOLDING TIMES

– Analyze samples as soon as possible. Samples that are

collected and stored as described in Section 8.1 and 8.4 must be analyzed within 14 days of

collection

.

9. QUALITY CONTROL

QC requirements include the Initial Demonstration of Capability and ongoing QC requirements

. This section describes each QC parameter, its required frequency and the performance criteria that

must be met in order to satisfy EPA quality objec tives. The QC criteria discussed in the following sections are summarized in Section 17, Ta bles 1 2 and 1 3 . These QC requirements are considered the minimum acceptable QC criteria. Laboratories are encouraged to institute additional QC practices to meet their specific needs. Compliance with the requirements of the IDC must be demonstrated for each analyte that the laboratory intends to report us ing full scan MS and for each analyte that the laboratory intends to report in the SIM or SIS detection mode.

9.1 METHOD MODIFICATIONS

– The analyst is permitted to select purge

- and

- trap and GC

conditions appropriate for the available instrumentation. H owever
, five key parameters are524.4

- 16 restricted to prescribed ranges. These ranges are summarized in the table below

. If the chosen parameters fall within the “recommended” ranges, the laboratory may proceed with

the IDC. If values outside the “recommended” ranges are selected for any one of these five parameters, the laboratory must demonstrate equivalent performance in accordance with the guidelines provided in Section 9.4 and then the analyst must repeat the procedures of th e IDC. However, values for the five key parameters must n ever exceed the “allowable” ranges listed

in the table below. In addition, s ample size cannot be varied from t he 5

- mL volume prescribed in this method

. All other parameters including the remaining concentrato r conditions, GC conditions and MS conditions may be varied without restriction

.

Parameter Recommended Allowable

Minimum Maximum Minimum Maximum Sample temperature Ambient 40 o C Ambient 60 ° C

Purge flow rate 40 mL/min 55 mL/min 20 mL/min 80 mL/min Purge volume 360 mL 520 mL 320 mL 520 mL

Desorb time 1 min 1 min 0. 5 min 2 min Purge volume + d ry purge volume 360 mL 7 2 0 mL 320 mL 7 20 mL

NOTE: The “recommended” values provided equivalent response factors and internal

standard areas compared to helium purge

. The “allowable” limits resulted in a wider variation in response factors compared to helium purge; however, operation within this range may be appropriate for limited analyte lists and other concentrator designs. Sample temperature is

limited to 6 0 o C to avoid acid

- catalyzed decomposition of method analytes. See Table 2 in Section 17 for typical values for purge

- and

- trap parameters.

9.2 INITIAL DEMONSTRATION OF CAPABILITY (IDC)

– The IDC must be successfully perf ormed prior to analyzing any field samples. Prior to conducting the IDC, the analyst must meet the calibration requi r ements outlined in Section 10. The IDC must be completed for each concentrator and trap. For example, if dual concentrators are interfac ed to a single GC/MS, p erform the IDC for each system

. I f a new trap is installed with sorbent materials

different from the original trap, repeat the IDC. Requirements for the IDC are described in the following sections and are summarized in Table 1 2

.

9.2.1 D EMONSTRATION OF LOW SYSTEM BACKGROUND

– Analyze a LRB

. Confirm that the blank is free of contamination as defined in Section 9.3.1

.

N OTE : The system must be checked for carryover by analyzing a LRB immediately following the highest calibration standard. If this LRB does not meet the criteria outlined in Section 9.3.1, then carryover is present and the cause must be identified

and eliminated

.

9.2.2 DEMONSTRATION OF PRECISION

– Prepare and analyze seven replicate LFBs. Fortify the se samples near the midrange of the initial calibration curve

. The method preservation reagents must be added to the LFB s as described in Section 8.1

. The

percen t relative standard deviation ( % RSD) of the concentra tions of the replicate analyses must be ≤ 20% for all method analytes

.524.4

- 17 100 ion Concentrat Average ions Concentrat Measured of Deviation Standard RSD % × =

9.2.3 DEMONSTRATION OF ACCURACY

– Calculate the average percent recovery

u sing the same set of replicate data generated for S ection 9.2.2

. The average recovery of the replicate analyses must be within + 2 0% of the true value.

100 ion Concentrat Fortified ion Concentrat Measured Average Recovery % × =

9.2.4 MINIMUM REPORTING LEVEL (MRL) CONFIRMATION

– Establish a target

con cen tration for the MRL based on the intended use of the data

. The lowest

calibration standard used to establish the initial calibration (as well as the low

- level Continuing Cali bration Check) must be at or below the concentration of the MRL. Establishing the MRL concentration too low may cause repeated failure of ongoing QC req uirements. Confir m the MRL following the procedure outlined below.

NOTE: Method analytes that are consistently present in the background (e.g., methylene chloride , TBA , chloromethane and bromomethane ) should be report ed as detected in field samples only after careful eva luation of the background levels. In such cases, an MRL must be established at a value no less than three times the

standard deviation of the mean LRB concentration or three ti mes the mean LRB concentration, whichever is greater

. This guidance is intende d to minimize the occurrence of reporting false positive results.

9.2.4.1 Fortify and analyze seven replicate LFBs at or below the proposed MRL

concen tra tion. The LFBs must contain the method preservatives as specified in Section 8.1 . Calculate the mean ( Mean ) and standard deviation ( S ) for these replicates. Determine the Half Range for the Prediction

Interval of Results ( HR PIR ) using the equation below

HR PIR = 3.963 S

where S is the standard deviation and 3.963 is a constant value for seven replicates. 1

9.2.4.2 Confirm that the U pper and L ower limits for the Prediction Interval of

Result s ( PIR = Mean + HR PIR ) meet the upper and lower recovery limits as

shown below

.

The Upper PIR Limit must be ≤ 150 % recovery.

Mean HR

Fortified Concentrat ion PIR +

× ≤ 100 150%

The Lower PIR Limit must be ≥ 50 % recovery.524.4

- 18 Mean HR

Fortified Concentrat ion PIR − × ≥ 100 50%

9.2.4.3 The MRL is validated if both the Upper and Lower PIR Limits meet the criteria described above. If these criteria are not met, the MRL has been set
too low and must be confirmed again at a higher concentration.

NOTE: These equations are only valid for seven replicate samples.

9.2.5 QUALITY CONTROL SAMPLE (QCS)

– Analyze a mid

- level Quality Control Sample (Sect. 9.3. 10 ) to confirm the accuracy of the primary calibration standards

.

9.2.6 DETECTION LIMIT DETERMINATION ( optional )

– While DL determination is not a specific requirement of this method, it may be required by various regulatory bodies associated with compliance monitoring. It is the responsibility of the laboratory to ascertain whether DL determination is required based upon the intended use of the data.

Analyses for this procedure must be done over at l e ast three days. Prepare at least

seven replicate LFBs

. Fortify the LFBs at a concentration estimated to be near the

DL. This fortification level may be estimated by selecting a concen tration at two to
five times the noise level. The method preservatives must be added to the samples as

described in Section 8.1. Process the seven replicates through all steps of Section 11.

NOTE : If a data set used for the MRL confirmation step of the IDC meets these requirements, a DL may be calc ulated from the MRL confirmation data and no additional analyses are necessary.

Calculate the DL using the following equation:

DL = S x t (n

- 1,1

- α = 0.99)

where

t (n

- 1,1

- α = 0.99) = Student's t value for the 99% confidence level with n

- 1 degrees of

freedom (for seven replicate determinations, the Student’s t value is 3.143 at a 99% confidence level)

, n = number of replicates and

S = standard deviation of replicate analyses

.

NOTE : Do not subtract blank values when performing DL calculat ions.

9.3 ONGOING QC REQUIREMENTS

– This section describes the ongoing QC procedures that must be followed when processing and analyzing field samples. Table 13 summarizes these requirements.

9.3.1 LABORATORY REAGENT BLANK (LRB)

– Analyze a LRB with each Analysis

Batch

. The LRB must contain the method preservatives

, the internal standard s and surrogate analyte s at the same concentration used to fortify all field samples and524.4

- 19 calibration standards

. Background from method analytes or contaminants that inter

fere with the measurement of method analytes must be less than 1⁄2 the MRL

. If the

method ana lytes are detected in the LRB at concentrations equal to or greater than this level, then all data for the problem analyte(s) must be considered invalid for all samples that yielded a positive result. Subtracting LRB values from sample results is not permitted.

NOTE : Al though quantitative data below the MRL may not be accurate enough for data reporting, such data are useful in determining the magnitude of background interference. Therefore, blank contamination levels may be estimated by extrapolation when the concentrat ion is below the MRL

.

NOTE: After analysis of a sample in which method analytes exceed the calibration

range
, one or more LRBs must be analyzed (to detect potential carryover) until the system meets th e LRB acceptance criteria. If this occurs during an automated sequence, examine the results of samples analyzed following the sample that exceeded the calibration range. If the analytes that exceeded the calibration range in the previous sample are detected at or above the MRL, the se samples are invalid. If the affected analytes do not exceed the MRL, these subsequent samples are valid. THMs are excluded from this requirement.

NOTE: The LRB test in the IDC may be particularly difficult to pass for compounds analyzed using the SIM detection mode. For analytes monitored in SIM mode, the laboratory should restrict the high calibration point to 1.0 or 2.0 μg/L and consider

other t echniques such as using a dedicated sparge vessel and more aggressive recycle parameters. If possible, s elect MRLs that allow monitoring goals to be achieved, but that are well above typical blank values.

9.3.2 CONTINUING CALIBRATION CHECK (CCC)

– Analyze CCC standards at the beginning of each Analysis Batch, after every ten field samples and at the end of the Analysis Batch. See Section 1 0

. 2 for concentration requirements and acceptance

criteria.

9.3.3 LABORATORY FORTIFIED BLANK (LFB)

– Because this method utilizes procedural calibration standards , which are fortified reagent water s, there is no

difference between the LFB and the CCC standard s . Consequently, the analysis of a

separate LFB is not required as part of the ongoing QC ; howeve r, the t er m “ LFB ” is used for clarity in the IDC.

9.3.4 MS TUNE CHECK

– The procedure for con ducting the MS Tune Check for BFB is

found in Section 10. 1 .1. Acceptance criteria for the MS Tune Check are summarized in Section 17, Table 1. The MS Tune Check must be perfo rmed prior to establishing

and/or re

- establishing an initial calibration (Sect. 10.1) and each time a major change

is ma de to the mass spectrometer . Daily BFB analysis is not required

.

9.3.5 INTERNAL STANDARD S (IS)

– The analyst must monitor the peak area s of the

internal standard s in all injections of the Analysis Batch. The IS response s (peak area) in any chromato grap hic run must not deviate from the response in the most recent CCC by more than + 30% and must not deviate by more than + 50% from the524.4

- 20 average area measured during initial analyte calibration. If an IS area for a sample

do es not meet th ese criteria

, check the corresponding IS area of the most recent CCC

and p roceed as follows

.

9.3.5.1 If the IS criteria are met in the CCC but not the sample, r e analyze the sample ( FD ) in a subsequent Analysis Batch. If the IS area fail s to meet the acceptance criteria in the FD , but pass es in the most recent CCC, report the sample results as “ suspect/matrix. ”

9.3.5.2 If both the original sample and the CCC fail the IS criteria

, take corrective

action beginning with an extended bake cycle for the GC column and the

concentrator trap. Area counts may decrease as the rate of water entering the mass spectrometer exceeds the capacity of the pum ping system to

remove it. Additional measures such as clipping the inlet side of the GC column and cleaning the MS source may be indicated. Verify the integrity of the IS solution and the fortification technique. Perform the appropriate

in strument main tenance and then re analyze the sample ( FD ) in a subsequent Analysis Batch

. If the IS area fail s to meet the acceptance criteria in the FD

, but pass es in the most recent CCC, report the sample results as “suspect/matrix.”

9.3.6 SURROGATE RECOVERY

– The surrogate analyte s are fortified into all calibration standards, field samples and QC samples prior to purge

- and

- trap analysis

. Calculate the percent recovery (%R) for each surrogate using the following equation :

100 B A %R ×      

=

where A = calculated surrogate concentration for the QC or field sam ple and

B = fortified concentration of the surrogate.

