Document N2Z7a38zQwrQvXRQ3Ox7Jdv7y
CHEMICALS
INTEROFFICE / LAKE CHARLES
TO: DISTRIBUTION FROM: JIM WYCHE
DATE: JULY 25, 1990
RE: ENVIRONMENTAL PROCEDURE II-11 COMPLIANCE WITH VINYL CHLORIDE REGULATIONS
Attached Is your copy of an expanded procedure covering VC
regulatory compliance which replaces existing procedures II10, II-ll, and 11-12. Please see that those needing this information in your organization have access to this document.
DISTRIBUTION;
Manager, Derivatives Area Supervisor, VC-II Area Supervisor, TE-II Area Supervisor, Shipping Area Supervisor, WTU Manager, Operations Services Manager, Maintenance Engineering Foreman, Maintenance, Analyzers Environmental
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ENVIRONMENTAL PROCEDURE. 11-11
TITLE: BESVIAX0RY REFERENCE: OBJECfT*TTE!
Compliance with
vinyl Chloride Regulations
Louisiana Emissions standards for Hazardous Air Pollutants, LAC 33, Part III, Chapter 25
To assure compliance with LDEQ hazardous air pollutant standards (LESHAP) for vinyl chloride and OHC-EDC plants.
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Revised 5/90 Page 2 of 44
ENVIRONMENTAL PROCEDURE 11-11 TABLE OF CONTENTS
INTRODUCTION
I. WHAT IS COVERED
II. FOUR THINGS YOU CANNOT DO
III.
SIX STEPS REQUIRED TO CONSTRUCT A NEW VC OR OHC PLANT OR MODIFY AN EXISTING PLANT
IV. OPERATING STANDARDS FOR VC AND OHC-EDC PLANTS
V. HOW COMPLIANCE IS MEASURED
VI. CALIBRATION AND MAINTENANCE REQUIREMENTS
VII. WHAT RECORDS MUST BE CREATED AND MAINTAINED
VIII. WHAT MUST BE REPORTED TO DEQ
IX. TRAINING
X. SUMMARY OF RESPONSIBILITIES
XI. APPROVALS
FIGURE 1
FIGURE 2
FIGURE 3
PAGE 3 4 5 6
7
18 22 23 26 29 30 41 42 43 44
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Revis d 5/90 Page 3 of 44
A 22H2E XQ compliance WITH miL CHLORIDE REGULATIONS im THE OPERATOR QL YS. AEQ ohc-edc PLANTS
INTRODUCTION
This guide to LDEQ vinyl chloride regulations promulgated
under the Hazardous Air Pollutants requirements of the
f deral Clean Air Act is intended for use by operational
supervision and management who are ultimately responsible for 100% compliance with these regulations. Although other
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groups such as Instrument Maintenance, Shipping, Environmental, and Records, as Indicated herein, are
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responsible for various elements, the overall responsibility for seeing that all things necessary for compliance with these regulations are done resides with Operations, primarily with the Area Supervisors of the VC-II and TE-II production units and WTU. Operations should make such checks as needed
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to assure that not only those items directly in their control taao to
are being done, but also that those to be done by other
groups are, in fact, being done in a timely and appropriate
fashion. In order to make this document as simple and clear as possible, some interpretation and abbreviation of the
e v C e
r gulations has been necessary. For example, rules
P rtaining to PVC manufacturers have been omitted since PPG
does not produce PVC. Questions which may arise, or the need
SL 002251
R vised 5/90 Pag 4 of 44
for further explanation, should be directed to Environmental for resolution. I. WHAT IS COVERED (Applicability!
1) VC-II including OHC-EDC and LP EDC, the latter because OHC-EDC material is processed in the LP EDC portion of VC-II
2) The VC portion of TE-II, but not the DCE or NC sections
3) OHC-II 4) All VC product storage and loading facilities
including the VC tank car loading rack The boundaries of the affected facilities are indicated in Figures 1, 2, and 3. Note that the HC1 by-product from VC production is not covered; neither are any other units not listed or described in the Figures. Some of the standards apply only to elements (i.e., pumps, compressors, pressure relief devices, sampling connection systems, open-ended valves or lines, valves, flanges and other connectors, and control devices or systems required by these regulations) "in VC service" (contains 10% or more VC). For an element to be considered not "in VC service", it must be determined (by testing or by engineering judgement) that the VC content can be reasonably expected never to exceed 10% by weight. These standards are identified herein as applying to equipment "in VC service".
$L 002252
COMFIDENTlALi 1V. fcubjfect to Protective Order
14 th judicial District Court
Ho. 91-1145
R vised 5/90 Pag 5 of 44
Responsibilities: * For advising Environmental of any process changes which
may affect Figures 1, 2, and 3 and/or applicability of these regulations - Area Supervisors VC-II, TE-II, WTU, and Shipping * For identifying equipment and elements "in VC service" Area Supervisors vc-II, TE-II, and Shipping * For advising Operations and Shipping of regulatory changes and their impact and for interpreting the regulations - Environmental * For revising applicability Figures 1, 2, and 3 as necessary - Environmental
Circumvention) (1) Construct a new or modify an existing VC or OHC facility
without first obtaining a permit from DEQ. Modification is any physical change in, or change in the method of operation of, a source that would increase the amount of VC emitted, but does not include routine maintenance, repair, replacement, or increase in production rate if such increase does not exceed the design capacity. (2) Operate in violation of these regulations except in very limited circumstances which could not have been avoided such as an act of God, of war, or of sabotage. (3) Fail to submit the reports and test results required by these regulations.
Revised 5/90 Page 6 of 44
(4) Make any effort to conceal an emission which would otherwise constitute a violation, or to avoid coverage intended by these regulations.
Responsibilities: * For permitting - see Section III * For maintaining operations in compliance - Area
Supervisors VC-II, TE-II, WTU, and Shipping * For reports - see Section VII. * For not circumventing the regulations - Area
Supervisors VC-II, TE-II, WTU, and Shipping
III-,__ SIX STEPS REQUIRED TO CONSTRUCT A NEW VC OR OHC PLANT SR, MSPIEf AN-EXISTING PLANT (Permitting)
1) Obtain a pre-construction permit from DEQ before commencing construction of a new source, or modification of an existing source. Modification is any physical change in, or change in the method of operation of, a source that would increase the amount of VC emitted but does not include routine maintenance, repair, replacement or increase in production rate if such increase does not exceed the design capacity. See the regulations (Par. 2513 and 2551.B.8) for a description of the required contents of a permit application.
2) Notify DEQ of the anticipated date of initial start up <60 >30 days ahead of time.
3) Notify DEQ of the actual start-up date within 10 working days.
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Revis d 5/90 Pag 7 of 44
4) Submit to DEQ an initial report within 90 days of initial start up. See the regulations (Par. 2559.C) for a listing of report contents.
5) Conduct an initial performance test when specified by the DEQ to demonstrate compliance with the 2% allowable leaking valve standard.
6) Conduct an emission test within 90 days of initial start up, providing the DEQ at least 30 days advance notice.
R sponsibilities: * For seeking (through Environmental) a determination of
permitting requirements before commencing construction Derivatives Operations * For providing to Environmental timely, sufficient, and complete information for permit applications, start up notifications, initial report, and initial emission and leaking valve test results reports - Derivatives Operations * For preparing and submitting the permit application, start up notifications, initial report and emission and leaking valve test results - Environmental. * For explaining & interpreting the term, conditions, and requirements of permits - Environmental. For the emission and leaking valve tests - see Section
V.
