The present invention is directed to systems for detection and analysis of halogenated aromatic hydrocarbons, and more particularly to automated gas chromatographic analysis systems for detection and quantitation of polyσhlorinated biphenyls.

Polyσhlorinated biphenyls (PCB's) have been manufactured and used in large quantity for use as dielectric materials for electrical equipment such as transformers and capacitors. Polychlorinated biphenyls have been conventionally manufactured by chlorinating biphenyl and have been sold as products having a predetermined, desired degree of chlorine substitution of the reaction mixture, generally having a distinctive distribution of PCB compounds and isomers characteristic of the particular PCB product. For example, poly¬ σhlorinated biphenyl compositions having respectively, 41, 42, 54 and 60 weight percent of chlorine have been commercially marketed, each having a different character¬ istic mixture and proportion of PCB compounds and isomers.

Unfortunately, it has now been recognized that such materials pose a significant health threat which has been widely dispersed. Accordingly, methods and apparatus which may be utilized in the field for on site detection and quantitation of such materials would be desirable. Conventional analysis of PCB's in environ¬ mental samples is carried out by extraction of PCB compounds from the environmental sample (oil, sludge, soil, etc.) by means of an organic solvent, which is analyzed by gas chromatograph. However, conventional PCB extraction and gas chromatographic analysis procedures are time consuming and not well adapted for on site utilization by relatively unskilled personnel. Because of the wide spread distribution of PCB's, there is a need for field analysis systems for routine PCB analysis.

Accordingly, it is an object of the present invention to provide improved methods and apparatus for the detection and quantitation of polychlorobiphenyls. It is a further object to provide a rugged, portable instrument and PCB testing procedure which may be utilized by relatively untrained personnel in the field for analysis of PCB's. These and other objects of the invention will become more apparent from the following detailed description and the accompanying drawings, of which

FIGURE 1 is a perspective view of an embodiment of an automated field analyzer system for polychlo inated biphenyls in accordance with the present invention,

FIGURE 2 is a block schematic diagram of various of the components of an embodiment of an automated PCB analyzer like that of FIGURE 1, and

FIGURE 3 is an embodiment of a logic flow diagram for the operation of an automated PCB analyzer like that of FIGURE 1.

Generally in accordance with the present invention, methods and apparatus are provided for the detection and quantitation of polychlorinated biphenyls. In accordance with method aspects of the invention, a predetermined amount of sample to be tested in simultaneously mixed with predetermined quantities of concentrated sulfuric acid and a lower alkane such as hexane. Some samples such as soils may desirably first be extracted with a lower alcohol solvent such as methanol to provide a fluid sample for sulfuric acid/alkane processing. Subsequently, a predetermined sample portion of the hexane phase is subjected to gas chromatographic separation of PCB components and electron capture detection of the separated PCB components.

In accordance with apparatus aspects of the invention, a sample preparation kit is provided comprising means for measuring a predetermined sample

quantity of sulfuric acid and lower alkane processing agents, which are preferably provided in premeasured quantities for individual sample treatment,- and a container for mixing the measured sample and the processing agents. The analysis system further includes an automated, gas chromatographic detector comprising a gas chromatographic column for separating polychloro- biphenyl components, an electron capture detector for detecting separated component peaks from the gas chromatographic column, and means for recording the peak elution times and detector response areas. The apparatus further includes means for storing standard peak elution times and detector response data for a plurality of standard PCB mixtures, means for comparing the sample data with the PCB standard data for recognition of a substantially similar elution pattern therewith and means for calculating the PCB sample concentration of a PCB sample having an elution pattern substantially similar to a stored standard PCB elution pattern. Detector response peak areas and peak elution times are calculated and stored, and subsequently compared with stored peak area and elution time data for a plurality of standard PCB mixtures each comprising a different blend of PCB components. A cosine theta pattern recognition algorithm is particularly preferred for comparison. Upon recognition of similarity with a PCB standard, the PCB concentration is calculated based on detector response, sensitivity and predetermined sample size.