9.3.6.1 Surrogate recovery must be in the range of 70 % to 130%. When surrogate recovery from a field sample, bl ank or QC sample is less than 70% or greater than 130% check : 1) calculations to locate possible errors, 2) the integrity of the surrogate analyte solution and the fortification technique

, 3) c ontamination and 4) instrument calibration

. Also, see corrective action options in Section 9.3.5.2. Correct the p roblem and reanalyze the sample in a subsequent A nalysis B atch using the appropriate FD

.

9.3.6.2 If the re peat analysis meets the surrogate recovery criterion, only report data

f

or the FD

.

9.3.6.3 If the FD fails the surrogate recovery criterion after corrective action has

been taken , report all data for that sample as “suspect/sur rogate recovery.”

9.3.7 LABORATORY FORTIFIED SAMPLE MA TRIX (LFSM)

– Within each Analysis Batch, analyze a minimum of one LFSM. The native concentrations of the analytes524.4

- 21 in the sam ple matrix must be determined in a separate aliquot and subtracted from the

measured values in the LFSM . If a variety of different sample matrices are analyzed regularly, for example

, drinking water from ground water and surface water sources, performance data must be collected for each source.

9.3.7.1 Prepare the LFSM by fortifying a FD w ith an appropriate amount of an analyte PDS (Sect. 7. 3 .2). Select a spiking concentration that is greater than or equal to the native background concentration, if known. Select ing a duplicate aliquot of a sample that has already been analy zed aids in the

selection of an appropriat e spiking level. If this is not possible, use historical data and rotate through low, medium and high calibration concentrations when selecting a fortifying concentration.

NOTE : If the presence of DBPs (e.g., THMs) preclude s selection of an appropriate fortification level for the majority of the method analytes, the

DBP s may be ignored. For example, if the analyst wishes to estimate accuracy and precision at 1.0 μg/L and chloroform is present in the native matrix at 10 μg/L, chloroform is fortified at only 10% of its native concentration. In such cases, recovery results for the DBPs may fail the acceptance criteri a for LFSM

. Appropriately qualify the QC result when

this occurs

. If the laboratory is analyzing specifically for DBP s or does not

wish to exclude them , select a fortification level based on the DPB

concentrations in the native sample such that the final DBP results fall within the calibration range.

9.3.7.2 Calc ulate the percent recovery (%R ) using the equation:



## ( ) 100 C B

- A %R × =

where A = measured concentration in the fortified sample B = measured concentration in the unfortified sample and

C = fortification concentration

.

9.3.7.3 Recoveries for samples fortified at concentrations near or at the MRL (within a factor of two times the MRL concentration) must be within + 50%

of the true value. Re coveries for samples fortified at all other concentrations

must be within + 30% of the true value. If the accuracy for any analyte falls outside the designated range and the laboratory performance for that analyte is shown to be in control in the CCCs, the recovery is judged matrix biased. The result for that analyte in the unfortified sa mple is labeled

“ suspect/matrix .”

NOTE: In order to obtain meaningful percent recovery results, correct the

measured values in the LFSM and LFSMD for the native levels in the unfortified samples, even if the native values are less than the MRL. This524.4

- 22 situation and the LRB are the only permitted uses of analyte results below

the MRL.

9.3.8 FIELD DUPLICATE OR LABORATORY FORTIFIED SAMPLE MATRIX DUPLICATE ( FD or LFSMD)

– Within each Analysis Batch, analyze a minimum of

one FD or one LFSM Duplicate

. If method analytes are not routinely observed in field samples, analyze a n LFSMD rather than a n FD

.

9.3.8.1 Calculate the relative percent difference (RPD) for duplicate measurements ( F D 1 and F D 2 ) using the equation :



## ( ) 100 /2 FD FD FD

FD RPD

2 1 2

1 ×
+

−

=

9.3.8.2 RPDs for FD s must be ≤ 3 0%. Greater variability may be observed when

FD s have analyte concentrations that are near or at the MRL (within a factor

of two times the MRL c oncentration) . At these concentrat ions, FD s must

have RPDs that are ≤ 50%. If the RPD of an analyte falls outside the designated range and the laboratory performance for the analyte is in control in the CCC, the precision is judged matrix influenced. The result from the unfortified sample is labeled “ suspect/matrix

. ”

9.3.8.3 If a n LFSMD is analyzed instead of a FD , calculate the RPD for the LFSM

and LFSMD using the equation :

9.3.8.4 RPDs for duplicate LFSMs must be ≤ 3 0%. Greater variability may be observed when fortified LFSMs have analyte concentrations that are near or at the MRL (within a factor of two times the MRL concentration) . LFSM s
at these concentrations must have RPDs that are ≤ 50%. If the RPD of an analyte falls outside the designated range and the laboratory performan ce for

th at analyte is in control in the CCC, the precision is judged matrix

influenced. The result from the unfortified sample is labeled

“ suspect/matrix

. ”

9.3.9 FIELD REAGENT BLANK (FRB)

– FRBs must be analyzed if compounds other

than common ly occurring DBPs

, such as THMs

, are detected in field samples

. Q ualify the result for any analyte that is detected in both a field sample and in the

associated FRB as “probable contribution from shipping and storage

. ” Subtracting FRB values from sample results is not permitted.

9.3.10 Q UALITY CONTROL SAMPLE (QCS)

– A QCS must be ev aluated as part of the

IDC and repeated at least quarterl y

. Fortify t he QCS near the mi dpoint of the calibration range. T he acceptance criteria for the QCS are the same as the mid

- level and high

- level CCC s (Sect

. 10. 2.1 ). If the accuracy for any analyte fails the recovery 

## ( ) 100 /2 LFSMD LFSM LFSMD

LFSM RPD ×
+

−

=524.4

- 23 criter ion , check the standard preparation process, stock standard sources and the purity of neat materials used to prepare the stock standards to locate and correct the problem.

9.4 METHOD MODIFICATION QC REQUIREMENTS

– The analyst is permitted to modify the

five key purge

- and

- trap parameters ( sample temperature, purge flow rate

, purge volume

, desorb time and d ry purge volume )

. The analyst is not permitted to modify sample collection

or preservation

, change the QC requirements of the method or increa se the sample volume

above 5 mL. Do not add or delete QC compounds from the list prescribed in the method: ISs (Sect. 7.2.1) and surrogates (Sect. 7.2.2). If modified parameters fall outside of the

“recommended” minimum and maximum for one of the five key parameters the laboratory

must confirm that the new parameters provide acceptable method performance as defined in the following subsections.

9.4.1 The new parameters must fall within the “allowable” minimum and maximum limits specified in Section 9. 1 . Values outside these limits are not p ermitted

.

9.4.2 Perform an initial calibration procedure (Sect. 10.1) for the method analytes that the laboratory intends to report using conditions that fall within the “recommended” ranges as presented in Section 9.1. D eterm ine relative response factors ( RRF ) for

each analyte averaged over the entire calibration range

. 

## ( ) ( ) ( ) (μg/L) Analyte area IS μg/L IS area Analyte RRF

× ×

=

9.4.3 Optimize the purge

- and

- trap system using the proposed method modifications. Analyze three mid

- level calibration standards and calculate mean RRFs for each method analyte. If all of the response factors observed using the modified conditions

are ≥ 7 0% of the initial calibration response factors obtained using the

“recommended” method conditions (Sect. 9.4. 2 ) , then the modified method

parameter s are permitted . Repeat the procedures of the IDC (Sect. 9.2) employing the modified parameters

.

9.4.4 T he analyst is also required to evaluate and document method performance for the proposed method modifications in real matrices that span the range of waters that the laboratory analyze s. This additional step is required because modifications that perform acceptably in the IDC

, which is conducted in reagent water

, could fail ongoing meth od QC requirements in real matrices. If

, f or example, the laboratory

ana l yzes drinking water from both surface and ground water municipalities, this requirement can be accomplished by assessing precision and accuracy (Sects. 9.2.2 and 9.2.3) in a surface water with moderate to high total organic carbon ( e.g., 2 mg/L

or g reater) and a hard ground water [ e.g., 250 mg/L as calcium carbonate (CaCO 3 ) equiva lent or greater]

.

9.4.5 The results of Sections 9.4. 3 and 9.4. 4 must be appropriately documented by the analyst and should be independently assessed by the laboratory’s QA officer prior to analyzing field samples.524.4

- 24 9.4.6 When implementing method modifications, it is the responsibili ty of the laboratory to closely review the results of ongoing QC and in particular, the results associated with the LFSM (Sect. 9.3. 7 ), LFSMD (Sect. 9.3. 8 ), CCCs (Sect. 9.3.2) and the IS area counts (Sect. 9.3. 5 ) . If repeated failures are noted, the modification must be

abandoned.

10. CALIBRATION AND STANDARDIZATION

Demonstration and documentation of acceptable analyte cali bra tion is required before performing the IDC (Sect. 9.2) and pri or to analyzing field samples. Verification of the MS calibration and the

i nitial cali bra tion must be repeated each time a major instrument modification or maintenance is performed.

NOTE: For tandem concentrators or older system s that utilize multiple sparging vessels and/or traps, a separate calibration and all required QC samples must be analyzed on each sample path. In addition, a qualitative marker compound must be added to all samples to uniquely identify the sample path and ensure that samples are m atched to the proper calibration and QC results . For example, fluorobenzene could be added to all samples analyzed on the second sample path of a tandem concentrator system.

10.1 PURGE

- AND

- TRAP GC/MS OPTIMIZATION AND INITIAL CALIBRATION

– An ini tial calibration requires optimizing purge

- and

- trap and GC/MS conditions, confirming that the

ins trument meets the BFB tune check criteria and the preparation and analysis of at least

seven calibration standards to determine the calibration curve. Ca libration must be performed using peak areas and the internal standard technique. Calibration using peak heights and

external standard calibration are not permitted.

10.1.1 MS TUNE/MS TUNE CHECK

– Calibrate the mass and abundance scales of the MS utilizing calibration compounds and procedures recommende d by the manufacturer with any modifi cations necessary to meet tuning requirements. In troduce BF B (Sect.

7. 5) into the GC/MS system. Acquire a mass spectrum using the same scan range employed for full scan sample analyses . Use a single spectrum at the apex of the

BFB peak, an average spectrum of the three highest points of the peak or an average spectrum across the entire peak to evaluate the performance of the system. Appropriate background subtracti on is allowed; however, the background scan(s) must be chosen from the baseline prior to or after elution of the BFB peak. If the

BFB mass spectrum does not meet all criteria in Table 1, the MS must be retuned to meet all criteria before proceeding with t he initial calibration.

10.1.2 PURGE

- AND

- TRAP CONDITIONS

– Establish purge

- and

- trap parameters following the manufacturer’s recommendations. M ake sure that the sample

temperature, purge flow rate

, purge volume

, desorb time and d ry purge volume are within the “ allowable ” r anges specified in section 9.1

. Optimize purge

- an d

- trap
parameters to maximize purging efficiency and minimize the transmission of water to the GC/MS system.

10.1.3 GC CONDITIONS

– Establish GC operating conditions appropriate for the GC

column dimensions by optimizing the split ratio and temperatu re program

. Generally, the required spli t ratio is inversely proportional to column diameter. The user must524.4

- 25 balance the need to transfer enough of the method analytes to achieve the desired

MRLs and the need to reduce water transmission fro m the purge

- and

- trap

concentrator . The split ratio will also affect the chromatographic peak profile of the

most volatile method ana l ytes , commonly referred to as “gases.” Sufficient

r esolution and symmetrical peak profile s with minimal tailing for these analytes must

be achieved to enable accurate and precis e integration. A mass chromatogram of the

gases obtained during method development is provided in Figure 1 . The G C program

must be optimized to provide adequate resolution of the method analytes as defined in the following subsections.

10.1.3.1 If possible, optimize chromatographic conditions such tha t a unique quantitation ion is available for each analyte that is free from interference

d ue to an identical fragment ion in any co

- elut ing (or overlapping) peak (s)

.

10.1.3.2 If a unique quantitation ion of sufficient intensity to set the desired MRL is not available, overlap with an identical ion from an overlapping analyte is permitted, providing that at least a 50% valley between the mass peaks is

achieved.