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CONFIDENTIALi Subject to Protective Order of 14th Judicial District court
No. 91-1145
Revised 5/90 Page 8 of 44
IV,__ OPERATING STANDARDS FOR VC AND OHC-EDC, PLANTS The VC regulations prescribe three types of standards; emission limits, equipment standards, and procedural requirements. A. Emission Limits
1) The concentration of VC in exhaust gases (may be liquid or gas) discharged directly or ultimately to the atmosphere from any equipment used in VC formation and/or purification and in OHC-EDC purification (see Figures 1, 2, and 3 for applicability) shall not exceed 10 ppm. This does not apply to equipment that has been opened in accordance with the vessel opening requirements of these regulations. (See Section c below.) Note that leaks and relief valve discharges (SRVs, PCVs, etc.) are not considered exhaust gases and hence are not subject to the 10 ppm standard. [Vent headers in each area collect regulated exhaust gases for incineration. Extensive systems and procedures are employed to insure all VC vents are incinerated 100% of the time. If the stack monitors indicate the VC concentration in the exit gas is greater than 10 ppm, the operational parameters of the incinerator are checked immediately and, if a reason can be found, corrective action is immediately taken to reduce the VC concentration to less than 10 ppm.
SL 002256
of 14th Judicial
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NO. 91-1H5
Revis d 5/90 Page 9 of 44
2) Emissions of VC from each OHC-EDC reactor are not to exceed 0.2g/kg of the loot EDC so produced. [Because Lake Charles has elected to incinerate this source along with all the other VC regulated vents, this standard does not affect our operations except that venting of OHC reactor emissions to the scrubber must be considered a by-pass of incineration for reporting purposes.]
3) There is to be no non-leak discharge from any relief valve on any equipment nin VC service" (contains 10% or more VC) except for "non preventable" discharges. "Non-preventable" is interpreted by the DEQ to be very restrictive (act of God, war, sabotage, etc). [Extensive design precautions and inspection/testing procedures are used to minimize the potential for SRV releases. See Environmental Procedure 11-13.]
4) Each in-process wastewater stream must be reduced to 10 ppm VC or less before being miXfid with anx other -in-pcggggg waatewatsc containing <l& ppm and feelore halos axpsasd s the atmosphere. [This rule does not preclude mixing with other non-vinvl process water as long as the mixture is ducted to a common control device before being exposed to the atmosphere.] This does not apply to water used to wash out equipment after the equipment has already been opened in accordance with the vessel opening
R vised 5/90 Pag 10 of 44
requirements of these regulations (see Section C
below). This exception also covers purging
wastewater from equipment, sight glasses, etc. for
maintenance purposes. Sampling is also exempted
since the wastewater contains less than 10% VC.
However, any removal of material for processing
such as organic phase or sludge from the CSS feed
tanks must be done without exposing the material to
the atmosphere. (If, because of equipment problems
or process upsets, any in-process wastewater cannot
be steam stripped, the VCM Emission Control SOP
located in each control room is followed.]
5) Any control device employed to meet the
requirements of these regulations must also meet
the 10 ppm VC in exhaust gas standard. [The in-
process wastewater strippers are vented to the
incinerators.]
The percentage of leaking valves "in VC service"
(containing 10% or more VC) must be < 2% in each
process unit, or else more elaborate fugitive
control standards apply).
Responsibilities:
* For keeping all VC exhaust gases in the incinerator
header, routed to incineration, and for avoiding
non-incineration events - Area Supervisors VC-II,
TE-II, WTU, and Shipping
* For avoiding SRV releases - Area Supervisors VC-II,
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CONFIDENT I hy*
it to protective Order
.indicia! District C
of
R vised 5/90 Page 11 of 44
TE-II, and Shipping * For keeping all in-process wastewater contained and
routed to the Central Steam Stripper or TE-XI steam stripper and for avoiding dilution of in-process wastewater before stripping - Area Supervisors ve il , TE-II, and WTU * For operating the incinerators , Central Steam Stripper and TE-II steam stripper in such a manner to achieve the 10 ppm standard - Area Supervisors VC-II, TE-II/ and WTU * For maintaining an up-to-date listing of all equipment and SRVs "in VC service" - Area Supervisors VC-II, TE-II, and Shipping Equipment Standards 1) Pumps, compressors, and agitators "in VC service" (contains 10% or more VC) must be sealless or employ double mechanical seals. For double mechanical seals, the pressure between the two seals must be such that any leak is into the pump [or, in Lake Charles case, into the vent header] and any VC between the two seals must be ducted to a control device achieving the 10 ppm exhaust gas limitation. 2) A rupture disk must be installed between the equipment and relief valves installed on equipment "in VC service" (contains lot or more VC) unless
SL 02259
Revis d 5/90 Pag 12 of 44
the discharge is routed back into the process. 3) A reliable and accurate fixed point area monitoring
system to detect major leaks and identify the general area of.the plant where the leak is located must be installed to minimize leaks from equipment containing 10% or more VC. The monitor must obtain air samples on a continuous sequential basis and analyze the samples by gas chromotography. The location and number of sample points must be consistent with the number of pieces of equipment containing 10% or more VC and the size and physical layout of the plant. 4) A reliable and accurate portable HC detector must be available and used to find small leaks (see section C5 below). 5) Open-ended valves or lines (containing 10% or more VC) must be equipped with a cap, blind flange, plug or second valve which must seal the opening at all times except during operations requiring flow through the open-ended valve or line. For two valve arrangements, the valve on the process fluid end must be closed before the second valve is closed. For double block and bleed systems, the bleed valve or line may remain open during operations requiring venting the line between the two valves but must be capped, plugged, etc. at all other times.
COMF1 DEfTHAlj! Subject to ^otcctive *r
Ko.
R vised 5/90 Pag 13 f 44
R sponsibilities:
* For making sure all pumps comply with the double seal
requirements - Area Supervisors VC-II, TE-II, and
Shipping
For making sure applicable SRVs are protected with
rupture disks and monitoring the disks to promptly
detect and replace disk failures - Area Supervisors VC-
II, TE-II, and Shipping
For making sure the fixed point monitoring system
coverage is appropriate, that the system is operational,
and that portable leak detectors are available in each
area - Area Supervisors VC-II, TE-II, and Shipping
* For seeing that the open-ended valve/line requirements
are met - Area Supervisors VC-II, TE-II, and Shipping
C. Procedural Requirements
1) Opening of equipment/loading lines. The quantity
of VC in any (not limited to 10% VC) VC or OHC
%
equipment must be reduced to 2.0% by volume or 25
gallons, whichever is larger before opening the
equipment to the atmosphere. This would apply also
to purging of liquid from headers and/or knock out
pots. The VC removed in making this reduction must
be ducted to a control device meeting the 10 ppm
standard. This reduction standard also applies to
loading and unloading lines which are not opened
after each operation. For those lines which are
opened after each operation, the standard is no
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order Cc ourt
SL 002261
Revised 5/90 Page 14 of 44
more than 0.13 cubic foot (one gallon) at STP. A written procedure for determining the amount of VC in equipment prior to opening is to be included in the standard operating procedure for the plant. [See Par. 2551.C in the regulations for details. Also see B)6 above for procedures regarding operation of double block and bleed arrangements on open-ended lines.] 2) Manual Venting. Manual venting of gases from equipment "in VC service" (contains 10% or more VC) must be ducted to a control device meeting the 10 ppm exhaust gas standard. 3) Leakage from SRVs. hll&X. Ah pressure release (those containing 10% or more VC), the relief devices must be restored to a condition of no detectable emissions by replacing the rupture disk as soon as practicable, but no later than 5 calendar days after such release unless repair is technically infeasible without a process unit shutdown. In such case repair must occur before the end of the next unit shutdown. 4) Samples - Unused portions of samples containing 10% or more by weight VC must be returned to the process and sampling collection systems must be closed loop with zero VC emissions to the atmosphere. This does not apply to non-extractive samplers or in-line samples (or to in-process
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wastewater since it does not contain 10% or more
VC).