As indicated, in accordance with the present invention, methods and apparatus are provided for the gas chromatographic/electron-capture detection determination of polychlorobiphenyl compounds in transformer oils, sludges, sediments and soils by a field-usable instrumental analysis method. Important features of the system are a sampling pretreat ent kit to extract and isolate PCB's from sample substrates (e.g., oil, soil.

sludge, etc., matrices), and electron-capture detector gas chromatograph apparatus having PCB pattern recognition capability for recognition of specific PCB isomer mixtures. In accordance with various aspects of the present disclosure, PCB determinations may be made in a short time (e.g., less than one hour) by field personnel and without the assistance of personnel skilled in analytical chemistry. In this regard, the extraction and cleanup time can be reduced by direct cleanup and extraction at the test site. For example, a predeter¬ mined quantity, such as a one-gram sample of the sample substrate (transformer oil, soil, etc.), can be transferred to a glass vial having a volume in the range of 40- to 50-ml. Predetermined amounts of concentrated sulfuric acid and a lower alkane partition solvent may be combined with the sample. The sulfuric acid/ alkane processing agents may be conveniently stored, for example, in a quick-break stemmed ampoule, or a glass vial which may serve as the mixing chamber for the sample and processing agents. The components are mixed for a limited time period which may be less than ten minutes and desirably less than a minute. The concentrated sulfuric acid, which desirably is at least 95 percent by weight and preferably 98 percent by weight H SO , does not react with polychlorinated biphenyls, but does react with and retain a wide variety of potentially interfering materials. The PCB compounds themselves are preferentially partitioned into the alkane layer, which separates on the top of the mixture upon cessation of mixing. For simple samples, such as transformer oils, the sample treatment and preparation can be accomplished in a few minutes. For more complicated samples, including solid components, such as soils, sludges, etc., the sample is desirably first extracted with a lower alcohol, preferably methanol. In this regard, a predetermined amount (such as one gram) of the sample is

O ?I_

mixed with a predetermined quantity of alcohol. After mixing, a predetermined amount of the alcohol phase is subsequently utilized as a fluid sample in the previously described alkane/sulfuriσ acid sample processing procedure.

Illustrated in FIGURE' 1 is an automated PCB analysis system 100 which includes a sample preparation kit 104 and a microprocessor controlled PCB analyzer 102. The sample preparation kit 104 includes pipet 103 and balance 105 for measuring predetermined quantities of fluid and solid samples, respectively. The kit further may include a plurality of glass vials 106 containing pre easured quantities of sulfuric acid (5 ml.) and hexane (5 ml.) for sample processing, and a septum-capped vial 107 containing a PCB standard for instrument calibration. Vials containing a premeasured amount of methanol may also be included in the kit 104.

After processing of the sample with the sulfuric acid/alkane mixture, a suitable sample portion of the upper organic (e.g., hexane) phase may be removed by a syringe from the vial 106 and injected into the heated sample inlet of the gas chromatograph detection apparatus 102.

The illustrated apparatus 102 (FIGURE 1) comprises a conventional injection port 108, a printer 110, a carrier gas flow rate indicator and control 112 and a number of indicators and controls including a calibration control 148, an analysis-in-process indicator 134, a sample initiation control 150, a print temperature control 152, an over power indicator 119, and a power "on" control 146.

The portable PCB analyzer 102 illustrated in FIGURE 1 is an automated instrument for identifying and measuring polychlorinated biphenyls such as commercial Aroclor mixtures 1260, 1254, 1242 and 1016 sold by Monsanto Chemical Company of St. Louis, Missouri. The

PCB detection is carried out by utilizing an electron- capture detector equipped gas chromatograph, operated at an elevated temperature, with accompanying -sample plumbing, data processing and output electronics. The instrument 102 is highly automated and field portable» PCB's are recognized using microprocessor controlled pattern recognition techniques, and quantitation is achieved automatically through comparison with known standards. The instrument 102 has in addition, limited ability to compensate for interferences, as will be discussed. PCB detection is accomplished at elevated temperatures with an electron-capture detector in series with a gas chromatographic column. Samples are introduced by syringe injection through a septum into the column by means of the injection port 108. A reference sample of known composition and concentration may be periodically injected into the apparatus 102 to provide periodic calibration and sensitivity checks.

The electron-capture detector utilizes the high electron affinity of compounds with halogen group elements to provide a measurable signal, and is accordingly particularly adapted for PCB determination. A sample is separated into components by means of a gas chromatographic column. For PCB determination, this column may comprise a conventional siloxane polymer (such as OV-101 siloxane polymer of Ohio Valley Company) coated on an inert solid support.

In the detector module, a scandium tritide 3 (Sc Rr. ) foil provides a source of beta particles which ionize dry nitrogen carrier gas and develop a secondary electron flow, termed the standing current. The detector collects these electrons, and an electro¬ meter measures the current. An electonegative material such as a PCB will capture electrons from this ionized gas stream. The presence of an electonegative compound flowing through the detector thus decreases the standing

O PI_

current (by absorbing electrons) in proportion to the concentration of the electron-capturing substance. The electrometer detects this change in current, and provides an output voltage proportional to the concentration of gas.