10.1.4 FULL SCAN MS CON DITIONS

– Select a scan range that allows the acquisition of

a mass spectrum for each of the method analytes, which includes all of the major fragments mass

- to

- charge ratio ( m/z ) 3 5 and above. However, dur ing elution of the

water/carbon dioxide peak, the analyst is permitted to begin the scan at m/z 45 to eliminate the appearance of these matrix components in the baseline.

10.1.5 SIM MS CONDITIONS

– In SIM mode, choose one primary quantitation ion and at least one secondary ion . If possible, select a second con firmation ion. Additional ions may be monitored that demonstrate a unique characteristic in the mass spectrum such as a halogen cluster. Verify that the primary ion is free from interference (Sect. 10.1.3.1 and Sect. 10.1.3.2) due to an identical fragmen t ion in any overlapping peak ( s ) . If the chromatogram is divided into SIM windows (also termed segments or periods), the laboratory must ensure that each method analyte elute s entirely within

the proper window during each Analysis Batch . Make this observation by viewing

the mass chromatogram of the quantita t ion ion for each SIM analyte in the CCC analyzed at the beginning and end of each Analysis Batch. This requirement does not preclude continuous operation by sequencing multiple Anal ysis Batches; however,

the entire A nalysis B atch is invalid if one or more analyte peaks drift outside of designated SIM windows in either of these CCC s

. For l arge analyte lists, minimize the number of ions monitored in each chromatographic window to ensu re adequate sensitivity to meet the desired MRL. During method development, five SIM windows were used as indicated in Section 17, Table 5.

10.1.6 ALTERNATING FULL AND SIM SCAN MODES

– Alternating full and SIM scan functions during a single sample acquisition is permitted if the minimum number of scans across each GC peak acquired in this mode is maintained, i.e.

, six scans as specified in Section 6. 9.4 in each full and SIM scan modes.

10.1.7 CALIBRATION STANDARDS

– Prepare a set of at least seven calibration standards

as described in Section 7. 4

. The lowest concentration of the calibration standards524.4

- 26 must be at or below the MRL. The MRL must be confirmed using the procedure outlined in Section 9.2.4 after establishing the initial calibration

. Additionally, field samples must be quantified using a calibration curve that spans the same concentration range used to collect the IDC data (Sect. 9.2), i

. e ., ana lysts are not permitted to use a restricted calibration range to meet the IDC criteria and then use a larger dynamic range during analysis of field s amples

.

10.1.8 CALIBRATION

– Calibrate t he GC /MS system using peak areas and the internal

standard technique

. Fit the calibration points with either a linear or a quadratic regression (response vs. concentration). Weighting may be used. The GC/ MS instrument used during method development was calibrated using inverse

concentration

- weighted quadratic curves. Sugg ested internal standard assignments and quantitation ions for each method analyte evaluated in full scan mode are presented in Table 4

. Suggested internal standard assignments and quantitation ions for each method analyte evaluated in SIM mode are presented in Table 5.

NOTE: Because the surrogate analytes are added at a single concentration level to the calibration standards, calibrate for each surrogate using an average response factor.

10.1.9 FORCING ZERO

– Forcing the calibration curve through the o rigin is not recommended. However, zero must be forced for method analytes (e.g., common laboratory contaminants and for carbon

- based traps, potentially chloromethane and

bromomethane ) if they are consistently detected in the Laboratory Reagent Blanks.

F orcing zero allows for a better estimate of the background level of blank contaminants. An accurate estimate of background contamination is necessary to set
MRLs for method analytes wh en blank levels are problemati c (Sect. 9.2.4 )

.

10.1.10 CALIBRATION ACCEPTANCE CRITERIA

– The initial calibration is validated by calculating the concentration of the analytes for each of the analyses used to generate the calibration curve by use of the regression equations. Calibration points that are

≤ MRL must calculate to be with in + 50% of their true value. All other calibration points must calculate to be within + 30% of their true value. If th ese criteria cannot be met, the ana lyst will have difficulty meeting ongoing QC criteria. In this case,

corrective action such as reana lyz ing the calibration standards , restrict ing the range of

calibration or perform ing instrument maintenance is recommended

.

10.2 CONTINUING CALIBRATION CHECKS (CCCs)

– Analyze a CCC to verify the initial calibration at the beginning of each Analysis Batch

, after every tenth field sample and at the end of each Analysis Batch. The beginning CCC for each Analysis Batch must be at or below

the MRL. Th is CCC verif ies instrument sensitivity prior to the analys i s of samples

. Alternate

s ubseq uent CCCs betwe en the remaining calibration level s

.

10.2.1 Calculate the concentration of each analyte in the CCC. Each analyte in t he CCC

fortified at ≤ MRL must calculate to be within + 50 % of its true value. A t all other

levels

, each analyte, including the surrogate analyte s
, must calculate to be within

+ 30 %. If these limits are exceeded , then all data for the failed analyte s must be

considered invalid

. Any field samples analyzed since the last acceptable CCC that524.4

- 27 are still within holding time must be reanalyzed after an a cceptable calibration has

been restored.

10.2.2 REMED IAL ACTION

– Failure to meet QC performance criteria for CCCs requires

remedial action. Acceptable method performance may be restored simply by recalibrating in accordance with the guidelines in Section 10. 1 and verify ing sensitivity by analyzing a CCC at or below the MRL. Because of the volatile nature of the method analytes, PDS have limited shelf life. Prepare a fresh PDS and repeat the CCC before contemplating instrument main tenance. If internal standard and calibration failures persist, maintenance such as extended bake cycles for both the

purge

- and

- trap concentrator and the GC/MS

, clipping the GC column

, replacing the

concentrator trap and cleaning the MS source may be required

. Following major maintenance, the analyst must return to the initial calibration step (Sect. 10. 1 ).

11. PROCEDURE

Important aspects of this analytical procedure include proper sample coll ection and storage (Section 8), ensuring that the instrument is properly calibrated (Section 10) and that all required QC elements are included (Section 9). This method is designed for a 5

- mL sample volume. The concentration of the internal standards and surrogate analytes must be the same in the samples as

in the calibration standards. In the laboratory, m aintain field samples, QC samples and calibration

standards at or below 6 °C at all times while in storage. While resident in the autosampler awaiting analysis, samples must be maintained at less than or equal to 10 °C

. Do not store samples in the autosampler longer than the time required to complete the Analysis Batch.

11.1 SAMPLE PREPARATION: SYRINGE METHOD

– For concentrators with a single

sparg ing vessel and autosamplers with multiple sparg ing vessels, load the sample (or previously prepared calibration standard) by use of a 5

- mL syringe . If the purge cycle will be initiated immediately after this step, warm the sample to room temperature. Remove the plunger from two sy ringes and attach a closed syringe valve. Open the VOA vial and

carefu lly pour the sample into the syringe barrel to just short of overflowing. Replace the syringe plunger, invert the syringe and compress the sample. Open the syringe valve and vent any residual air while adjusting the sample volume to 5 mL. A dd the internal standard/surrogate analyte PDS to the sample through the syringe valve. Immediately load the sample into the sparging vessel.

NOTE: Do not store samples in syringes or prepare QC samples by filling two syringes. A

second VOA vial ( i.e., a FD ) is required as a means of ensuring that a back up sample is

available and for preparing F D, LFSM and LFSMD QC samples.

11.1.1 PREPARATION OF LFSM and LFSMD : SYRINGE M ETHOD

– Three 40

- mL

vials (FDs) are required for a sample and its associated LFSM and LFSMD. Fortify two of the samples using an analyte PDS of appropriate concentration by injecting through the syringe valve

. Add the internal standards and surrog a t es as directed in

Section 11.1

.

11.1.2 F IELD DUPLICATE : SYRINGE METHOD

– F ill a 5

- mL syringe with the selected

FD and fortify with internal standards and surrogates. Analyze FDs at the frequency specified in Section 9.3.8.524.4

- 28 11.2 SAMPLE PREPARATION: VIAL AUTOSAMPLER METHOD

– Activate the cooling mechanism of the refrigerated autosampler and allow it to reach the temperature set point.

R emove samples from cold storage and immediately load them into the vial autosampler

. Prepare the IS / s urrogate fortification solution at a concentration appropriate for the

automated standard addition device.

11.2.1 PREPARATION OF LFSM and LFSMD FOR VIAL AUTOSAMPLERS

– Three

40

- mL vials (FDs) are required for a sample and its associated LFSM and LFSMD. Fortify two of t he samples using an analyte PDS of appropriate concentration by puncturing the septa of each vial with a syringe

. Allow time for the compounds to disperse homogeneously within the sample. Assume that the sample volume is 40

mL or estimate the typical vol ume of a 40

- mL vial in use at your laboratory. Fortification may be accomplished by use of a standard addition module if the autosampler is so equipped.

11.2.2 FD s FOR VIAL AUTOSAMPLERS

– Load the appropriate FD vial into the autosampler. A nalyz e FDs at the frequency specified in Section 9.3.8.

11.3 PURGE

- AND

- TRAP ANALYSIS

11.3.1 Establish purge

- and

- trap and GC/ MS operating conditions per the guidance in

Section 10. 1

.

11.3.2 Bake the concentrator trap and GC column to remove contaminants that may have collected in the system. This step is especially important if the analytical system has

been idle for more than a few hours.

11.3.3 Initiate the purge cycle and autosampler sequence. After the purge cycle, preheat the

trap as recommended by the manufacturer. Start the data acquisition at the beginning of the desorb cycle. Bake the trap and rinse the sparging vessel and autosampler delivery lines using settings optimized to minimize sample carryover.

NOTE: The method preservatives cause the water column in the sparging vessel to appear effervescent during the purge cycle. This is normal and no adverse effects

occur as a result of the effervescence.

11.4 THE ANALYSIS BATCH

– Establish a valid initial calibratio n following the procedures

outlined in Section 10. 1 and confirm that the calibration is still valid by analyzing a CCC at
or below the MRL as described in Section 10. 2

. Alternately, verify that an existing calibration, established for a previous Analysis Batch, is valid by analyzing a CCC at or

below the MRL. Next, analyze a LRB. Continue the Analysis Batch by a naly zing aliquots

of field and QC samples at appropriate frequencies (Section 9 .3 )

, employing the optimized conditions used to acquire the initia l calibration. Analyze a mid

- or high

- level CCC after every ten field samples and at the en d each Analysis Batch

.

NOTE: Each Analysis B atch must begin with the analysis of a CCC at or below the MRL for each analyte that the laboratory intends to report

, followed by the analysis of a LRB.

This is true whether or not an initial calibration is analyzed. After 20 field samples, the low

-524.4

- 29 level CCC and the LRB must be repeated to begin a new Analysis Batch. The acquisition

start time of the mid

- level CCC at the end of the Analysis Batch must be within 24 hours of the acquisition start time of the low

- level CCC at the beginning of the Analysis Batch. Multiple Analysis Batches within a 24

- hour period are permitted. Do not count QC samples (LRBs, FRBs, FDs, LF SMs, LFSMDs) when calculating the frequency of CCCs that are required during an Analysis Batch

.

12. DATA ANALYSIS AND CALCULATIONS

12.1 COMPOUND IDENTIFICATION

– Establish an appropriate retention time window for each analyte to identify them in QC and field sample chromatograms. Base this assignment on measurements of actual retention time variation for each compound in standard solution s analyzed on the GC/MS over the course of time. The suggested variation is plus or minus

three times the stan dard deviation of the retention time for each compound for a series of injections. The in jections from the initial calibration and from the ID C (Sect. 9.2) may be used to calculate the retention time window. However, the experience of the analyst should weigh heavily on the determination of an appropriate range.

12.1.1 At the conclusion of data acquisition, use the same software settings established during the calibration procedure to identify peaks of interest in the predetermined

retention time windows. Initially

, i dentify an analyte by comparison of its retention time with that of the corresponding analyte peak in a recent initial calibration

stan dard or CCC.

12.1.2 Some GC/MS programs use spectra matching criteria when collecting data in full scan mode based on the comparison of field sample spectra (after background subtraction if necessary) to a reference spectrum in the user

- created database

. This

d atabase should be created prior to conducting the IDC from spectra obtained for a

mid

- level to high

- level c alibration s tandard and updated as necessary. If available, this feature may be utilized as a secondary identification routine; however, the primary criterion must be based on the analyte retention time.