5) All procedural requirements described above must be
incorporated into a standard operating procedure
document available for inspection. This procedure
must include provisions for measuring the VC
content of equipment 1,250 gallons or larger before
opening to the atmosphere.
6) Leak Detection and Elimination - A formal leak
detection and elimination program must be written
and implemented to minimize leaks from equipment
containing 10% or more VC. Two systems are
required, a reliable and accurate fixed point area
monitoring system and a reliable and accurate
portable HC detector. The former is to detect
major leaks and identify the general area of the
plant where the leak is located. The monitor must
obtain air samples on a continuous sequential basis
and analyze the samples by gas chromatography. The
latter is to be used routinely to find small leaks
and to pinpoint major leaks indicated by the fixed
point system. In both cases the location and
number of sample points and frequency of monitoring
must be consistent with the number of pieces of
equipment containing 10% or more VC and the size
and physical layout of the plant.( Incinerator vent
headers are to be included in the monitoring.] ^
SL 002263
CONFIDENTIAL:
Subj ct to Protective Order of 14th Judicial District Court
Wo. 91-1145
Revised 5/90 Page X6 of 44
Areas which do not have equipment containing 10% or more VC (i.e., CSS area) are not required to be monitored. The program must contain two further elements. What constitutes a leak must be defined taking into account background concentration of VC in the area being monitored. The definition need not be the same for all areas of the plant and may be changed over time as background concentrations are reduced. A plan of action to be taken when a leak is detected must be in place. [See the three Lake Charles plans -VC-II, TE-II, and Shipping for details.] The promulgation in 1984 of new fugitive monitoring regulations for volatile hazardous air pollutants required that existing leak detection and elimination plans be demonstrated to be adequate or else be replaced with a program defined in the new regulations. The new regulations also defined acceptable leak repair time. (See 7 below.) Demonstration that an existing plan is adequate is done by means of an annual performance test of 90% of all valves, or 200, whichever is smaller, containing 10% or more VC (except those designated as unsafe to monitor) in each unit (TE-II and VC-II).
7) Leak repair. When a leak is detected, a plan of action must be implemented. Unless repair of a leak is technically infeasible without a process
COfIPl OWIALs
Revised 5/90 Page 17 of 44
unit shutdown, in which case the repair must occur before the end of the next process unit shutdown, a leak must be repaired as soon as practical, but not later than 15 calendar days after it is detected. A first attempt at repair must be made no later than five calendar days after each leak is detected. In the case of valves and flanges, the first attempt should include, but not necessarily be limited to, tightening of bonnet bolts; replacement of bonnet bolts; tightening of packing gland nut; and injection of lubricant into a lubricated packing. Delay of repair for valves is also allowed if it can be shown that emissions of purged material resulting from immediate repair are greater than the fugitive emissions likely to result from delay of repair, and when repair is effected, the purged material is collected and destroyed or recovered. 8) A formal leak detection and elimination program incorporating the above must be written and available for inspection. Responsibilities; For maintaining a written procedure for all procedural requirements in Section c in the standard operating procedure for the unit - Area Supervisors VC-II, TE-II, and Shipping For seeing that the equipment/loading line opening
Revised 5/90 Page 18 of 44
procedures are followed - Area Supervisors VC-II, TE-II, WTU, and Shipping * For abiding by the manual venting rule and for conducting all VC sampling in closed loop samplers, and returning unused samples to the process -Area Supervisors VC-II, TE-II, and Shipping, and Lab * For monitoring pressures and promptly replacing rupture disks under SRVs - Area Supervisors VC-II, TE-II, and Shipping * For abiding by the written leak detection and elimination plan (see plans for details but primarily performing leak patrols, checking fixed point monitoring system reports, and responding to alarms/leaks documenting the response) and for advising Environmental of any revisions/updating required (including revision to definition of a leak) - Area Supervisors VC-II, TE-II, and Shipping * For preparing the written leak detection and elimination plan and for submitting to DEQ leak detection plan revisions -Environmental
3L--HOW. COMPLIANCE. IS MEASURED IEmission Tests, Eniasian
Monitoring) Continuous monitoring of emissions is required,
along with an annual compliance test, to demonstrate
compliance with the 10 ppm standard for emissions and
wastewater.
In addition, an annual performance test must be CONFIDENTIALl
Subject to Protective Order Of 14th Judicial District Court
No- 91-1145
SL 002266
R vised 5/90 Page 19 of 44
performed to demonstrate compliance with the allowable percentage of leaking valves. A. Continuous system for incinerator stacks. The
monitoring system must obtain air samples on a continuous sequential basis from' all emission points for which a standard applies [these have been determined to be the three incinerator stacks (all four incinerators)] and analyze the samples by gas chromatography and record the results. A system to automatically calculate and record emission concentration averaged over each one hour period is necessary to comply with the Quarterly Report requirements. Emergency emission points such as relief valves and scrubber vents (i.e., discharges from OHC Rxs) are exempted from such monitoring. Operation without the monitoring system in service (except for momentary outages for calibration, etc.) would be considered a violation of these regulations. [The three incinerator stacks are sampled at approximately five minute intervals and analyzed by GC with flame ion detection. Results are printed out in the control rooms and alarms sounded whenever the analysis exceeds 10 ppm VC. These monitoring systems receive emergency maintenance service 24 hours per day as needed. Incinerator operators monitor the hourly average values printed out by the systems and "call out" *7
9
analyzer maintenance personnel whenever the analyzer obviously malfunctions*or whenever readings in excess of
SL 002267
Subjrect t?
Order
R vis d 5/90 Page 20 of 44
10 ppm VC are recorded for two consecutive hours and all efforts to correct the problem have been exhausted, and in the case of >10ppm hourly averages, to
Environmental to prepare the quarterly report.]
Annual Compliance Test for CSS and TE-II steam stripper. 7
An annual test for compliance with emission' and wastewater standards must be conducted. [The testing requirement applies to the incinerator stacks and the discharge of the Central Steam Stripper. (CSS) and TE-II steam stripper but does not apply to uncontrolled emergency discharge lines, such as scrubber stacks, that vent through relief valves. Because the continuous
analyzers on the incinerator stacks have been certified through testing as equivalent to the annual compliance test, only the steam strippers have to be tested each year.] The DEQ must be given at least 30 days notice of the testing. Testing requirements are as follows:
1) Adequate sample ports, safe sampling platforms,
safe access to platforms, and adequate utilities must be provided. 2) The testing must be conducted at the maximum production rate at which the equipment will be operated and under other conditions representative of its operation.