An important part of the automated PCB analysis instrument 102 is the utilization of microprocessor controlled pattern recognition logic. In this regard, the integrated current/time output of the detector, after injection of the sample is digitally stored by the instrument 102. This set of current/time output (integrated areas) varies for each of the potential PCB mixtures. By comparing the relative output integrated areas at the specific intervals of the gas chromatographic output, pattern recognition routines may be utilized, as subsequently described in more detail, to identify which PCB groups of compounds are present. By comparing the peak area response of the unknown sample with those of standards or calibration mixtures, the amount of each specific PCB can be calculated. By using a constant amount of sample substrate, (such as transformer oil, soil, sludge, etc.), the output may be provided in the units of mg PC _. B (Aroclor type) per kg sample (ppm) .

If the pattern recognition routine cannot clearly discern the presence or absence of any of the common PCB mixtures, the instrument will signal the operator to request more detailed laboratory analysis of the sample, as will be more fully described.

The detector output signal is converted to a succession of digital values which are evaluated within the onboard dedicated microcomputer. This evaluation comprises converting the successive digital values to a series of peak area/retention time pairs. The relative magnitudes of the peak areas and their retention times are compared by the microcomputer to reference data in

its memory to determine if specific PCB mixtures are present. If a specific PCB mixture (Aroclor) is identified, concentrations are calculated in the microcompouter by comparing the peak areas to stored reference data. These concentrations are statistically evaluated, statistically improbable peaks ("outliers") are rejected, and a final mean concentration reported at the printer.

The instrument 102 may be calibrated by means of one or more of a known set of PCB standards in hexane and verifying that the desired output is obtained. If the measured values do not correspond to the actual values for the measured standard, the instrument calibration factors are adjusted to compensate for the deviations. The unprocessed analog signal from the electrometer is available at a BNC connector on the rear panel. This output may be connected to a strip chart recorder set for, 0.5 volt full-scale. Processed data in the form of PCB percentage is provided by means of the paper tape printer on the front of the unit.

The PCB analyzer 102 may also contain suitable programs to plot acquired data on the printer during acquisition, advise the operator of problems encountered with the results and recommend possible solutions to those problems, request injection of calibration check and other quality control samples.

Turning now to FIGURE 2, various internal features of the device 102 will be further described. As illustrated in FIGURE 2, the PCB analyzer 102 comprises a conventional heated sample injection port 108 having a nitrogen inlet port to which may be connected a high purity nitrogen supply 110. Carrier grade or oxygen free nitrogen (N-) is connected to the instrument by means of a flexible tubing. Gas control hardware includes a fitting for an external gas supply on the rear panel of the instrument, a carrier gas flowmeter, metering valve.

and interconnecting plumbing. During operation of the gas chromatograph, nitrogen carrier gas is passed through the column into the electron-capture detector, and then vented. Gas flow may be adjusted, by means of a suitable metering valve, to provide a flow of 25 ml/min, as indicated on the front panel meter. After opening the nitrogen valve, gas must be allowed to flush the lines, gas chromatographic column and detector.

The apparatus 102 further comprises a heated gas chromatographic column 116 located within a suitable insulating oven 114 containing electrical resistance heating elements 137 under control of heating circuit 136. The column output is directed to heated detector 118 which is supplied with pulse generator 119.

The gas chromatograph/detector assembly may be substantially similar to the commercially available electron-capture gas chromatographic apparatus such as that utilized in the Model 215ACA automated monitor of Systems, Science and Software (now S-Cubed) of San Diego, California, and as described in U.S. Patents 4,112,302 and 4,156,813. The gas chromatographic apparatus should be provided with an isothermal oven for maintaining the gas chromatographic column at a desired elevated temperature (180-200° C). A scandium tritide (ScH 3) source is desirably used in the electron-capture detector (to meet applicable NRC regulations regarding transfer and sale of equipment without requiring a special license) . The use of other electron-capture detector beta sources, however, is also contemplated. A heated inlet system sample valve is incorporated to facilitate injection of -liquid samples, and a liquid/gas sample splitting system may be incorporated in the gas chromatograph to facilitate appropriate dilution, as will be more fully described.