12.2 COMPOUND CONFIRMATION FULL SCAN MODE

– In general, all ions that are present above 30 percent relative abundance in the mass spectrum of th e user

- generated database

must be present in the mass spectrum of the sample component and must agree within an absolute 20 percent of the relative abundance in the reference spectrum. For example, if an ion has a relative abundance of 30 percent in the s tandard spectrum, its abundance in the sample spectrum must be in the range of 10 to 50 percent. Some ions, particularly the molecular ion, are of special importance and should be evaluated even if they are below 30 percent relative abundance.

NOTE: Compound identification is more challenging when sample components are not resolved chromatographi cally and produce mass spectra containing ions contributed by more than one analyte. When GC peaks obviously represent more than one sample component (i.e. , broadened peak with shoulder(s) or valley between two or more maxima), characteristic analyte spec tra may be obtained by examining the spectra of individual scans across the peak

and then applying appropriate background subtraction . When analytes co

- el ut e (i.e., only one GC peak is apparent), the identification criteria may be met but each analyte spectrum will contain extraneous ions contributed by the co

- elut ing compound.524.4

- 30 12.3 COMPOUND CONFIRMATION SIM MODE

– In SIM mode, each confirmation ion should be present

. For each analyte identified by retention time, t he abundance of the confirmation ions relative to the quantitation ion should agree within an absolute 20 percent of the relative

abundance in the spectrum taken from a recent calibration standa rd analyzed in SIM mode

. For example, if an ion has a relative abundance of 30 percent in the calibration standard, its abundance in the sample spectrum should be in the range of 10 to 50 percent.

12.4 COMPOUND QUANTITATION

– Calculate analyte concentrations using the multipoint

calibration established in Section 10. 1 . Report only those values that fall between the MRL and the highest calibration standard

.

12.4.1 Calculations must use all available digits of precision, but final reported

concentrations should be ro unded to an appropriate number of significant figures (one digit of uncertainty); this is typically two and not more than three, significant figures.

12.4.2 Prior to reporting data, the chromatograms must be reviewed for incorrect peak

identification or imp roper integration

.

12.4.3 Prior to reporting data, the laboratory is responsible for assuring that QC requirements have been met and that any appropriate qualifier is assigned.

12.5 EXCEEDING THE CALIBRATION RANGE

– The analyst must not ext rapolate beyond the

established calibration range. If an analyte result exceeds the range of the initial calibration curve, dilute the FD using reagent water containing the method preservatives. Re

- inject the diluted sample. Incorporate t he dilution factor into final concentration calculations. The resulting data must be annotated as a dilution and the reported MRLs must reflect the dilution

factor

.

13. METHOD PERFORMANCE

References to specific brands or catalog numbers are included as examples only and do not imply endorsement of the product. These references do not preclude the use of other vendors or supplies.

13.1 PRECISION, ACCURACY AND DETECTION LIMITS

– The method performance data presented in Section 17 were collected using a Tekma r Stratum Purge

- and

- trap C oncentrator
with a Tekmar A QUA Tek 70 V ial A utosampler interfaced to an Agilent 6890 Plus GC and an Agilent 5973 MS

. Table 2 lists t he purge

- and

- trap conditions used to gather the method performance data presented in Section 1 7. GC/MS conditions for the Agilent system are presented in Table 3

. Table 4 present s the qua n titation ions employed in full scan mode appropriate for the Restek Rtx ®

- VMS column (no interference from overlapping peaks) for each analyte

, internal standard and surrogate analyte , suggested internal standard assignments

and observed retention times associated with the method performance results. Table 5 lists

the method a nalytes for which method performance data were collected in t he SIM mode ; primary quantitation ions , confirmation ions and internal standard references are provided

. Single laboratory LCMRLs and DLs determined in full scan mode are listed in Table 6

. Single laboratory p recision and accuracy data obtained in full scan mode are presented for

three water matrices : reagent water ( Table 7 ), chlorinated (finished) ground water (Table 8 )

and chlo rinated (finished) surface water (Table 9 ). LCMRLs and DLs obtained in SIM mode524.4

- 31 for selected method analytes are presented in Table 1 0

. Figure 1 depicts an extracted ion chromatogram of the method analytes that are gases at room temperature acquired in full scan

mode

. Figure s 2 and 3 are total io n chromatograms of the method analytes in reagent water
and drinking water obtained under the condi tions employed during method development in full scan mode. Figure 4 depicts an extracted ion chromatogram of the method analytes that

are gases at room temperature acquired in SIM mode . Figure 5 is a total ion chromatogram of the method analytes in reagent water obtained under the condi tions employed during method development in SIM mode.

13.2 SAMPLE STORAGE STABILITY STUDIES

– An analyte storage stability study was

conducted during the development of EPA Method 524.3 by fortifying the analytes (20 μ g/L of each analyte) into a chlorinated surface water that was collected, preserved and stored as described in Section 8. The average recovery of triplicate analyses, conducted on Days 0, 7

and 14 are presented in Table 1 1

. Th ese results are reproduced in Method 524.4 to document that storage s tability for the method analytes has been demonstrated.

14. POLLUTION PREVENTION

For information about pollution prevention applicable to laboratory operations described in this method,

consult: Less is Better, Guide to Minimizing Waste in Laboratories

, a web

- based resource available from the American Chemical Society website.

15. WASTE MANAGEMENT

The analytical procedures described in this method generate relatively small amounts of waste since only small amounts of reagents and solvents are used. The matrix of concern is finished drinking water. However, the Agency requires that laboratory waste management practices be conducted consistent with all appli cable rules and regula tions and that laboratories protect the air, water and land by minimizing and controlling all releases from fume hoods and bench operations. In addition, compliance is required with any sew age discharge permits and regula tions, particularly the hazardous waste identification rules and land disposal restrictions

.

16. REFERENCES

1. Winslow , S

. D.; Pepich, B

. V.; Martin, J

. J.; Hallberg, G

. R.; Munch D

. J.; Frebis, C

. P.; Hedrick, E

. J.; Krop, R

. A. Statistical Procedures for Determination and Verification of Minimum Reporting Levels for Drinking Water Methods

. Environ. Sci. Technol

. 2006 ; 40,

281

- 288.

2. Glaser, J.A. ; Foerst, D.L.; McKee, G.D.; Quave, S.A.; Budde, W.L. Trace Analyses for

Waste waters

. Environ. Sci. Technol. 1981 ; 15, 1426

- 1435.

3. Occupational Exposures to Hazardous Chemicals in Laboratories

, 29 CFR 1910 .1450

, Occupational Safety and H ealth Administration

.

4. Safety in Academic Chemistry Laboratories ; American Chemical Society Publication ; Committee on Chemical Safety : 7 th Edition, 2003

.524.4

- 32 5

. Standard Practice for Sampling Water from Closed Conduits ; ASTM Annual Book of Standards, Section 11 , Volume 11.01, D3370

- 07 ; American Society for Testing and Materials : Philadelphia , PA

, 2007

.524.4

- 33 17. TABLES, DIAGRAMS, FLOWCHARTS and VALIDATION DATA

The conditions listed in the tables of this section were used to collect method performance data at EPA. They do not represent any form of guidance for acceptable parameter settings. Refer to the relevant sections of the method for guidance on optimizing and selecting purge

- and

- trap and GC/MS conditions.

TABLE 1. 4

- BROMOFLUOROBENZENE (BFB) MASS INTENSITY CRITERIA

m/z Required Intensity (relative abundance)

95 Base peak, 100% relative abundance

96 5 to 9% of m/z 95

173 Less than 2% of m/z 174

174 Greater than 50% of m/z 95

175 5 to 9% of m/z 174

176 Greater than 95% but less than 10 5 % of m/z 174

177 5 to 10 % of m/z 176

TABLE 2

. PURGE

- AND

- TRAP CONDITIONS USED FOR METHOD PERFORMANCE

RESULTS

Parameter Conditions a
Sample volume 5 mL Sample purge temperature 40 o C Trap Supelco K

- Trap ( Vocarb ® 3000 ) Purge c ycle 4 0 mL/ min for 11 min Condenser purge temperature 20 o C Dry purge 100 mL/min for 3 min Desorb preheat temperature 250 o C

Desorb cycle 260 o C for 1.0 min Bake rinse cycles Sparging vessel and autosampler sample path rinsed twice Bake cycle 2 6 0 o C for 6 min @ 20 0 mL/min

a The chrom atograms presented in Figures 2 and 3 were obtained under these conditions.524.4

- 34 TABLE 3

. GAS CHROMATOGRAPHY/MASS SPECTROMETRY (GC/MS) CONDITIONS

FOR METHOD PERFORMANCE RESULT S

Parameter Conditions a

Column Restek Rtx ®

- VMS 30 meter, 0.25 mm i.d., 1.4 μm d f Inlet liner 1

- mm i.d., deactivated glass

Inlet conditions 30:1 split ratio, 200 °C , helium carrier gas, column flow rate : 0.9 mL/min

GC temperature program 45 ° C for 4.5 min, 12 o C /min to 100 ° C, hold 0 min, 25 °C to 240 °C

, hold 3 .3 2 min Solvent delay 1. 5 min before activating filaments in the electron impact source MS source temperature 230 o C MS quadrupole temperature 150 ° C

GC/MS interface Direct, 240 o C

Full scan window 1 m/z 47 to 150 (1. 7 to 2.9 min )

Full scan window 2 m/z 35 to 260 ( 2.9 min to 18 min )

SIM parameters multiple retention time window s; dwell times set to allow seven to 10 scans across chromatographic peaks