3) Each sample must be analyzed within 72 hours of collection and emissions determined within 30 days.
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CONFIDENTIAL: Subject to Protective Order
judicial District Court of l*th
No.
Revis d 5/90 Page 21 of 44
4) Approved test methods must be used. [See Par.
2555.G of the regulations for details.]
C. Valve leaks. Each year, at least 90%, or 200, whichever
is smaller, of the valves in each process unit (VC-II
and TE-II) containing 10% or more VC must be monitored
for leakage with the portable HC detector. The test
must be made by traversing the instrument probe around
the potential leak interfaces as close to the interface
as possible. A reading of >1,500 ppm indicates a leak.
(the regulation specifies 10,000 ppm but PPG has chosen
to use a more stringent standard). Acceptable
performance is 2% or less leakers. These valves are to
be monitored within a one week time frame and the HC
detector must be calibrated on the same day that the
monitoring is performed. (See Section V.) The
percentage leakers must be calculated.
Responsibi1ities:
* For keeping the continuous incinerator stack
monitoring systems in operation - Area Supervisors
VC-II and WTO, and Instrument Maintenance
* For scheduling and conducting the annual
compliance test on the steam stripper effluents and
for notifying DEQ in advance of the test -
Environmental
* For providing appropriate compliance test
conditions and relevant operational data for the
test - Area Supervisors WTU and TE-II
SL 002269
COMF1DBMTIALt Sublet to Pr tective Ord r of 14th Judicial District Court
No. 91-1145
R vised 5/90 Page 22 of 44
* For conducting the annual valve leak performance test - Area Supervisors VC-II and TE-II
VI^ CALIBRATION AND MAINTENANCE REQUIREMENTS An acceptable calibration and maintenance schedule is reguired for the continuous emission monitors, the fixed point monitoring system and the portable HC detector. The schedules must include for the former two, a daily (defined in the Leak Detection Program as 5 days/vk) span check using a concentration of VC equal to that defined as a leak (currently 5 ppm) for the fixed point system and 10 ppm in the case of the emission monitors. Each portable HC detector must be calibrated weekly and, in the case of the annual performance test for leaking valves, be calibrated each day of the test. The HC detector is to be calibrated using a concentration of VC equal to that defined as a leak (currently 10 ppm) for routine testing and using a concentration of 1,500 ppm methane or n-hexane for the annual performance test. The calibration gas cylinder (See par. 2551 and 2643 of the regulations for details on the gas mixtures required.) used for these checks must have affixed (by the supplier) a tag giving the date of preparation, the recommended shelf life, and a certification of the VC (or HC) concentration. The DEQ has indicated that an acceptable plan will also include an annual check of the integrity of the fixed point monitoring system sampling lines by introducing a known concentration of VC into each sample point. All
S(- 002270
CONFIOSHTIALi Subject to Protective Order Of llth Judicial District Court
Ho. 91-1145
R vised 5/90 Page 23 of 44
calibration activities should be documented thoroughly. Responsibilities:
*
* For calibrating each portable HC detector weekly (daily during the annual valve leak performance test) and documenting the results -Instrument Maintenance
* For performing the daily span checks on the incinerator stack monitors and the fixed point monitoring systems Instrument Maintenance
* For performing the annual integrity test on the fixed point systems sample lines - Instrument Maintenance
* For assuring that the calibration gas used is appropriate and that the cylinders are correctly labeled throughout the period of use - Instrument Maintenance For keeping the monitoring systems on line and documenting any down time - Instrument Maintenance
30L. WHAT RECORDS MUST BE CREATED AND MAINTAINED
(Recordkeeping)
A. The following must be created and maintained for a
minimum of 5 years (PPG policy):
1) A record of fixed point monitoring results showing
the concentration of VC, location of each
measurement, and the date and approximate time of
each measurement. Those analyses indicating a leak
must be identified and a brief description of the
cause and corrective action noted on the record. Sub)tCWFptoSctiveOraer^
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Revised 5/90 Page 24 of 44
2) A record of leak patrols conducted with the
portable HC detector, including the identification
of the detector used; the location, date and tine
of leaks found; the cause of each leak; action
taken to repair the leak; and any action taken to
prevent a recurrence of that leak.
3) A record of continuous emissions monitoring data
generated by the incinerator stack monitor. This
record should identify each one-hour period
(interpreted to mean each hour beginning on the
hour) for which the VC concentration averages in
excess of 10 ppm and the reason for such emission.
All three hour averages which include an hour in
excess of 10 ppm should be calculated and made part
of the record.
4) A record of calculated VC emissions to the
atmosphere from venting of OHC reactor emissions to
the vent scrubber (including reactor start-ups).
This record should identify date, time, duration,
total quantity of VC emitted, and whether or not
the 0.2 g/Kg standard was exceeded.
5) A written report of each SRV release, or other
sudden release of VC (regardless of the amount),
containing the information specified in the VC SRV
Release Report (for SRVs) and the Complex
Environmental Incident Report (for all other
releases).
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CONFIDENTIAL: Subject to Protective Order Of 14th Judicial District Court
No. 91-1145
Revised 5/90 Pag 25 of 44
6) A record of calibration and maintenance work done on the portable HC detector, the fixed point monitoring system, and the incinerator stack monitors including dates, nature of work, and downtime.
B. The following must be created and maintained for a minimum of 10 years (PPG policy): 1) A record of annual emission test results (CSS and TE-II steam stripper effluent) including process data needed to define operating conditions at the steam strippers during the sampling. 2) A record of the annual leaking valve performance tests including identification of the valves tested, persons performing the test, and the HC detectors used.
C. The following must be maintained for a minimum of 10 years (PPG policy) after expiration: 1) Permit applications, permits, leak detection plans.
Responsibi1ities:
For verifying that the fixed point and incinerator stack
monitoring system results reports are printing correctly
and advising Instrument Maintenance of any problems --
Area Supervisors VC-II, TE-II, WTU, and Shipping
* For documenting leaks, causes, corrective action, etc.