The detector output is directed to high gain analog amplifier 120, the output of which is received as

an input to the analog to digital converter 122. The analog to digital convertor receives the analog output from the amplifier 120 and periodically converts this output to a digital value which may be addressed as a digital input to microcomputer 124.

In this regard, the PCB Analyzer 102 incorporates a dedicated microcomputer 124 for analyzing the digitized sample data. The microcomputer is desirably a bus-oriented system such as the Motorola eight-bit 6809 microprocessor chip and associated input-output device circuitry for the microprocessor. The microcomputer system 124 as shown, includes the system I/O devices. A wide variety of peripheral data acquisition systems can be easily interfaced to the PCB analyzer by virtue of its bus-oriented architecture. The A/D converter and microcomputer and microcomputer I/O circuitry 124 operate under the timing control of clock 126. The microcomputer 124 has further data input from programmed read-only memory (PROM) 128, and has operating access to random access memory 130. ^' The microcomputer has as an output device printer 132 and status lights 134 which indicates when a sample is being analyzed.

As indicated, the column is maintained at an elevated temperature by an appropriate analog circuit 138 (the output of which may be adjusted by a suitable trimmer resistor) and resistance elements 137 within the column oven. The circuit 138 is provided with an output light 119 which Indicates when power is being provided to the column oven resistance elements. The output from thermocouple temperature sensing elements in the column is converted to a digital value by the analog to digital (A/D) converter 140, which further provides input to the microcomputer 124. Similarly, the sample injection port and detector are heated to appropriate temperatures by means of similar resistance heating element circuitry 142, 144, respectively. The respective temperature of

- li ¬ the injection port and detector are similarly converted to digital values, by A/D converter 140 and provided in digital form to microcomputer 124. The microcomputer 124 may be directed by the operator to print out the temperature of the injection port, column and detector by "print temp" switch 152. Additional input status switches to the microcomputer are "on" switch 146, calibrate switch 148 and sample switch 150.

A sample to be tested is injected in a conventional manner through a septum into an injection port 108, into a flow of carrier gas, which in the illustrated embodiment 102 is high purity nitrogen. The carrier gas with the injected sample flows through column 116 at a predetermined velocity adjusted by valve and flowmeter. The PCB sample constituents are separated in the column so that they have different elution times. The column discharge flows to the electron capture detector 118 in which the various PCB compounds, if present, absorb the electrons passing between the detector electrodes and disposed within the detector and thereby reduces the electron flow. The decrease in the electron flow is measured and amplified by an analog' amplifier circuit 120 which may be of conventional design.

In this regard, after passing through the column, the carrier gas and any accompanying sample flow to the detector, which includes an electrically conductive housing, a central electrode, and a source of ionizing electrons preferably a beta source such as

3 ScH . The central electrode is encased within and is electrically separated from the electrically conductive housing. A vent for the gas in the housing is provided by a tube connected to the housing and the flow of gas through the system is monitored by a gas flow meter connected to the outlet of the tube. The housing is repeatedly pulsed to a negative voltage by the pulse generator 119. The ionizing source in the detector

^ σvFi

produces energetic electrons by means of radioactive decay. These energetic electrons in turn ionize any gas present between the conductive housing and -the electrode producing less energetic secondary electrons. Repeated pulsing of the conductive housing drives the secondary electrons toward the electrode where they are collected and produce a current which is measured and amplified by an analog circuit. PCB components function as electron capture materials, particularly in view of their halogen content. Accordingly, any PCB elution peak passing through the detector absorbs and thereby reduces the electron flow or current in proportion to the concentration of the PCB component.

FIGURE 3 illustrates a logic flow diagram for the PCB analyzer 102, from which appropriate software coding may be provided. The specific software coding will vary with the particular microprocessor system and associated hardware utilized.

As illustrated in FIGURE 3, upon turning the system on the system waits to achieve the appropriate temperature equilibration conditions in the column, injection port and analyzer by means of calibration routine 302. To carry out a calibration, a predetermined sample size of a predetermined standard PCB mixture is injected into the instrument, and the respective elution peak areas and elution times for the calibration sample are stored in a calibration memory portion of RAM 130. The relative retention times and the peak areas are compared with stored values for the standard in PROM 128. If the calibration values are sufficiently similar to the stored "expected" values, then the instrument is considered to be operating properly and the appropriate calibration sensitivity factors for the Instrument based on the known PCB concentrations in the sample are retained in RAM memory for sample quantitation purposes as will be more fully described. It should be noted that

the hexane portion of the injected sample passes relatively rapidly through the column to the detector, where it is detected. Elution times are calculated from the time of the detection of the hexane carrier. Moreover, relative retention times for the peaks of the calibration sample are important for comparison with the calibration standard, and for this purpose, the elution times are compared by an appropriate normalizing factor which is the ratio of the elution time of the largest peak of the stored standard data to the elution time of the largest peak of the calibration sample.