TABLE 4

. RETENTION TIMES, RECOMMENDED QUANTITATION IONS and

SUGGESTED INTERNAL STANDARD REFERENCES FOR FULL SCAN MODE a

Analyte Peak no. Fig.’s 2a, 2b, 2c RT Q

- Ion IS b Reference

dichlorodifluoromethane 1 1.84 85 1

chlorodifluoromethane 2 1.90 51 1

chloromethane 3 2.05 50 1

vinyl chloride 4 2.10 62 1

1,3

- butadiene 5 2.11 54 1

bromomethane 6 2.40 94 1

trichlorofluoromethane 7 2.66 101 1

diethyl ether 8 2.98 59 1

1,1

- dichloroethene 9 3.18 96 1

carbon disulfide 10 3.23 76 1

methyl iodide 11 3.36 142 1

allyl chloride 12 3.74 76 1

methylene chloride 13 3.87 84 1

trans

- 1,2

- dichloroethene 14 4.08 96 1

methyl acetate 15 4.10 43 1

methyl

- t

- butyl ether

- d 3 (surrogate #1) 16 4.21 76 1

methyl

- t

- butyl ether (MtBE) 17 4.23 73 1

t

- butyl alcohol (TBA) 18 4.38 59 1

diisopropyl ether (DIPE) 19 4.77 45 1

1,1

- dichloroethane 20 4.94 63 1

t

- butyl ethyl ether (ETBE) 21 5.29 59 1

cis

- 1,2

- dichloroethene 22 5 .68 96 1

bromochloromethane 23 5.95 128 1524.4

- 35 Analyte Peak no. Fig.’s 2a, 2b, 2c RT Q

- Ion IS b Reference

chloroform 24 6.05 83 1

carbon tetrachloride 25 6.22 117 1

tetrahydrofuran 26 6.26 72 1

1,1,1

- trichloroethane 27 6.32 97 1

1,1

- dichloropropene 28 6.48 110 1

1

- chlorobutane 29 6.55 56 1

benzene 30 6.80 78 1

t

- amyl methyl ether (TAME) 31 6.96 73 1

1,2

- dichloroethane 32 7.06 62 1

trichloroethene 33 7.53 132 1

1,4

- difluorobenzene (IS #1) 34 7.58 114 1

t

- amyl ethyl ether (TAEE) 35 7.85 59 1

dibromomethane 36 8.05 93 1

1,2

- dichloropropane 37 8.18 63 1

bromodichloromethane 38 8.26 83 1

cis

- 1,3

- dichloropropene 39 9.06 75 1

toluene 40 9.32 92 2

tetrachloroethene 41 9.73 166 2

trans

- 1,3

- dichloropropene 42 9.78 75 2

ethyl methacrylate 43 9.96 69 2

1,1,2

- trichloroethane 44 9.94 83 2

dibromochloromethane 45 10.12 129 2

1,3

- dichloropropane 46 10.21 76 2

1,2

- dibromoethane 47 10.35 107 2

chlorobenzene

- d 5 (IS #2) 48 10.82 117 2

chlorobenzene 49 10.84 112 2

ethylbenzene 50 10.86 91 2

1,1,1,2

- tetrachloroethane 51 10.90 131 2

m

- xylene 52 10.99 106 2

p

- xylene 53 10.99 106 2

o

- xylene 54 11.36 106 2

styrene 55 11.41 104 2

bromoform 56 11.43 173 2

isopropylbenzene 57 11.62 105 2

4

- bromofluorobenzene (surrogate #2) 58 11.85 95 3

bromobenzene 59 11.94 156 3

n

- propylbenzene 60 11.96 91 3

1,1,2,2

- tetrachloroethane 61 12.01 83 3

2

- chlorotoluene 62 12.08 126 3

1,3,5

- trimethylbenzene 63 12.11 105 3

1,2,3

- trichloropropane 64 12.12 110 3

4

- chlorotoluene 65 12.21 91 3

t

- butylbenzene 66 12.35 134 3

pentachloroethane 67 12.38 167 3524.4

- 36 Analyte Peak no. Fig.’s 2a, 2b, 2c RT Q

- Ion IS b Reference

1,2,4

- trimethylbenzene 68 12 .40 105 3

sec

- butylbenzene 69 12.49 105 3

4

- isopropyltoluene 70 12.59 119 3

1,3

- dichlorobenzene 71 12.66 146 3

1,4

- dichlorobenzene

- d 4 (IS #3) 72 12.71 152 3

1,4

- dichlorobenzene 73 12.72 146 3

n

- butylbenzene 74 12.90 134 3

hexachloroethane 75 13.02 166 3

1,2

- dichlorobenzene

- d 4 (surrogate #3) 76 13.03 152 3

1,2

- dichlorobenzene 77 13.04 146 3

1,2

- dibromo

- 3

- chloropropane 78 13.61 157 3

hexachlorobutadiene 79 14.05 225 3

1,2,4

- trichlorobenzene 80 14.08 180 3

naphthalene 81 14.31 128 3

1,2,3

- trichlorobenzene 82 14.44 180 3

a These quantitation ions are appropriate for the column used to generate method performance data. The user must verify that the quantitation ions selected for their column are unique and free from interference due to overlapping method analytes.

b IS = internal standard.

TABLE 5. RETENTION TIMES, RECOMMENDED QUANTITATION IONS, CONFIRMATION IONS, SUGGESTED INTERNAL STANDARD REFERENCES, EXAMPLE

CHROMATOGRAPHI C WINDOWS and DWELL TIMES FOR SIM MODE a

Analyte Peak no. Fig.’s 5a, 5b, 5 c RT Q

- Ion Confirmation

Ions IS b

Reference Window c

chlorodifluoromethane 1 1.87 51 67 1

1 chloromethane 2 2.03 50 52 1

vinyl chloride 3 2.09 62 64 1

1,3

- butadiene 4 2.10 54 53 1

b romomethane 5 2.39 94 96 1

1,1

- dichloroethene 6 3.18 96 61, 98 1

methylene chloride 7 3.87 84 49 1

trans

- 1,2

- dichloroethene 8 4.07 96 61 1

2 methyl

- t

- butyl ether

- d 3 (surrogate #1) 9 4.20 76 57 1

methyl

- t

- butyl ether (MtBE) 10 4.22 73 57 1

1,1

- dichloroethane 11 4.94 63 65 1

cis

- 1,2

- dichloroethene 12 5.68 96 61 1

bromochloromethane 13 5.96 128 130 1

chloroform 14 6.05 83 85 1

carbon tetrachloride 15 6.22 117 119 1

1,1,1

- trichloroethane 16 6.31 97 99 1

benzene 17 6.79 78 77 1

1,2

- dichloroethane 18 7.06 62 64 1 3 trichloroethene 19 7.54 132 130, 95 1524.4

- 37 Analyte Peak no. Fig.’s 5a, 5b, 5 c RT Q

- Ion Confirmation

Ions IS b

Reference Window c

1,4

- difluorobenzene (IS #1) 20 7.59 114 63 1

1,2

- dichloropropane 21 8.19 63 65 1

bromodichloromethane 22 8.26 83 85 1

toluene 23 9.32 92 91 2

tetrachloroethene 24 9.74 166 164 2

1,1,2

- trichloroethane 25 9.95 83 97 2

dibromochloromethane 26 10.12 129 127 2

4 1,2

- dibromoethane 27 10.35 107 109 2

chlorobenzene

- d 5 (IS #2) 28 10.83 117

- 2

chlorobenzene 29 10.84 112 114 2

ethylbenzene 30 10.86 91 106 2

1,1,1,2

- tetrachloroethane 31 10.90 131 133 2

m

- xylene 32 11.00 106 91 2

p

- xylene 33 11.00 106 91 2

o

- xylene 34 11.36 106 91 2

styrene 35 11.41 104 103, 78 2

bromoform 36 11.43 173 175 2

4

- bromofluorobenzene (surrogate #2) 37 11.85 95 174 3

5 n

- propylbenzene 38 11.96 91 120 3

1,2,3

- trichloropropane 39 12.12 110 112, 75 3

sec

- butylbenzene 40 12.49 105 134 3

1,4

- dichlorobenzene

- d 4 (IS #3) 41 12.71 152

- 3

1,4

- dichlorobenzene 42 12.73 146 148 3

1,2

- dichlorobenzene

- d 4 (surrogate #3) 43 13.03 152

- 3

1,2

- dichlorobenzene 44 13.04 146 148 3

1,2

- dibromo

- 3

- chloropropane 45 13.61 157 155, 75 3

1,2,4

- trichlorobenzene 46 14.08 180 182 3

a These quantitation ions are appropriate for the column used to generate method performance data. The user must verify that the quantitation ions selected for their column are unique and free from interference due to overlapping method analytes.

b IS = internal standard

.
c Chromatographic window (also termed g roup number or period); dwell time for each ion is 10 milliseconds.

TABLE 6. LOWEST CONCENTRATION MINIMUM REPORTING LEVELS (LC MR L s) AND DETECTION LIMITS (DLs) FOR FULL SCAN MODE a

Analyte LCMRL, μg/L DL Fortification, μg/L DL, μg/L

dichlorodifluoromethane 0.33 0.25 0.12

chlorodifluoromethane 0.16 0.25 0.059

c hloromethane 0.16 0.10 0.077
vinyl chloride 0.15 0.25 0.063

1,3

- butadiene 0.33 0.10 0.055

b romomethane 0.28 0.25 0.099

trichlorofluoromethane 0.23 0.25 0.083524.4

- 38 Analyte LCMRL, μg/L DL Fortification, μg/L DL, μg/L
diethyl ether 0.35 0.25 0.070

1,1

- dichloroethene 0.18 0.25 0.14

carbon disulfide 0.20 0.10 0.078
methyl iodide 0.24 0.25 0.099
allyl chloride 0.26 0.25 0.12
methylene chloride 0.15 0.25 0.18

trans

- 1,2

- dichloroethene 0.29 0.25 0.1 2
methyl acetate 0.21 0.25 0.1 2
methyl

- t

- butyl ether (MtBE) 0.17 0.10 0.042

t

- butyl alcohol (TBA) 0.33 0.25 0.11
diisopropyl ether (DIPE) 0.10 0.10 0.029

1,1

- dichloroethane 0.14 0.10 0.095

t

- butyl ethyl ether (ETBE) 0.12 0.10 0.033

cis

- 1,2

- dichloroethene 0.21 0.10 0.083

b romochloromethane 0.56 0.25 0.092

c hloroform 0.16 0.10 0.070

carbon tetrachloride 0.14 0.10 0.073

t etrahydrofuran 0.49 0.10 0.063

1,1,1

- trichloroethane 0.17 0.10 0.060

1,1

- dichloropropene 0.50 0.25 0.14

1

- chlorobutane 0.10 0.10 0.053

b enzene 0.11 0.10 0.028

t

- amyl methyl ether (TAME) 0.16 0.10 0.054

1,2

- dichloroethane 0.23 0.10 0.027

trichloroethene 0.13 0.10 0.078

t

- amyl ethyl ether (TAEE) 0.13 0.10 0.050

d ibromomethane 0.18 0.25 0.1 3

1,2

- dichloropropane 0.17 0.10 0.088

bromodichloromethane 0.19 0.25 0.081

cis

- 1,3

- dichloropropene 0.13 0.10 0.050

toluene 0.13 0.10 0.031

t etrachloroethene 0.27 0.25 0.059

trans

- 1,3

- dichloropropene 0.20 0.25 0.095

ethyl methacrylate 0.11 0.25 0.10

1,1,2

- trichloroethane 0.38 0.10 0.048

dibromochloromethane 0.23 0.25 0.10

1,3

- dichloropropane 0.12 0.10 0.098

1,2

- dibromoethane 0.13 0.10 0.090

chlorobenzene 0.20 0.10 0.050

ethylbenzene 0.15 0.10 0.026

1,1,1,2

- tetrachloroethane 0.18 0.10 0.081

m

- and p

- xylene 0.30 0.20 0.11

o

- xylene 0.26 0.25 0.11

styrene 0.20 0.10 0.033

bromoform 0.26 0.25 0.14

isopropylbenzene 0.12 0.10 0.028

bromobenzene 0.19 0.10 0.066524.4

- 39 Analyte LCMRL, μg/L DL Fortification, μg/L DL, μg/L

n

- propylbenzene 0.18 0.10 0.045

1,1,2,2

- tetrachloroethane 0.15 0.10 0.06 7

2

- chlorotoluene 0.26 0.10 0.088

1,3,5

- trimethylbenzene 0.12 0.10 0.037

1,2,3

- trichloropropane 0.42 0.25 0.13

4

- chlorotoluene 0.23 0.10 0.082

t

- butylbenzene 0.25 0.25 0.16

pentachloroethane 0.29 0.25 0.16

1,2,4

- trimethylbenzene 0.18 0.10 0.055

sec

- butylbenzene 0.24 0.10 0.052

4

- isopropyltoluene 0.16 0.10 0.064

1,3

- dichlorobenzene 0.20 0.10 0.049

1,4

- dichlorobenzene 0.19 0.10 0.029

n

- butylbenzene 0.30 0.10 0.094

hexachloroethane 0.62 0.25 0.14

1,2

- dichlorobenzene 0.14 0.10 0.056

1,2

- dibromo

- 3

- chloropropane 0.44 0.25 0.15

hexachlorobutadiene 0.34 0.10 0.086

1,2,4

- trichlorobenzene 0.15 0.10 0.071

naphthalene 0.14 0.10 0.044

1,2,3

- trichlorobenzene 0.16 0.10 0.042

a LCMRLs calculated according to the procedure in reference 1 with the following modification: Instead of evaluating seven replicates at four concentration levels, LCMRLs are now obtained by analyzing four replicates at

seven concentration levels

.524.4

- 40 TABLE 7

. PRECISION AND ACCURACY OF METHOD ANALYTES FORTIFIED AT 0.50

, 1.0 AND 1 0 μg/L IN REAGENT WATER FOR FULL SCAN MODE

Analyte Fortified Conc. = 0.50 μg/L
(n=7) Fortified Conc. = 1.0 μg/L
(n=7) Fortified Conc. = 1 0 μg/L
(n=7)

Mean % Recovery RSD a Mean % Recovery RSD Mean % Recovery RSD

dichlorodifluoromethane 77.4 8.5 82.8 17 104 6.3

chlorodifluoromethane 127 4.1 122 4.7 110 7.1

chloromethane 88.8 14 102 3.3 108 5.5 vinyl chloride 103 8.7 106 6.0 109 6.5
1,3

- butadiene 107 8.3 106 6.7 110 6.5

bromomethane 111 6.7 104 5.3 110 6.8

trichlorofluoromethane 105 9.0 104 8.2 111 6.9 diethyl ether 120 13 108 5.9 112 5.2
1,1