on the monitoring records from the fixed point systems,
the portable HC detector patrols, and the incinerator
SL 002273
CONFIDENTIAL: Subject to Protective Order of 14th Judicial District Court
No. 91-1145
Revised 5/90 Page 26 of 44
stack monitors, for calculating three hour averages of incineration stack excursions, and for calculating VC emissions from venting of OHC reactor emissions to the vent scrubber - Area Supervisors VC-II, TE-IX, WTU, and Shipping. * For keeping records from the fixed point systems, the portable HC detector patrols, and the incinerator stack monitors for the specified time - Records * For keeping records of SRV releases, other sudden releases, annual emission test results, leaking valve performance tests, permit applications, permits, and leak detection plans for the specified time Environmental * For creating and keeping calibration and maintenance records on the fixed point monitoring systems, the portable HC detectors, and the incinerator stack monitors - Instrument Maintenance
VIII. WHAT MUST BE REPORTED TO DEQ (Reporting Requirements) A. Telephone. The DEQ must be notified immediately but not
later than 3 hours after learning of VC discharges from: 1) SRV releases 2) line or vessel ruptures 3) equipment failures 4) any other sudden release (i.e., CSS system rupture
disk releases) 5) by-pass of VC vents (including OHC reactor vents)
SL 002274
CONFIDENTIAL:
Subject to Protective Order
of 14th Judicial District Court
No. 91-1145
Revised 5/90 Page 27 of 44
from incineration or of wastewater from either steam stripper for more than 60 minutes (in these cases notification must be within 3 hours from beginning of the discharge) [Blown rupture disks on VC vent header systems are considered to be sudden releases rather than incinerator bypasses. VC leaks detected by the fixed point monitoring system or portable HC detector are to be recorded as specified in the leak detection and elimination plan and are exempt from these reporting requirements. The distinction between a leak qualifying for this exemption and a sudden release which must be reported is a gray area. Generally leaks are regarded as slow and non-sudden. A drip or trickle from a corrosion point, bad gasket, valve stem, etc., is considered a leak. A spray which suddenly develops is probably a sudden release. To qualify for the exemption, the incident must be regarded as a leak and be within the area covered by the leak detection and elimination plans.] B. Incident Reports. A written report on each incident listed above must be submitted to DEQ within seven working days after learning of the discharge. The required information is listed in the Lake Charles Complex Environmental Incident Report, and, in the case of SRV releases, in the VC SRV Release Report. In the case of OHC reactor vent bypasses, if the calculations
SL 002275
f **h ^JelaT Wo. 91-j
Order
Jt Court
R vised 5/90 Page 28 of 44
indicate the resultant emissions are within regulatory limits, the report should so indicate. C. Quarterly Report. A written discharge report must be submitted to DEQ by March 15, June 15, September 15, and December 15 of each year. The report must include the identity of the source, date and time of the discharge, and the approximate quantity of VC discharged from any: 1) SRV release, 2) line or vessel rupture, 3) equipment failure, 4) any other sudden release, 5) by-pass of VC vents (excluding OHC reactor
emissions) from incineration or of wastewater from the CSS or TE-II steam stripper (for any period of time). 6) by-pass of OHC reactor emissions from incineration if the 0.2 g/KG standard is exceeded. Xn addition the report must include a tabulation of date, time, and reason for any incinerator stack emission which averaged over any one hour period (interpreted to mean any hour period beginning on the hour) exceeds 10 ppm VC. The highest three consecutive hour average including each one hour excursion is also reported. Lake Charles policy permits repetitive incinerator bypass events separated by less than 15 minutes and stemming from the same cause to be reported as a single occurrence. The results of the annual leaking valve pr "''-nuance tests must be included in the first quarterly
CONFIDENTIAL: Subject to Protective Order of 14th Judicial District Court
No. 91-1145
Revised 5/90 Pag 29 of 44
report following each test. Responsibilities: * for detecting and promptly notifying Environmental of
incidents requiring telephone notification - Area Supervisors VC-II, TE-II, WTU, and Shipping for providing to Environmental prompt and complete written reports of these incidents - Area Supervisors vc-Il, TE-II, WTU, and Shipping * for providing to Environmental on a timely basis the required information on incinerator stack emissions, incinerator bypasses, and steam stripper bypasses - Area Supervisors VC-II, TE-II, and WTU * For making telephone notifications and submitting all written reports to DEQ on a timely basis -Environmental
IX. TRAINING A copy of this procedure is kept in the Control Rooms at VCII, TE-II, Organics Shipping, and WTU. Area Supervisors are responsible for seeing that their personnel are familiar with applicable portions of this procedure through initial training sessions, on-the-job training, and annual training programs. Requirements of the VC regulations are also woven into the SOP manuals in each Control Room. Responsibilities: * For training personnel on the regulations - Area
Supervisors VC-II, TE-II, WTU, and Shipping.
CONFIDENTIAL* Subject to Protective order of 14th Judicial District Court
No. 91-1145
R vised 5/90 P ge 30 of 44
x. SUMMftBX fiE responsibilities
A. Area Supervisor VC-II
1) For advising Environmental of any process changes which may affect applicability of these regulations
2) For identifying and maintaining an up-to-date listing of all equipment and elements "in VC service1* .
3) For maintaining operations in compliance
4) For not circumventing the regulations
5) For keeping all VC exhaust gases in the incinerator header and routed to incineration and for avoiding non-incineration events
6) For avoiding SRV releases
7) For keeping all in-process wastewater contained and routed to the CSS and for avoiding dilution before stripping
8) For operating the incinerator in such a manner to achieve the 10 ppm standard at all times
9) For making sure all pumps comply with the double seal requirements
10) For making sure applicable SRVs are protected with rupture disks and monitoring the disks to detect and replace disk failures
11) For making sure the fixed point monitoring system coverage is appropriate, that the system Is operational, and that portable leak detectors are available
12) For seeing that the open-ended valve/line requirements are met
13) For maintaining a written procedure for all procedural requirements in the standard operating procedure for the unit
14) For seeing that equipment/loading line opening procedures are followed
15) For abiding by the manual venting rule and
SL 002278
CONFIDENTIAL: Subject to Protective order
of 14th Judicial District Court. No. 91-1145
R vised 5/90 Page 31 of 44
conducting all VC sampling in closed loop samplers and returning unused samples to the process.
16) For abiding by the written leak detection and elimination plan and for advising Environmental of any revisions/updating required.
17) For verifying that the fixed point and incinerator stack monitoring systems results reports are printing correctly and advising Instrument Maintenance of any problems.
18) For keeping the continuous incinerator stack monitoring system in operation
19) For conducting the annual valve leak performance test
20) For documenting leaks, causes, corrective actions, etc. on the monitoring records from the fixed point systems, the portable HC detector patrols, and the incinerator stack monitor.
21) For calculating and providing to Records the required information on VC emissions from venting of OHC reactors to the vent scrubber.
22) For detecting and promptly notifying Environmental of incidents requiring telephone notification of DEQ
23) For providing to Environmental prompt and complete written reports of these incidents
24) For providing to Environmental on a timely basis the required information on incinerator by-passes and incinerator stack emissions including three hour averages for each >10 ppm incinerator stack incident.
25) For training personnel on the regulations1
SL 002279
1 CONFIDENTIAL:
Order
, Duoject to ProtBSfcivtcerdonrt P ith Judicial Dj*rict Court
No. 91-1145
Revised 5/90 Pag 32 of 44
Area Supervisor TE-II
1) For advising Environmental of any process changes which may affect applicability of these regulations
2) For identifying and maintaining an up-to-date listing of all equipment and elements "in VC service"
3) For maintaining operations in compliance
4) For not circumventing the regulations
5) For keeping all VC exhaust gases in the incinerator header and routed to incineration and for avoiding non-incineration events
6) For avoiding SRV releases
7) For keeping all in-process wastewater contained and routed to the CSS or TE-XX steam stripper and for avoiding dilution before stripping
8) For operating the TE-XX steam stripper in such a manner to achieve the 10 ppm standard at all times
9) For making sure all pumps comply with the double seal requirements
10) For making sure applicable SRVs are protected with rupture disks and monitoring the disks to detect and replace disk failures
11) For making sure the fixed point monitoring system coverage is appropriate, that the system is operational, and that portable leak detectors are available
12) For seeing that the open-ended valve/line requirements are met
13) For maintaining a written procedure for all procedural requirements in the standard operating procedure for the unit
14) For seeing that equipment/loading line opening procedures are followed
15) For abiding by the manual venting rule and conducting all VC sampling in closed loop samplers and returning unused samples to the process.
SL 002280
CONFIDENTIALi Subject to Protective Order of; 1*1 tii Judicial District Court
No. 91-U45
Revis d 5/90 Page 33 of 44
16) For abiding by the written leak detection and elimination plan and for advising Environmental of any revisions/updating required.