Upon calibration, the operator may start the testing of an unknown sample by activating the start switch on the PCB analyzer 102 (initiating the start enable module 304) and by injecting the sample. This initiates a sample run, pursuant to which the detector output is converted to digital values and the retention times and the areas of the respective peaks from the sample run are stored in memory 130 by means of routine 306. Upon completion of the run, the retention times and areas are checked against an overflow value by saturation routine 308 to determine whether the sample contained an excessive amount of PCB's to be analyzed. In this regard, the maximum sensitivity of the instrument analog output is nominally 10 volts, and a sample output value of 10 volts for any peak indicates a saturated condition. If the output is saturated, the PCB analyzer routine 310 requests that the operator dilute the sample, by printing out an appropriate message, and enforces a waiting period of up to 30 minutes or more to permit the column to be "flushed out" of the excessive PCB components, which were introduced during the preceeding run. The gas chromatograph inlet system may be modified to permit splitting of the sample by either 1 to 10 or 1 to 1000, and the diluted portion is transferred to the gas chromatographic column. Alternatively, the dilution

step can be handled by transferring a small portion of the organic layer to a separate vial containing a known quantity of pesticide hexane; the diluted sample is mixed carefully and then a portion of the diluted sample is then injected into the gas chromatograph.

In the event that the output is not saturated by exceeding the maximum device output range, the retention time and area information stored for the preceeding run is checked for the existence of peaks by peak detection module 314. If the output is "flat" (i.e., no peaks), routine 317 directs the printer of the device 102 to report that there were no PCB's present in the sample.

In the event that there are peaks present in the stored peak retention time-area information for the sample run, routine 316 of the apparatus 102 determines pattern similarity of this stored sample data, with predetermined stored PCB patterns in the non-volatile memory of the apparatus 102. The pattern similarity algorithm 316 is a cosine theta pattern recognition algorithm utilizing multi-variant statistical analysis. Such pattern recognition algorithms are generally well known. In this regard, the stored peak retention time and peak area data for the unknown sample is represented as a vector in n-dimensional space, as are each of the stored retention time and area data sets for the respective stored PCB patterns. Each respective different peak of the sample (and stored standard data) is regarded as a separate dimension, with the integrated peak height-time area representing the position value of that dimension. The cosine theta pattern recognition algorithm 316 determines the difference in angle between the unknown sample vector in n-dimensional space and each of the respective PCB standard vectors. As previously indicated, it is relative elution times for the measured peaks which is important in the pattern recognition, and the peak elution time/area table for the sample is

"normalized" for the comparison by a factor corresponding to a ratio of the elution time of the largest stored PCB standard peak and the largest sample peak (ratios with several sample peaks may be calculated successively to provide better pattern recognition) . Two thresholds of difference of the sample vector angle from each of the PCB standard vectors are established, and stored in PROM. The first threshold represents substantial similarity or identity between the unknown sample vector and the particular PCB standard vector. The second threshold indicates a strong similarity which is strongly suggestive of the presence of PCB's, which requires further, more detailed analysis. If the difference in angle between the unknown vector, and the closest of the standard PCB vectors stored in nonvolatile memory is below the second threshold, then low match subroutine 318 directs the printer to report the absence of PCBs by module 317 as in the case of the absence of any output peaks from the unknown sample. If the cosine theta correlation between the sample of the n-dimensional unknown sample vector and the most similar standard PCB vector is between the first and second threshold values, but does not equal or exceed the high correlation value, high match subroutine 320 directs through request analysis subroutine 322 that the printer print a message to the operator advising the operator to request further labroatory analysis of the sample.

If the n-dimensional vector angle of the unknown sample has a high cosign theta match (i.e., close to one) with any of the stored standard PCB vectors, as previously discussed, then the quantitative amount of the PCB sample is determined by module 324, based on the current instrument sensitivity factors determined by the calibration run of the calibration standard. The area (peak heigh integrated oven elution time) of each of the stored peaks is converted to a quantitative value, and a

table of quantitative values is stored in the random access memory corresponding to each of the respective peaks stored for the unknown. Each peak may have a different sensitivity and a different calibration factor. For example, a first peak may have an area value of 10,000 arbitrary units which may be converted to a concentration of, say, 50 parts per million by application of the appropriate conversion factors and apparatus sensitivity based on the previous calibration run.