- dichloroethene 108 7.9 93.2 5.3 103 6.0

carbon disulfide 93.6 6.4 92.3 6.0 98.9 6.6 methyl iodide 95.5 7.3 93.9 6.5 105 5.6 allyl chloride 76.1 5.6 84.2 6.1 100 8.0 methylene chloride 69.2 11 84.5 15 102 6.3

trans

- 1,2

- dichloroethene 108 6.5 104 3.2 100 6.5 methyl acetate 88.9 11 89.6 12 103 4.3 methyl

- t

- butyl ether (MtBE) 97.5 8.9 97.6 3.5 103 5.2

t

- butyl alcohol (TBA) 45.7 31 75.8 13 105 4.6 diisopropyl ether (DIPE) 90.5 3.5 96.2 2.5 103 5.2
1,1

- dichloroethane 89.4 5.3 91.6 5.8 102 5.1

t

- butyl ethyl ether (ETBE) 91.3 4.8 97.0 3.8 103 4.8

cis

- 1,2

- dichloroethene 84.1 8.5 94.2 5.6 102 6.5

bromochloromethane 93.8 13 96.5 4.9 104 6.0

chloroform 90.1 4.5 97.3 4.3 103 5.5

carbon tetrachloride 83.0 9.7 92.4 3.9 100 5.2 tetrahydrofuran 86.6 21 93.5 8.9 100 5.1
1,1,1

- trichloroethane 79.3 4.3 91.1 6.3 102 5.7
1,1

- dichloropropene 99.7 6.6 95.6 6.7 97.6 8.1

1

- chlorobutane 91.5 8.2 92.3 7.1 100 7.2

benzene 81.6 3.5 93.6 4.6 102 6.4

t

- amyl methyl ether (TAME) 98.9 3.9 98.4 3.0 102 5.2

1,2

- dichloroethane 105 4.0 102 4.5 104 4.3

trichloroethene 99.6 5.2 103 4.9 103 6.3

t

- amyl ethyl ether (TAEE) 91.4 3.6 94.1 1.8 104 5.2

dibromomethane 89.0 12 93.8 6.1 104 5.4
1,2

- dichloropropane 85.1 6.3 92.4 6.0 102 6.0

bromodichloromethane 87.3 8.5 97.1 3.7 104 4.7

cis

- 1,3

- dichloropropene 83.9 3.9 92.7 3.5 102 5.9

toluene 85.6 3.4 92.0 6.5 102 4.4

tetrachloroethene 74.3 12 87.2 5.8 102 6.3

trans

- 1,3

- dichloropropene 77.4 7.4 90.1 5.6 103 5.4 ethyl methacrylate 90.9 9.1 93.7 5.3 103 5.2
1,1,2

- trichloroethane 97.6 7.0 101 8.5 104 3.7

dibromochloromethane 90.7 5.2 95.7 3.7 102 4.8
1,3

- dichloropropane 93.0 2.7 96.4 4.0 105 3.9
1,2

- dibromoethane 75.1 7.6 89.5 4.5 104 4.4

chlorobenzene 82.6 4.8 93.4 3.3 104 5.2 ethylbenzene 87.1 3.9 93.8 3.8 102 5.4524.4

- 41 Analyte Fortified Conc. = 0.50 μg/L
(n=7) Fortified Conc. = 1.0 μg/L
(n=7) Fortified Conc. = 1 0 μg/L
(n=7)

Mean % Recovery RSD a Mean % Recovery RSD Mean % Recovery RSD

1,1,1,2

- tetrachloroethane 83.0 5.9 94.1 3.6 104 5.1

m

- and p

- xylene 82.6 7.0 93.3 2.9 102 4.5

o

- xylene 77.3 5.6 94.3 2.7 103 5.6

styrene 88.2 8.1 95.3 3.3 102 5.3

bromoform 80.6 6.8 91.0 3.9 103 6.2 isopropylbenzene 83.1 2.8 93.6 3.0 103 5.3

bromobenzene 91.9 4.1 96.8 5.0 102 5.7

n

- propylbenzene 89.7 4.1 96.3 2.1 100 6.1
1,1,2,2

- tetrachloroethane 96.2 8.3 97.9 4.6 102 5.4

2

- chlorotoluene 95.0 5.2 98.2 2.2 100 6.2
1,3,5

- trimethylbenzene 87.4 4.4 94.9 1.8 102 5.8
1,2,3

- trichloropropane 84.2 7.6 92.9 8.4 102 6.6

4

- chlorotoluene 83.2 4.4 94.2 1.3 100 5.7

t

- butylbenzene 86.9 8.7 92.4 6.9 102 6.0 pentachloroethane 87.6 12 89.9 5.8 100 5.8
1,2,4

- trimethylbenzene 87.0 5.0 94.1 1.8 101 6.0

sec

- butylbenzene 81.4 3.6 93.3 3.6 101 6.1

4

- isopropyltoluene 84.5 5.9 95.5 2.4 102 6.6
1,3

- dichlorobenzene 84.5 5.9 92.2 2.0 100 5.9
1,4

- dichlorobenzene 86.6 4.2 97.2 3.3 102 5.7

n

- butylbenzene 73.5 6.8 93.0 5.0 103 6.2

hexachloroethane 81.1 16 94.7 5.3 102 6.1
1,2

- dichlorobenzene 83.0 6.2 96.6 3.4 103 5.6
1,2

- dibromo

- 3

- chloropropane 80.5 10 90.9 7.1 103 5.7

hexachlorobutadiene 64.2 6.0 85.7 6.6 100 6.9
1,2,4

- trichlorobenzene 90.7 5.3 91.9 2.1 100 5.2 naphthalene 88.0 2.9 94.0 3.2 102 5.7
1,2,3

- trichlorobenzene 86.8 8.7 92.4 4.0 101 5.5

a RSD = relative standard deviation

.524.4

- 42 TABLE 8

. PRECISION AND ACCURACY OF METHOD ANALYTES FORTIFIED AT 0.50,

1.0 AND 1 0 μg/L IN DRINKING WATER FROM A GROUND WATER SOURCE a FOR FULL

SCAN MODE

Analyte Native

C onc., μ g/L (n= 3 ) Fortified Conc. = 0.50 μg/L (n=7) Fortified Conc. = 1.0 μg/L (n=7) Fortified Conc. = 1 0 μg/L (n=7)

Mean % Recovery b RSD c Mean % Recovery b RSD Mean % Recovery b RSD

dichlorodifluoromethane N.D. 112 2.8 95.0 5.6 104 4.1

chlorodifluoromethane N.D. 80.7 8.9 91.4 6.8 105 4.5

chloromethane N.D. 90.7 4.5 92.3 9.2 105 2.5 vinyl chloride N.D. 98.9 6.9 97.3 5.0 103 3.2
1,3

- butadiene N.D. 66.1 16 84.3 5.9 101 4.0

bromomethane N.D. 115 7.3 115 8.4 127 10

trichlorofluoromethane N.D. 101 5.4 101 5.8 103 3.6 diethyl ether N.D. 101 5.6 103 9.0 103 1.4
1,1

- dichloroethene N.D. 89.6 11 91.1 12 97.8 3.1

carbon disulfide N.D. 88.8 8.7 93.7 5.4 99.9 2.5 methyl iodide N.D. 81.0 18 81.6 11 105 8.5 allyl chloride N.D. 92.0 13 99.2 12 96.7 4.6 methylene chloride 0.39 73.7 10 97.8 11 100 3.4

trans

- 1,2

- dichloroethene N.D. 82.2 19 91.2 8.2 102 3.4 methyl acetate N.D. 96.5 7.3 86.9 15 98.6 2.1 methyl

- t

- butyl ether (MtBE) N.D. 80.6 12 86.2 5.1 97.9 1.5

t

- butyl alcohol (TBA) N.D. 92.3 9.7 97.9 9.4 91.3 2.0 diisopropyl ether (DIPE) N.D. 95.3 3.6 97.8 7.4 98.9 1.9
1,1

- dichloroethane N.D. 86.0 10 93.9 5.7 99.8 2.9

t

- butyl ethyl ether (ETBE) N.D. 81.4 5.7 91.2 3.3 98.1 2.2

cis

- 1,2

- dichloroethene N.D. 87.3 9.4 94.8 4.3 97.1 2.5

bromochloromethane N.D. 101 9.5 104 7.0 97.2 3.3

chloroform 3.48 d 3.5 d 1.9 97.4 1.7

carbon tetrachloride N.D. 71.0 8.4 86.2 10 98.7 0.87 tetrahydrofuran N.D. 127 8.3 128.5 4.4 98.3 2.7
1,1,1

- trichloroethane N.D. 90.2 8.5 98.7 5.5 99.9 2.8
1,1

- dichloropropene N.D. 100 6.6 97.4 8.2 99.6 3.3

1

- chlorobutane N.D. 94.7 9.1 98.9 4.7 101 3.2

benzene N.D. 84.5 7.3 93.0 4.7 98.6 2.6

t

- amyl methyl ether (TAME) N.D. 97.3 4.2 92.3 8.7 94.5 2.4

1,2

- dichloroethane N.D. 95.2 7.4 103 7.1 99.6 2.3

trichloroethene N.D. 83.6 6.8 91.9 6.3 98.3 2.7

t

- amyl ethyl ether (TAEE) N.D. 89.0 8.8 96.4 5.4 96.3 1.7

dibromomethane N.D. 89.0 12 96.4 7.6 97.5 2.1
1,2

- dichloropropane N.D. 85.5 7.2 93.9 6.8 96.4 1.6

bromodichloromethane 5.09 78.4 d 1.5 75.5 d 1.5 97.4 1.9

cis

- 1,3

- dichloropropene N.D. 90.1 6.7 94.7 7.7 95.1 1.4

toluene N.D. 91.1 5.8 94.3 4.9 97.7 1.8

tetrachloroethene N.D. 93.5 12 95.3 11 97.3 2.9

trans

- 1,3

- dichloropropene N.D. 82.4 6.4 92.0 11 95.8 3.2 ethyl methacrylate N.D. 94.0 8.8 91.9 8.3 94.4 1.7
1,1,2

- trichloroethane N.D. 100 7.0 98.5 8.5 96.0 2.7

dibromochloromethane 6.08 d 1.8 d 3.5 97.6 1.4
1,3

- dichloropropane N.D. 87.2 5.1 93.0 8.1 96.3 2.5
1,2

- dibromoethane N.D. 99.0 8.0 98.8 9.1 95.8 3.1524.4

- 43 Analyte Native

C onc., μ g/L (n= 3 ) Fortified Conc. = 0.50 μg/L (n=7) Fortified Conc. = 1.0 μg/L (n=7) Fortified Conc. = 1 0 μg/L (n=7)

Mean % Recovery b RSD c Mean % Recovery b RSD Mean % Recovery b RSD

chlorobenzene N.D. 89.3 2.5 96.0 6.0 94.8 1.4 ethylbenzene N.D. 84.8 8.9 92.5 7.4 97.6 1.2
1,1,1,2

- tetrachloroethane N.D. 90.9 7.2 94.9 7.9 94.5 1.6

m

- and p

- xylene N.D. 92.6 5.6 94.0 4.7 96.7 1.6

o

- xylene N.D. 93.7 5.5 99.1 8.2 96.8 2.4

styrene N.D. 88.3 6.6 90.5 3.5 96.0 2.1

bromoform 2.17 d 4.5 d 4.5 92.1 2.6 isopropylbenzene N.D. 85.9 3.6 93.7 5.6 98.2 1.8

bromobenzene N.D. 78.2 11 94.0 6.4 92.7 2.5

n

- propylbenzene N.D. 85.9 5.0 96.2 7.3 96.9 3.6
1,1,2,2

- tetrachloroethane N.D. 96.4 6.8 99.2 7.2 92.6 1.8

2

- chlorotoluene N.D. 83.3 4.8 93.8 8.1 93.2 2.9
1,3,5

- trimethylbenzene N.D. 85.4 5.1 95.9 6.3 96.6 3.4
1,2,3

- trichloropropane N.D. 92.5 10 96.8 10 93.3 2.9

4

- chlorotoluene N.D. 84.5 6.1 93.1 8.6 93.6 2.5

t

- butylbenzene N.D. 76.7 11 89.8 6.5 97.6 4.1 pentachloroethane N.D. 97.6 7.7 99.8 6.3 93.8 3.1
1,2,4