17) For verifying that the fixed point and incinerator stack monitoring systems results reports are printing correctly and advising Instrument Maintenance of any problems.
18) For providing appropriate compliance test (for steam stripper effluent) conditions and relevant operational data for the test
19) For conducting the annual valve leak performance test
20) For documenting leaks, causes, corrective actions, etc. on the monitoring records from the fixed point system, and the portable HC detector patrols
21) For calculating and providing to Records the required information on VC emissions from venting of OHC reactors to the vent scrubber.
22) For detecting and promptly notifying Environmental of incidents requiring telephone notification of DEQ
23) For providing to Environmental prompt and complete written reports of these incidents
24) For providing to Environmental on a timely basis the required information on incinerator by-passes
25) For training personnel on the regulations
SL 002281
, &SSZ&.
w
Revised 5/90 Page 34 of 44
Area Supervisor Shipping 1) For advising Environmental of any process changes
which may affect applicability of these regulations 2) For identifying and maintaining an up-to-date
listing of all equipment and elements nin VC service" 3) For maintaining operations in compliance 4) For not circumventing the regulations 5) For keeping all VC exhaust gases in the incinerator header and routed to incineration and for avoiding non-incineration events 6) For avoiding SRV releases 7) For making sure all pumps comply with the double seal requirements 8) For makina sure applicable SRVs are protected with rupture disks and monitoring the disks to detect and replace disk failures 9) For makina sure the fixed point monitoring system coverage is appropriate, that the system Is operational, and that portable leak detectors are available 10) For seeing that the open-ended valve/line requirements are met 11) For maintaining a written procedure for all procedural requirements in the standard operating procedure for the unit 12) For seeing that equipment/loading line opening procedures are followed 13) For abiding by the manual venting rule and conducting all VC sampling in closed loop samplers and returning unused samples to the process. 14) For abiding by the written leak detection and elimination plan and for advising Environmental of any revisions/updating required. 15) For verifying that the fixed point monitoring system results reports are printing correctly and advising Instrument Maintenance of any problems.
___
$L 002282
Revised 5/90 Page 35 of 44
16) For documenting leaks, causes, corrective actions, etc. on the monitoring records from the fixed point system, and the portable HC detector patrols
17) For detecting and promptly notifying Environmental of incidents requiring telephone notification of DEQ
18) For providing to Environmental prompt and complete written reports of these incidents
19) For training personnel on the regulations
SL 002263
CONFiOENTlAt.' ^
R vised 5/90 Page 36 of 44
D. Area Supervisor WTU
1) For advising Environmental of any process changes which may affect applicability of these regulations
2) For maintaining operations in compliance 3) For not circumventing the regulations 4) For beeping all VC exhaust gases in the incinerator
header and routed to incineration and for avoiding non-incineration events
For beeping all in-process wastewater contained and routed to the CSS and for avoiding dilution before stripping
For operating the incinerators and CSS in such a manner to achieve th(<).0 pp^standard at all times For seeing that equipment/loading line opening procedures are followed
For verifying that the fixed point and incinerator stacb monitoring systems results reports are printing correctly and advising Instrument Maintenance of any problems.
For beeping the continuous incinerator stacb monitoring system in operation
For providing appropriateticomjHiance test (for the CSS effluent) conditions and relevant operational data for the test
For documenting causes, corrective action, etc. on the monitoring records from the incinerator stacb monitors
12) For detecting and promptly notifying Environmental of incidents requiring telephone notification of DEQ
13) For providing to Environmental prompt and complete written reports of these incidents
14) For providing to Environmental on a timely basis the required information on incinerator by-passes and incinerator stacb emissions including three hour averages for each >10 ppm incinerator stacb incident
For training personnel on the regulations
SL 002284
CONFIDENTIAL: Order subject to lWfESSl ct Court
o mh 0uel.l_14S
Revised 5/90 Pag 37 of 44
Derivatives Operations 1) For seeking (through Environmental) a determination
of permitting requirements before commencing construction 2) For providing to Environmental timely, sufficient, and complete information for permit applications, start-up notifications, initial report, and initial emission and leaking valve test results reports
SL 002285
Subject
of 14th J
Revis d 5/90 Page 38 of 44
Instrument Maintenance
1) For keeping the fixed point and continuous monitoring systems on line and documenting any downtime .
2) For calibrating each portable HC detector weekly (daily during the annual valve leak performance test) and documenting the results
3) For performing the daily span checks on the continuous emission monitors and fixed point monitoring systems
4) For performing the annual integrity test on the sample lines for the fixed point systems
5) For assuring the calibration gas used is appropriate and that the cylinders are correctly labeled throughout the period of use.
6) For creating and keeping calibration and maintenance records on the fixed point monitoring systems, the portable HC detectors, and the incinerator stack monitors.
SL 002286
COHF1PEHT1AL* SuMrot to Protective Ord
r 'Judicial District
No. 91-1145
Revised 5/90 Page 39 of 44
Environmental
1) For revising applicability Figures l, 2, and 3 as necessary
2) For advising Operations and Shipping of regulatory changes and their impact and for interpreting the regulations
3) For preparing and submitting permit applications, start-up notifications, initial reports, and emission and leaking valve test results
4) For explaining and interpreting the term, conditions, and requirements of permits
5) For preparing and submitting to DEQ leak detection plans and revisions
6) For scheduling and conducting the annual compliance test on the steam stripper effluents and for notifying DEQ in advance of the test
7) For keeping records of SRV releases, other sudden releases, annual emission test results, leaking valve performance tests, permit applications, permits, and leak detection plans for the specified time
8) For making all telephone notifications and submitting all written reports to DEQ on a timely basis
SL 002287
tto "
Revised 5/90 Page 40 of 44 H. Lab 1) For returning unused samples to VC-II I. Records X) For keeping records from the fixed point systems, the portable HC detector patrols, the incinerator stack monitors, and calculated OHC reactor emissions from scrubber venting for the specified time (5 years)
002288
X. APPROVALS:
Revised 5/90 Page 41 of 44
SL 002289
l\>*
cP .,,C\0AVv'
&
SL 002290
INCINERATION
VENT HE/vOER \t> INCINERATOR ^ --------------------------------------- --------------------------
l
VC FURNACE
VC.EDC HCL
VC ABSORBER _______
HCL - -----------
STRIPPER
VC PRODUCT
SKLL
vO I'ROI/.Uul lu SIOPAuE/SI III'L ING
RECYCLE]
VENT HEADER TO INCINERATOR
--
one
RXS HtL
DH STILLS
CRUDE
STG
V 4%
%% %
4
INTER STG
TANKS
* a / qL 7> Av;V*s.a*
S %
CV ^V_
FIGURE 1. VC-II
LIGHTS STILL
I TVS STILL
HEAVIES IO BOTTOMS I'lAfll
SL 002291
CO
o flAi -)H
o
ro
OHC
PHASE
|
1 It-II
/
A/or COUFPFD
N3 CO
___
CHLORAL -[ STEAM
ro RXS
SEP.
TRMT
1 STRIPPER
' WTU
ORGANICS PIXYClEb ro proc ess
VC -
*[ OSS
I EEIj TANKS
ui OHC
O w.