Following the quantitative determination of each of the unknown peaks, subroutine 326 determines the "reasonableness" of the quantitative values of each of the peaks, based on the particular PCB standard with which the unknown sample vector had the closest match. For example, if a particular calculated sample concentration calculated for a peak area deviates by, for example, more than two standard deviations from the mean of the concentration values calculated from all sample peaks, it may be presumed that this component peak may have suffered interference from some other non PCB component, or that other error may be involved. Subroutine 326 eliminates these "outlying" values from the unknown sample concentration tables which were generated by subroutine 324. Using the remaining values which have been determined to be reasonable values, the concentration of the particular PCB is reported, using the mean value of each of the remaining peaks.

The automated apparatus 102 is adapted to require calibration after a predetermined number, here 10, of analytical runs. In this regard, after the reporting of each of modules 312, 317, 322 or 328, a counter is incremented and module 330 determines whether or not a calibration run is necessary.

It will be appreciated that the instrument 102 may be readily used by unskilled personnel for field

analysis of PCB's. In the preparation of dielectric fluid and other oil samples for analysis, a measured amount of the sample is mixed with predetermined quantities of concentrated sulfuric and an aliphatic hydrocarbon, such as hexane. The illustrated sample preparation kit contains an Eppendorf style pipet and disposable tips for use in sampling dielectric fluids. Once the sample has been removed from the transformer or other device containing the oil, it is sampled using the pipet to deliver 100 microliters of sample to a prefilled glass vial 10 containing predetermined quantities of hexane (e.g., 5 ml.) and concentrated sulfuric acid (e.g., 5 ml.). The screw cap of the vial, having an inert poly tetra-fluoroethylene covered septum for purposes of safety is next sealed tightly onto the vial, which is then vigorously shaken for approximately 30 seconds. The layers are then permitted to separate (for most samples this should only require a minute or so) into layers including a lower sulfuric acid layer and an upper hexane layer. The hexane layer sample is now ready for injection into the PCB analyzer 102.

In order to prepare a solid or more complex sample, such as soil, for analysis, a predetermined weight of the solid sample (e.g., one gram) is weighed into a solid sample vial, which in the illustrated embodiment has a volume of 40 ml. for a one gram sample size. A predetermined quantity of methanol from a premeasured vial is added to the sample vial 106, which is then capped and vigorously shaken for 30 seconds. The solid material is allowed to settle to the bottom of the vial, and a 1 illiliter sample of this solution (as a fluid sample) is withdrawn by syringe and placed in a vial containing predetermined quantities of hexane and sulfuric acid, as previously described with respect to dielectric fluid sample preparation. The methanol extracted PCB fluid sample is shaken vigorously for 30

-£UIEX f OMΓ-I

^•

seconds, and the layers are permitted to separate. Upon separation of the layers into an upper hexane layer and lower sulfuric acid, the hexane sample is ready for injection into the PCB analyzer 102, as previously described.

Prior to the analysis of samples, a calibration must be performed, as previously discussed in respect to the processing logic diagram of FIGURE 3. The calibration serves two purposes: 1) it provides a system check to ensure that all parts of the instrument are functioning properly, and 2) it serves to compensate for any daily fluctuations in the response of the analyzer.

Calibration of the illustrated embodiment 102 is carried out by injecting a calibration standard mixture 107 which may be a solution of one part per million by weight of PCB mixture having the polychlorinated biphenyl isomer mixture corresponding to 54 weight percent of chlorine substitution (Aroclor 1254, a product. of Monsanto Chemical Co.) in hexane, a two microliter aliquot of which may be injected into the analyzer in calibration mode. When the calibration analysis is successfully completed, which may take approximately 10 minutes, the instrument is ready for introduction of a sample solution. If the calibration can not be satisfactorily carried out, an appropriate message is printed out to the operator, as previously described.

To carry out an analysis, the SAMPLE button on the front panel of the instrument is pressed by the operator. A two microliter aliquot of the hexane extract from the sample cleanup and extraction procedure is then injected into the injection port of the analyzer 102. The PCB analyzer will automatically initiate an analysis cycle after injection and will compensate for sample-to- sample variation in injection time.

While the present invention has been described for one particular embodiment, it will be appreciated that various modifications may be made within the spirit and scope of the present disclosure.