- trimethylbenzene N.D. 90.9 4.9 98.0 5.5 95.8 3.1

sec

- butylbenzene N.D. 85.9 1.8 97.6 4.7 97.3 3.3

4

- isopropyltoluene N.D. 85.1 5.6 97.0 4.7 96.7 3.4
1,3

- dichlorobenzene N.D. 88.6 4.5 98.0 7.0 93.6 2.0
1,4

- dichlorobenzene N.D. 86.5 2.9 94.9 7.3 92.7 2.3

n

- butylbenzene N.D. 87.0 3.6 95.8 5.9 95.2 3.1

hexachloroethane N.D. 99.5 15 103 10 97.6 4.4
1,2

- dichlorobenzene N.D. 89.6 7.1 95.6 7.0 92.9 2.4
1,2

- dibromo

- 3

- chloropropane N.D. 92.2 13 95.8 5.3 92.5 2.6

hexachlorobutadiene N.D. 80.8 6.1 91.7 6.8 94.8 3.6
1,2,4

- trichlorobenzene N.D. 82.1 3.3 92.1 6.0 92.5 2.5 naphthalene N.D. 95.4 4.1 93.2 5.2 92.8 2.0
1,2,3

- trichlorobenzene N.D. 101 5.0 95.6 6.8 91.4 2.6

a Ground water physical parameters : pH = 7.61 ; hardness = 3 50 milligrams/liter (mg/L) (as CaCO 3 ); free chlorine =

0. 77 mg/L

. b Recoveries corrected for native levels in the unfortified matrix



### .

c RSD = relative standard deviation

. d Fortified at less than 1⁄2 the concentration in the native matrix

.524.4

- 44 TABLE 9

. PRECISION AND ACCURACY OF METHOD ANALYTES FORTIFIED AT 0.50,

1.0 AND 1 0 μg/L IN DRINKING WATER FROM A SURFACE WATER SOURCE a FOR FULL

SCAN MODE

Analyte Native Conc., μ g/L (n=3) Fortified Conc. = 0.50 μg/L (n=7) Fortified Conc. = 1.0 μg/L (n=7) Fortified Conc. = 1 0 μg/L (n=7)

Mean % Recovery b RSD c Mean % Recovery b RSD Mean % Recovery b RSD

dichlorodifluoromethane N.D. 90.5 10 90.7 3.7 103 2.8

chlorodifluoromethane N.D. 102 9.9 97.3 5.3 105 3.1

chloromethane N.D. 96.7 7.1 94.0 6.4 102 3.0 vinyl chloride N.D. 104 6.3 105 4.5 106 3.1
1,3

- butadiene N.D. 109 5.5 97.9 8.7 104 3.0

bromomethane N.D. 108 8.5 104 9.1 116 5.3

trichlorofluoromethane N.D. 94.4 4.8 94.7 4.7 106 2.9 diethyl ether N.D. 104 8.3 104 4.7 104 3.7
1,1

- dichloroethene N.D. 97.9 10 97.7 6.8 98.2 3.2

carbon disulfide N.D. 94.6 5.9 93.7 7.2 99.7 2.3 methyl iodide N.D. 85.1 7.5 86.3 6.0 95.2 3.2 allyl chloride N.D. 104 9.4 92.9 4.0 96.3 3.7 methylene chloride N.D. 104 9.1 102 6.1 102 2.2

trans

- 1,2

- dichloroethene N.D. 100 11 89.8 12 97.7 3.0 methyl acetate N.D. 110 8.6 104 9.4 107 2.8 methyl

- t

- butyl ether (MtBE) N.D. 87.0 9.3 91.9 4.0 99.5 2.9

t

- butyl alcohol (TBA) N.D. 91.8 7.6 99.7 4.6 107 3.0 diisopropyl ether (DIPE) N.D. 85.5 4.0 90.4 5.7 100 2.2
1,1

- dichloroethane N.D. 95.1 5.1 92.4 4.3 98.9 3.2

t

- butyl ethyl ether (ETBE) N.D. 84.2 4.1 87.6 3.6 99.4 2.0

cis

- 1,2

- dichloroethene N.D. 97.3 5.5 96.6 7.5 101 2.5

bromochloromethane N.D. 90.8 16 98.3 8.3 103 2.1

chloroform 19.4 d 2.0 d 6.1 86.0 2.2

carbon tetrachloride N.D. 86.0 8.6 89.4 5.1 101 1.4 tetrahydrofuran N.D. 84.5 14 97.7 6.5 103 2.7
1,1,1

- trichloroethane N.D. 84.9 7.5 89.3 7.2 97.7 2.9
1,1

- dichloropropene N.D. 92.6 15 90.5 4.2 96.3 4.6

1

- chlorobutane N.D. 92.3 8.7 91.0 7.9 99.3 2.2

benzene N.D. 94.6 7.8 96.2 4.6 99.4 2.1

t

- amyl methyl ether (TAME) N.D. 80.8 9.8 88.8 8.7 100 2.6

1,2

- dichloroethane N.D. 94.7 8.7 90.8 3.5 99.8 1.8

trichloroethene N.D. 89.4 10 90.5 7.1 99.2 1.9

t

- amyl ethyl ether (TAEE) N.D. 59.5 7.1 83.1 3.4 104 2.3

dibromomethane N.D. 91.4 7.9 93.6 7.1 99.5 2.9
1,2

- dichloropropane N.D. 86.3 7.3 90.9 7.6 99.3 2.1

bromodichloromethane 20.3 d 1.6 d 3.4 87.4 2.4

cis

- 1,3

- dichloropropene N.D. 97.1 8.3 93.1 6.5 98.6 2.1

toluene N.D. 82.5 6.7 86.1 4.4 97.5 1.9

tetrachloroethene N.D. 80.3 7.1 83.5 5.9 93.6 1.5

trans

- 1,3

- dichloropropene N.D. 91.3 7.1 92.3 5.1 97.2 3.9 ethyl methacrylate N.D. 84.4 5.1 89.5 4.5 98.3 2.5
1,1,2

- trichloroethane N.D. 79.8 11 88.0 8.5 101 1.0

dibromochloromethane 16.1 d 1.3 d 3.0 99.6 2.7
1,3

- dichloropropane N.D. 87.6 8.5 91.6 4.3 98.5 2.3
1,2

- dibromoethane N.D. 80.8 4.9 83.9 5.6 97.7 3.0524.4

- 45 Analyte Native Conc., μ g/L (n=3) Fortified Conc. = 0.50 μg/L (n=7) Fortified Conc. = 1.0 μg/L (n=7) Fortified Conc. = 1 0 μg/L (n=7)

Mean % Recovery b RSD c Mean % Recovery b RSD Mean % Recovery b RSD

chlorobenzene N.D. 73.9 6.6 86.0 3.1 97.2 2.1 ethylbenzene N.D. 79.8 4.9 84.7 4.6 96.3 2.2
1,1,1,2

- tetrachloroethane N.D. 75.5 6.2 83.3 5.9 95.9 3.8

m

- and p

- xylene N.D. 80.1 4.2 86.8 3.3 98.3 2.0

o

- xylene N.D. 75.6 7.2 81.0 4.3 97.0 1.3

styrene N.D. 82.3 7.0 89.2 3.2 96.5 2.7

bromoform 3.63 d 3.5 d 4.0 96.0 2.4 isopropylbenzene N.D. 73.6 6.0 82.4 5.7 97.7 2.1

bromobenzene N.D. 79.0 11 86.1 7.5 95.7 3.7

n

- propylbenzene N.D. 64.9 6.9 82.2 3.6 97.0 3.1
1,1,2,2

- tetrachloroethane N.D. 74.1 8.0 86.3 4.7 96.9 4.6

2

- chlorotoluene N.D. 81.7 6.2 86.0 4.1 95.8 2.8
1,3,5

- trimethylbenzene N.D. 74.3 8.4 85.5 4.1 97.8 3.2
1,2,3

- trichloropropane N.D. 86.3 8.0 87.4 7.7 96.6 5.1

4

- chlorotoluene N.D. 69.9 11 79.7 5.8 97.2 2.8

t

- butylbenzene N.D. 69.4 13 84.8 9.1 97.4 4.1 pentachloroethane N.D. 72.0 10 84.3 8.2 96.4 3.7
1,2,4

- trimethylbenzene N.D. 77.8 4.8 86.0 6.1 97.8 2.9

sec

- butylbenzene N.D. 64.5 5.5 80.7 5.7 99.1 2.6

4

- isopropyltoluene N.D. 64.0 3.8 79.6 6.9 98.4 2.8
1,3

- dichlorobenzene N.D. 77.3 10 84.4 8.8 97.3 2.5
1,4

- dichlorobenzene N.D. 70.5 4.2 86.2 5.5 97.4 2.4

n

- butylbenzene N.D. 69.4 12 80.9 9.5 99.1 3.7

hexachloroethane N.D. 89.3 14 93.3 10 99.7 2.9
1,2

- dichlorobenzene N.D. 71.3 5.5 82.4 5.5 97.3 4.1
1,2

- dibromo

- 3

- chloropropane N.D. 73.2 11 87.8 8.6 95.9 4.0

hexachlorobutadiene N.D. 59.2 14 75.7 8.4 98.5 3.6
1,2,4

- trichlorobenzene N.D. 70.9 8.2 83.2 3.0 97.0 3.6 naphthalene N.D. 68.3 4.5 83.1 6.0 101 4.5
1,2,3

- trichlorobenzene N.D. 72.3 10 82.8 4.6 97.0 5.1

a Surface water physical parameters : pH = 7. 20 ; hardness = 15 2 milligrams/liter (mg/L) (as CaCO 3 ); free chlorine =

1.85 mg/L

. b Recoveries corrected for native levels in the unfortified matrix.

c RSD = relative standard deviation.

d Fortified at less than 1⁄2 the concentration in the native matrix.524.4

- 46 TABLE 1 0

. LOWEST CONCENTRATION MINIMUM REPORTING LEVELS (LC MR L s) AND DETECTION LIMITS (DLs) FOR SIM MODE a

Analyte LCMRL, μg/L DL Fortification, μg/L DL, μg/L

chlorodifluoromethane 0.027 0.025 0.006

chloromethane Not determined : significant background levels from tra p materials (See Section 4.3.4 )

vinyl chloride 0.048 0.025 0.007

1,3

- butadiene 0.028 0.025 0.008

bromomethane Not determined: significant background levels from tra p materials (See Section 4.3.4 )

1,1

- dichloroethene 0.0 61 0.050 0.009

methylene chloride Not determined: significant background levels from ambient sources

trans

- 1,2

- dichloroethene 0.028 0.025 0.014

methyl

- t

- butyl ether (MtBE) 0.012 0.025 0.009

1,1

- dichloroethane 0.011 0.025 0.007

cis

- 1,2

- dichloroethene 0.040 0.040 0.037

bromochloromethane 0.060 0.040 0.013

chloroform 0.032 0.025 0.015

carbon tetrachloride 0.033 0.025 0.008

1,1,1

- trichloroethane 0.039 0.025 0.009

benzene 0.022 0.025 0.012

1,2

- dichloroethane 0.029 0.025 0.012

trichloroethene 0.037 0.025 0.012

1,2

- dichloropropane 0.043 0.0 40 0.011

bromodichloromethane 0.027 0.025 0.011

toluene 0.034 0.025 0.009

tetrachloroethene 0.025 0.025 0.011

1,1,2

- trichloroethane 0.029 0.025 0.010

dibromochloromethane 0.016 0.025 0.006

1,2

- dibromoethane 0.048 0.025 0.023

chlorobenzene 0.036 0.025 0.009

ethylbenzene 0.013 0.025 0.0 09

1,1,1,2

- tetrachloroethane 0.059 0.025 0.011

m

- xylene and p

- xylene 0.17 0.025 0.020

o

- xylene 0.037 0.025 0.0 16

styrene 0.018 0.025 0.012

bromoform 0.021 0.025 0.008

n

- propylbenzene 0.022 0.025 0.010

1,2,3

- trichloropropane 0.033 0.040 0.028

sec

- butylbenzene 0.019 0.025 0.011

1,4

- dichlorobenzene 0.026 0.025 0.012

1,2

- dichlorobenzene 0.0 25 0.025 0.013

1,2

- dibromo

- 3

- chloropropane 0.069 0.040 0.033

1,2,4

- trichlorobenzene 0.030 0.025 0.013

a LCMRLs calculated according to the procedure in reference 1 with the following modification: Instead of evaluating seven replicates at four concentration levels, LCMRLs are now obtained by analyzing four replicates at

seven concentration levels.524.4

- 47 TAB LE 11

. SAMPLE HOLDING TIME DATA FOR METHOD ANALYTES FORTIFIED AT 20 μg/L IN A CHLORINATED SURFACE WATER a (n=3 SAMPLES)