R>.S
!?o--*4W-u>t-*ohMv;*O*t-jrfS<-*oftj-fc*t*of7i9nfi<t*t*oa<M'*aw5Hp%m!>;*!*i K- <& orr O
I I' .1101
ccc a*<**
NAOH
PHASE 4
SEP
(ALL VE:rJT=. COLLECTED FOR INCINERATION)
r
Eiri-UENl 10 OIIIFAII
x IN-PROCESS WASTEWATER Sr STEM
)
\
\
}l
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farnff obtcK
fi tf&ftxud jb cd&i^et ffu.%.
^ toMkbs & foflj bApidaut oj cur aMUu {ffi*j f&j uftndd (U#u pej^dif^ fliM 1pu*A& lijoncW od<Q tj, (|^ S3yewfc (MuhAAs f Butl^ ff^oW frdAJ {&
vS*e aifatfuA, ( Co u>i fiu& .
J^awu^ --
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fa
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, b*t *Aut
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U3W^it{ * (pMd4&M& (Al igwtflfac^ % jidshJ KranJtdb& ^
(*, p cU^WC olio^a** jct^
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* JZ_________ __ 2L. ' V
'V
Ut "*|uMf
9yfa& i
fowfiC, tuf cmh 4fcfjtfb.
SLfaamj^lt Zsfawcjfapw ouSwsfa.
<2<foc t/Adds o^ uttctuir
lAi W fldhbuuk ovaf^io
SL 002293
'tH'
6Bb1* "
ok&ntfa *
1: WHY MULTIVARIATE CONTROL ? CONSIDER A SITUATION WHERE THERE ARE ONLY TWO VARIABLES OF
INTEREST/ SAY X, AND Xj. NOW IF X, OPERATES INDEPENDENTLY OF X2 THEN THEIR CORRELATION COEFFICIENT R WILL BE CLOSE TO ZERO AND THE SCATTERPLOT OF DATA ON THESE TWO VARIABLES WOULD APPEAR AS A CIRCLE/ PROVIDED THEY ARE NORMALLY DISTRIBUTED/ E.G.,
* 't
f' ' \ *
NORMALITY WILL BE ASSUMED ON ALL VARIABLES SEPARATELY AND JOINTLY. NOW SUPPOSE THE TWO VARIABLES X1 AND Xj, ARE NOT INDEPENDENT.
THE CORRELATION COEFFICIENT AS MEASURED BY R WILL BE DIFFERENT FROM ZERO AND THEIR SCATTERPLOT WILL TAKE AN ELLIPTICAL SHAPE SUCH AS:
SL 002294
CONFIDENTIAL:
Subject to Protective OrAef 14th Judicial District Court
X%
4 /
**
X
I
THIS ELLIPTICAL SHAPE WILL TILT UP IF R>0 AND TILT DOWN IF R<0. THE IMPORTANT THING TO NOTE IS THAT IF X, IS AT A PARTICULAR
VALUE THEN Xj DOES NOT RANGE OVER ITS ENTIRE RANGE.
IT IS FOR THIS REASON THAT WE MUST LOOK AT TWO CORRELATED VARIABLES TOGETHER INSTEAD OF SEPARATELY.
SL 002295
2J MULTIVARIATE CONTROL AGAIN LET'S CONSIDER THE BIVARIATE CASE/ TWO VARIABLES X, AND
X2. IF INDIVIDUAL CONTROL CHARTS ARE RUN ON THE VARIABLES SEPARATELY, THEN THE JOINT CONTROL REGION WOULD APPEAR AS A BOX, I.E.,
- MCL
lcl -X.
LCL
*1
NOW IF THE VARIABLES ARE INDEPENDENT (UNRELATED) THEN THE BOX CONTROL REGION IS CORRECT. BUT IF X, AND X2 ARE DEPENDENT (CORRELATED,|R|>0) THEN THE JOINT CONTROL REGION SHOULD BE A
SL 002296
WITH THESE TWO GRAPHS SUPERIMPOSED ON ONE ANOTHER, IT IS EASY TO SEE THAT THE RECTANGLE REGION WOULD GIVE INCORRECT SIGNALS SAYING EVERYTHING IS IN CONTROL WHEN IN FACT ITS NOT.
NOW THIS CAN BE DONE BY HAND, THAT IS THE COMPUTING OF THE ELLIPSE, IF WE HAVE A BIVARIATE SITUATION. IN MOST CASES WE'RE DEALING WITH A TRULY MULTIVARIATE SITUATION, MAKING IT IMPOSSIBLE TO DO BY HAND.
3s THE MULTIVARIATE SITUATION IN THE MULTIVARIATE SITUATION WE HAVE p, THE NUMBER OF
VARIABLES, GREATER THAN TWO. EACH OBSERVATION ON p-VARIATES TAKES THE FOLLOWING FORM:
OBS.X OBS.2
X, Xj Xj ................... Xp X, X, X, ................... Xp
OBS.n
X, Xj Xj ................ Xp
THIS GIVES A DATABASE OF n OBSERVATIONS ON p-VARIABLES. FROM THIS DATABASE A CORRELATION MATRIX CAN BE COMPUTED. ITS FORM IS GIVEN BELOW:
SL 002297
CONFIDENTIAL:
act to Protective Ordf
f
h Judicial District Court Ct, "ift
1 Rl2 ^13 R21 1 ^23 * * ' ^2p
Rpi Rp3 Rp3 1
WHERE RfJ IS THE CORRELATION BETWEEN X, AND X;.
NOTE THEE
CORR(X,,X,) IS ONE, SINCE EVERY VARIABLE IS PERFECTLY CORRELATED
WITH ITSELF.
MOST OF THE WORK DONE IN MULTIVARIATE QUALITY CONTROL USES THE
CORRELATION MATRIX AS DEFINED ABOVE OR ITS COUNBTERPART THE
VARIANCE CO-VARIANCE MATRIX. (NOT DISCUSSED HERE.) THE CONTROL
REGIONS ARE VERY DEPENDENT ON THESE MATRICIES.
THE ELLIPITICAL REGION THHAT IS GENERATED IN THE TWO DEMENS ION
SITUATION (X^Xj) BE COMES AN ELLIPISOID IN THREE DIMENSION
(X1,X2,X,) AND A HYPER-ELLIPISOID IN HIGHER DIMENSION. THESE ARE
THE GEOMETRICAL NAMES OF THE CONTROL REGIONS. AS STATED EARILIER,
IT IS NEARLY IMPOSSIBLE TO COMPUTE THESE REGIONS BY HAND. BUT WE
DO HAVE COMPUTER PROGRAMS THAT ARE CAPABLE OF GENERATING THESE REGIONS. SCOUT IS ONE OF THEM.
SL 002298
subset to Protective Order Of 14th Judicial District Coui
No. 91-1145
4: THE SCOUT PROGRAM, A TOOL FOR MULTIVARIATE QUALITY CONTROL. FIRST OF ALL THE SCOUT PROGRAM IS FREE. (PUBLIC DOMAIN) IT WAS
CREATED BY LOCKHEED ENGINEERING AND SCIENCE COMPANY FOR THE EPA'S QUALITY ASSURANCE AND METHODS DEVELOPMENT DIVISION. ITS MAIN PURPOSE IS TO DETECT OUTLIERS (DISCORDANT OBSERVATIONS). OUTLIERS ARE DEFINED AS OBSERVATIONS THAT ARE HIGHLY UNUSUAL WHEN COMPARED TO THE REST OF THE DATA. THIS IS VERY CLOSE AKIN (ESSENTIALLY THE SAME) TO DETECTING WHEN THE PROCESS IS OUT OF CONTROL.