Analyte Day 0 Day 7 Day 14

Mean % Recovery RSD b Mean % Recovery RSD Mean % Recovery RSD

dichlorodifluoromethane 110 2.2 107 2.5 111 3.9

chlorodifluoromethane 112 2.0 109 0.63 107 0.87

chloromethane 114 0.88 110 1.1 112 2.0 vinyl chloride 117 0.99 113 1.6 116 0.87
1,3

- butadiene 116 1.3 106 1.9 105 4.6

bromomethane 117 6.9 116 3.5 114 2.5

trichlorofluoromethane 114 0.54 116 2.9 117 2.4 diethyl ether 110 1.2 106 1.5 113 1.0
1,1

- dichloroethene 106 0.94 107 0.62 111 2.3

carbon disulfide 108 0.58 106 1.9 107 3.0 methyl iodide 106 1.3 106 0.33 101 0.93 allyl chloride 108 0.57 100 0.73 101 1.0 methylene chloride 106 0.17 106 0.55 108 0.92

trans

- 1,2

- dichloroethene 107 0.89 103 1.8 107 1.5 methyl acetate 105 3.4 101 0.32 83.2 4.0 methyl

- t

- butyl ether (MtBE) 104 0.92 101 0.049 105 0.79

t

- butyl alcohol (TBA) 105 3.2 104 2.9 105 1.8 diisopropyl ether (DIPE) 107 0.71 109 0.72 109 0.65
1,1

- dichloroethane 109 1.0 108 0.82 111 0.74

t

- butyl ethyl ether (ETBE) 105 0.30 107 0.53 107 0.89

cis

- 1,2

- dichloroethene 106 0.66 105 0.67 108 0.71

bromochloromethane 104 0.64 104 1.4 105 0.45

chloroform 102 0.56 100 0.91 107 0.97

carbon tetrachloride 108 1.4 109 1.2 116 2.2 tetrahydrofuran 102 1.4 98.4 1.5 101 1.7
1,1,1

- trichloroethane 109 0.70 109 0.89 115 0.94
1,1

- dichloropropene 110 0.24 107 1.5 108 1.5

1

- chlorobutane 114 0.25 111 1.1 115 0.90

benzene 108 0.63 106 1.2 109 0.57

t

- amyl methyl ether (TAME) 105 0.56 107 0.45 107 0.59
1,2

- dichloroethane 108 2.1 105 0.59 108 1.2

trichloroethene 105 0.28 105 0.85 107 0.16

t

- amyl ethyl ether (TAEE) 107 0.31 108 0.73 107 0.69

dibromomethane 106 1.5 105 0.42 107 0.33
1,2

- dichloropropane 108 0.48 106 0.21 109 0.78

bromodichloromethane 105 0.85 104 1.2 109 1.2

cis

- 1,3

- dichloropropene 106 0.33 98.5 1.0 96.7 1.2

toluene 109 1.3 108 0.46 110 1.2

tetrachloroethene 110 2.4 106 1.1 111 2.7

trans

- 1,3

- dichloropropene 106 1.9 99.1 0.94 96.4 0.30 ethyl methacrylate 108 1.4 104 0.56 105 1.5
1,1,2

- trichloroethane 105 1.8 103 0.93 106 2.1

dibromochloromethane 104 0.99 104 0.98 107 0.98
1,3

- dichloropropane 108 1.0 104 0.10 106 1.2
1,2

- dibromoethane 104 1.7 104 1.3 106 0.72

chlorobenzene 108 1.4 106 0.36 109 1.1 ethylbenzene 115 1.1 110 0.33 116 1.4
1,1,1,2

- tetrachloroethane 106 1.6 106 0.35 110 0.92

m

- and p

- xylene 114 1.3 110 0.70 114 2.3524.4

- 48 Analyte Day 0 Day 7 Day 14

Mean % Recovery RSD b Mean % Recovery RSD Mean % Recovery RSD

o

- xylene 113 0.83 109 0.87 115 0.79

styrene 111 1.3 106 0.62 108 1.7

bromoform 103 1.8 101 1.7 108 1.5 isopropylbenzene 118 1.2 114 0.81 123 1.5

bromobenzene 109 0.38 104 1.9 107 1.8

n

- propylbenzene 122 1.3 111 2.0 119 2.1
1,1,2,2

- tetrachloroethane 108 0.63 100 1.5 103 0.83

2

- chlorotoluene 115 0.65 107 1.9 112 2.1
1,3,5

- trimethylbenzene 121 1.2 111 1.4 120 1.7
1,2,3

- trichloropropane 106 1.6 102 2.5 102 1.4

4

- chlorotoluene 113 4.1 106 1.8 110 2.0

t

- butylbenzene 123 0.84 115 1.3 129 0.38 pentachloroethane 109 2.2 103 3.0 112 0.47
1,2,4

- trimethylbenzene 120 0.99 110 2.0 118 1.5

sec

- butylbenzene 125 1.5 115 1.8 129 1.9

4

- isopropyltoluene 123 1.3 112 2.4 123 2.6
1,3

- dichlorobenzene 113 0.85 105 1.7 109 1.5
1,4

- dichlorobenzene 113 1.1 104 2.0 107 1.7

n

- butylbenzene 122 1.3 106 3.6 111 6.5

hexachloroethane 123 0.42 115 0.82 132 1.6
1,2

- dichlorobenzene 111 0.82 104 1.7 108 1.0
1,2

- dibromo

- 3

- chloropropane 105 1.9 99.1 1.9 103 2.4

hexachlorobutadiene 122 2.5 112 3.6 124 2.1
1,2,4

- trichlorobenzene 114 1.3 102 2.3 105 3.0 naphthalene 112 0.77 103 1.0 107 2.1
1,2,3

- trichlorobenzene 114 0.53 103 1.7 108 2.0

a Surface water physical parameters: pH = 7.43; hardness = 154 milligrams/liter (mg/L) (as CaCO 3 ); free chlorine =

2.7 mg/L; total chlorine = 3.7 mg/L.

b RSD = relative percent deviation.524.4

- 49 TABLE 1 2

. INITIAL DEMONSTRATION OF CAPABILITY (IDC) QUALITY CONTROL REQUIREMENTS

Method

Reference Requirement Specification and Frequency Acceptance Criteria

Section

9.2.1 Demonstration of

l ow s ystem
b ackground Analyze a Laboratory Reagent Blank (L RB ) prior to any other IDC steps. Demonstrate that all method analyte s are

< 1⁄2 of the Minimum Reporting Level ( MRL ) and that possible interferences from reagents and glassware do not prevent the identification and quantitation of method analytes

.
Section

9.2.1 Test f or s ystem

c arryover Analyze a LRB after the high calibration

standard during the IDC calibration. Demonstrate that the method analyte s are

< 1⁄2 of the MRL

.

Section

9.2.2 Demonstration of

p recision Analyze 7 replicate Laboratory Fortified

Blanks (LFBs ) fortified near the midrange concentration. Percent relative standard deviation must be

≤ 20%

.

Section

9.2.3 Demonstration of

a ccuracy Calculate average recovery for replicates

used in Section 9.2.2. Mean recovery within + 2 0 % of the true

value

.

Section

9.2.4 MRL c onfirmation Fortify and analyze 7 replicate L F Bs at the proposed MRL concentration. Confirm that the Upper P rediction

Interval of R esults ( PIR ) and Lower PIR (Sect. 9.2.4.2) meet the recovery criteria. Upper PIR ≤ 150%

Lower PIR ≥ 50%

S ection

9.2.5 Quality Control Sample (QCS) Analyze mid

- level QCS

. Results must be within + 30 % of the true

value.524.4

- 50 TABLE 1 3

. ONGOING QUALITY CONTROL REQUIREMENTS

Method

Reference Requirement Specification and Frequency Acceptance Criteria

Section

10.1 Initial ca libration Use the i nternal s tandard cali bration technique to generate a linear or quadratic cal ibration curve. Use at

least 7 standard concen trations.

Validate the cali bration curve as

des cribed in Section 10 .1. 10. When each calibration stan dard is calculated as an unknown using the calibration curve, the lowest level

standard must be within + 50 % of the true value. All other points must be

within + 30 % of the true value.

Section

9.3.1 Laboratory R eagent

B lank (LRB) Analyze one LRB with each Analysis

Batch

. Demonstrate that all method ana lytes

are below 1⁄2 the Minimum Reporting

Level (MRL) and that possible interference from reagents and glassware do not prevent identi fication and quantitation of method analytes.

Section

10.2 Continuing C ali bra

tion C heck (CCC) Verify initial calibration by ana lyzing

a l ow

- level CCC at the beginning of each Analysis Batch. Subsequent CCCs are required after every 10 field samples and after the last field sample

in a batch. The lowest level CCC must be within

+ 50 % of the true value. All other points must be within + 30 % of the

true value.

Results for field samples that are not bracketed by acceptable CCCs are

invalid.

Section

9.3.5 Internal standard (IS) I nternal standards are added to all standards and samples. Peak area counts for each IS must be

within ± 30% of the area in the most

recent CCC and ± 50% of th e average peak area in the initial calibration.

Section

9.3.6 Surrogate analyte s Surrogates are added to all field samples and QC samples prior to analysis

. 70% to 130% recovery

Section

9.3.7 Laboratory Fortified Sample Matrix (LFSM) Analyze one LFSM per Analy sis Batch. Fortify the LFSM with

method analytes at a con centration close to but greater than the nat ive concentrations (if known). For analytes fortified at concen trations

≤ 2 x the MRL, the result must be

within + 50% of the true value. All

other analyte s must be within + 30% of

the true value.

Section

9.3.8 Laboratory Fortified Sample Matrix Dup

licate (LFSMD) or

Field Duplicate ( FD ) Analyze at least one LFSMD or FD with each Analysis Batch. For LFSMDs or FD s, relative percent

differences must be ≤30% (≤50% if
concentration ≤ 2 x the MRL.)

.

Section

9.3.9 Field Reagent Blank (FRB) Analyze FRB if me thod analytes are detected in field samples (except disinfection byproducts)

. Qualify results of any analyte detected in both field samples and the FRB

.

Section

9.3.10 Quality Control Sample (QCS) Analyze mid

- level QCS at least quarterly

. Results must be + 30% of the true

value.524.4

- 51 Figure 1. Mass chromatogram s of "gases " in full scan mode @ 10 μg/L.524.4

- 52 Figure 2a. Reconstr ucted total ion chromatogram full scan mode: 10

- μ g/L procedural calibration standard. See Table 4 for peak number to peak name cross reference.524.4

- 53 Figure 2b. Reconstructed total ion chromatogram full scan mode : 10

- μ g/L procedural calibration standard. See Table 4 for peak

numb er to peak name cross refe rence.524.4

- 54 Figure 2c. Reconstructed total ion chromatogram full scan mode: 10

- μ g/L procedural calibration standard. See Table 4 for peak number to peak name cross reference.524.4

- 55 Figure 3

. Reconstructed total ion chromatogram full scan mode : m ethod analytes fortified into drinking water @ 1 0 μ g/L.524.4

- 56 Figure 4. Mass chromatograms of "gases" in SIM mode @ 1.0 μg/L.524.4

- 57 Figure 5a. Reconstructed total ion chromatogram SIM mode: 1

. 0

- μ g/L procedural calibration standard. See Table 5 for peak number to peak name cross reference.524.4

- 58 Figure 5b. Reconstructed total ion chromatogram SIM mode: 1

. 0

- μ g/L procedural calibration standard. See Table 5 for peak number to peak name cross reference.524.4

- 59 Figure 5c. Reconstructed total ion chroma togram SIM mode: 1

. 0

- μ g/L procedural calibration standard. See Table 5 for peak number to peak name cross reference.