TO BETTER UNDERSTAND THIS CONSIDER THE FOLLOWING CONTROL CHART FOR A UNIVARIATE SITUATION:
/
HISTORICAL DATA X1, Xj, ..., Xn ARE USED TO ESTABLISH THE CONTROL
CHART. NOW SUPPOSE WE HAVE A NEW OBSERVATION, SAY X^, AS
INDICATED ON THE CONTROL CHART. IF THIS BE THE CASE, THIN THE
PROCESS IS OUT OF CONTROL. NOW CONSIDER THE HISTORICAL DATA WITH
xncw' *
Xl, Xj, Xj, . .., X^f Xggy
IF X^ IS ATYPICAL TO THIS GROUP (X,, X^ Xj,...,,,) THEN IT WILL BE
SL 002299
owrtffiamML:
Subj ct to of 14th Judicial! District Court
Wo, WrU*5
DESIGNIATED AS AH OUTLIER WHEN COMPARED TO THE GROUP. IT IS IN THIS WAY THAT SCOUT CAN BE USED TO MONITOR A
MULTIVARIATE SITUATION. IF A NEW OBSERVATION IS DECLARED AN OUTLIER THEN THE PROCESS IS OUT OF CONTROL, OTHERWISE CONTROL IS BEING MAINTAINED, i.e., THE NEW OBSERVATION IS LIKE THE HISTORICAL DATA SET.
5: THE USE OF SCOUT TO BEGIN USING SCOUT FOR MULTIVARIATE QUALITY CONTROL, ONE
MUST FIRST UNDERSTAND ITS FUNDAMENTALS. IT IS BASICLY A RUN PROGRAM AND IS MENU DRIVEN. A WRITTEN TEXT IS INCORPORATED UNDER THE MENU 'SYSTEMS' WHICH GOES INTO SUBMENUS SUCH AS INTRODUCTION, FILE MANAGEMENT, DATA MANAGEMENT OUTLIER TESTING, tc. IF YOU'RE TO BE SUCCESSFUL IN USING SCOUT, THIS SECTION NEEDS TO BE READ AND RE-READ. COMPLETE UNDERSTANDING COMES WITH USE.
YOUR FIRST PROBLEM WILL BE ENCOUNTERED WITH FILE AND DATA MANAGEMENT. SCOUT DOES NOT ALLOW DIRECT ENTRY OF DATA INTO THE PROGRAM, NOR DOES IT ALLOW MAJOR INTERNAL CHANGES IN THE DATA FILE WHILE IN THE PROGRAM. SO ALL 07 YOUR DATA FILES MUST BE CONSTRUCTED AND MANIPULATED OUTSIDE OF SCOUT. THIS CAN BE DONE USING SOME OTHER DATA MANAGEMENT PROGRAM SUCH AS LOTUS. SCOUT DOES REQUIRE THAT DATA FILES BE OF A CERTAIN FORMAT (GEO-EAS FORMAT) WHICH IS EXPLAINED WITH EXAMPLES IN 'SYSTEMS'.
SL 002300
. .i
' ' '
w iftil Jswl.iciaf StSsttriLfit I 3
THE FOLLOWING IS A STEP-BY-STEP PROCEDURE FOR USING SCOUT TO CONTROL A MULTIVARIATE PROCESS.
1. CONSTRUCT A HISTORIAL DATA FILE (HDF) RECALL THIS MUST BE DONE OUTSIDE SCOUT BUT FOLLOWING THE
GEO-EAS FORMAT. TWO- THINGS TO NOTE THAT ARE NOT INCLUDED IN SCOUT'S MANUAL/ SCOUT WILL NOT ACCEPT A DATA FILE WITH ZERO AS A CONSTANT VALUE FOR A GIVEN VARIABLE. ALSO/ CERTAIN MENUS WILL NOT WORK ON A DATA FILE WHEN A VARIABLE IS CONSTANT AT SOME VALUE OTHER THAN ZERO.
2. ONCE HDF IS CONSTRUCTED ENTER SCOUT. UNDER MENU OUTLIER'/ RUN AN OUTLIER TEST. THE PURPOSE OF THIS TO PURGE HDF OF ATYPICAL OBSERVATIONS. RECALL YOU'LL HAVE TO EXIT SCOUT AND CREATE A NEW FILE BY DELETING THE OUTLIERS. I'LL REFER TO THIS NEW FILE AS HDF (OUT). THERE ARE OTHER WAYS OF HANDLING THIS/ E.G./ SCOUT WILL AUTOMATICALLY FLAG ALL OBSERVATIONS THAT ARE DECLARED AS OUTLIERS AND YOU'LL HAVE THE OPTION OF EXCLUDING THEM FROM ANY CALCULATIONS OR STATISTICAL PROCEDURES. HOWEVER/ I RECOMMEND REMOVAL. EXPLANATION WILL BE GIVEN LATER. SAVE HDF (OUT) AS A SCOUT FILE.
STUDY HDF (OUT). RUN SUB-MENU STATISTICS UNDER 'DATA'. EXPLORE THE GRAPHICS MENU. IF YOU UNDERSTAND RUN A PCA ON THE DATA. (DISCUSSED LATER). EXPLORATION DEPENDS ON YOUR STATISTICAL KNOWLEDGE BUT IS NOT NECESSARY TO ACHIEVE GOAL OF MULTIVARIATE QUALITY CONTROL.
3. CONSTRUCT DATA FILE OF NEW OBSERVATION(S) FOLLOWING THE SAME FORMAT AS HDF (OUT) . I'LL REFER TO THIS NEW DATA; FILE AS
SL 002301
CUWFlDENTlALt
fiubjfeCt to Protective Order
of Itth Judicial Oietrict Court
Wo.
5
DATA (NEW). TAKE DATA (NEW) INTO SCOUT AND SAVE AS A SCOUT FILE. APPEND DATA(NEW) TO HDF(OUT). REFER TO THIS NEW FILE AS HDF(APP). SAVE AS A SCOUT FILE.
4. MOVE TO 'OUTLIER* MENU AND RUN OUTLIER TEST ON HDF(APP) . IF THE NEW OBSERVATION(S) IS NOT DESIGNATED AS AN OUTLIER, THEN THE PROCESS IS IN CONTROL. IF THE NEW OBSERVATION(S) IS DECLARED AN OUTLIER, RUN THE SUB-MENU 'CAUSAL'. 'CAUSAL' IS A SUB-MENU THAT WILL PICK THE PARTICULAR VARIABLES(S) THAT STATISTICALLY CAUSED THE OBSERVATION TO BE DISCORDANT. A NOTE OF CAUTION. THIS IS A STATISTICAL PROCEDURE THAT WILL PRODUCE A STATISTICAL CAUSE OF DISCORDANCE. IT IS NOT TO BE INTERPRETED LITERALLY. USE YOUR KNOWLEDGE OF THE PROCESS - EXAMINE THE OBSERVATION - MAKE A DECISION PERTAINING TO THE OBSERVATION.
YOU HAVE ACHIEVED YOUR OBJECTIVE WITH THE COMPLETION OF THE ABOVE FOUR STEPS.
SL 002302
^rtyc-. a
co^ 'C \V>
V