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FOR DU PONT USE ONLY AR226-2909 W. A. FINTEL TEXTILE FIBERS DEPARTMENT SEAFORD November 22, 1982 OM^^, [TRIAL ^YGIEME SURVEY C"UyR^INfNGT: HPERIMBACRF YAkAaP'APL-IC-A'-T-ION OF ratory Report No. SUMMARY An industrial hygiene survey September 20, 1982. Areaj and was conducted at Seaford on determine the ^"^^llbers :" personnel samples r^e^sB^HfSIMeaBfollrldBBtfC'JF spinning were collected to machine operators off---------- during primary-application 7.3nig/n^ofH LOGAN, ^^.jSa neywiere r ipnngres evaluated ults usin g r a t n h g e e d c o from mput e 0 r . 4 to This recommL.--,- in Du [Font Safety confirmed that; exposures do Engineering Standard program S-12-T. of exceeding the 5 mg/m AEL is not less exceed the than 5%). AEL (pro* ^ility BACKGROUND which has a application _- oi as a contaminaf n f -- -- ^ ^ B ^ 'tlfa--sa--n fbaq^uewoeuisghbt.asecontainuad^BBB ^B^B^B^B^B^BmBdRymJ201is'^e01v1o1lw1"^!^^^w}^)!^!^^5^^^^^ - 'or a^ thenSar degradatfon^roduct. Present commercial run whj primary finish toig^ and finish roll spe Hot chest rpm. a 28-position was applied as a. Rperatures were 180^C Company SanUized. Doss not contain TSCA C% AIR SAMPLING AND ANALYSES J--m--i--fUI^--^^--^^^^w^^a^s^MI^^' collected on Tenax*-GC Cubes. Air was d tnrougnehe^ioss ;by Du Pont Model P-200 pumps calibrated at about 60 raL/min. Ten(ax-GC tubes were thermally desorbed ct 200C using an Envirochem Unacon Series 810 Thermal Desorber at Seaford. The carrier gas was nitrogen. Samples were analyzed on a Hewlett-Packard Series 5840 ais chromatograph equipped with a 3.26' x 1/8" stainless steel column packed with 15% Igepal* C0880 and 5% potassium hydroxijde on Chromosorb W. A flame loniza^on^ RESULTS ; offuj The eight personnel samples indicated thatuBBj concentrations ranged friom 0.7-1.6 mg/m , and areasanples ranged frwo.m 0e\ .4ji-_1i .6r _mg.//_m-- . mThLe_;j it.hl.r_e__e;bL.lIa-.n_i.._ L. i---i.dj ily.. s_.u.tb-_m: i1t.t1e._d.3 a-_s samples had low background levels of W^WTable I). Calculated eight-hour Time Weighted Average ("WA^^qSosures for the spinning machine operators and tu aers^r^presented in Table II? they ranged from 0.9-1.2 mg/m An explanation of TWA calculations is in Appendix ' DISCUSSION AND CONCLUSIONS Du Font Safety Engineering Standard S-12-T "Strategy for Workplace Sampling for' Ebcposure to Chemicals;" presents a strategy for air sampling and analysis. This analysis was done using the computer program LOGAN and is attached as Appendix.I. The five eight-hour TWA land four area samples collected around Spinning Machine 35 were.' combined because the omega statistic indicated that they were' from a single distribution (see S-12-T). Results indicate that there is less than a 5% probability of exposure exceeding the 5 rag/m AEL. These jobs should be resampled at least once per quarter for a year, to provide a good history on which to basel needed routine sampling frequency. The higbesty|Hfj7al|jes obtained for personnel samples (7.3 and 2.8 mg/m") were from; Tenax-GC tubes analyzed at Jackson Laboratory. Jackson Labarafeory uses ion selective chromatography to det&rmi.ne total fluorLde; it is assumed that all fluorideii amount of flucrids reported. contain -ySCACB^ Does"01,t CoroP8^ Saniilized. collecSteeadfob-r-ed_c--'sa--u_sa--enatlhye-ti--cf^a^-ualimGemeiAtohuoniidAizicamat^aiy^oonnalsdQoeeiteocvteorrescaknimateulff\ finish components that borne off the measure other fhvw agacsket ig<to-.g-.r--ap~hi. ----- Alenaarolyrt^icKaelseSaercctfifornff,i^revej Topnent and the Haskell Laboratory Report by; ^-/ ''7~C/~:' ' //^. ''''' /^'^y Christopher wiernicKi Industrial Hygienist Approved bys Stephen W. Dixon Section Supervisor Industrial Hygiene - 3 - .nTSCACSl Ooes "0AconW Sawa' ued. COWP^ TABLE I FOvfSffHSfHfIl RESULTS OF AIR SAMPLING AROUND BCF SPINNING MACHINE 35 ON SEPTEMBER 20, 1982 Sample Air Vol Tin.e (L) (Min) 8.0 128 9.6 158 H-82-52-4 H-82-52-5 H-82-52-6 H-82-52-7 H-82-52-8 H-82-52-9 H-82-52-10 H-82-52-11 5.3 9.6 11.5 Above "sucker gujn" Position 220. ' 18.5 IN Bea .E. r a s i wor de, k i n s t taht^i o n, BZ - 18.5 . Beam work station, west side, in the BZ. Above "sucker gun" Position 211. I-Beam work station, N.E. side of machine #34, in the BZ. ; Blank 17.9 18.6 86 161 182 300 302 295 290 300 11.5 185 TBA 1.0 0.7 b 7.3 b 2.8 0.7 b 0.9 i-4 I6 0.4 0.0 (pg) 1.4 Comments Person-net sample on tuber* Personnel sanplfc on SMO . Personnel sample on SMO. Personnel sample on SMO. Personnel sample on tube ; Area sample. Area sample. Area sample* Area sample. Area sample. Blank samples were submitted blindly as samples* Personnel sample on SMO. Compare Sanitized. Does not contain TSCA, CBS ! TABLE I (CONT.) FORflHHHBIHHvJ RESULTS OF AIR SAMPLING AROUND BCF SPINNING i MACHINE 35 ON SEPTEMBER 20, 1982 Sample # H-82-52-13 Location H-82-52-14 H-82-52-15 Blank H-82-52-16 H-82-52-17 Blank H-82-52-18 Air Vol (L) 6.0 10.5 5.4 5.9 Time (MJTU 101 167 85 96 TBA (mg/m'3) _Coninients 1.0 Personnel sample on SMO. 0.0 (pg) 1.6 Personnel sample on tuber. 0.8 (^g) 1.1 Personnel sample on tuber. 1.1 Personnel sample on SMO. a" SMO = spinning machine operator. c These samples were analyzed B2 s breathing zone. at ; Jackson Lab., see text of report for details. HLR#704-82 5 - , ^con^SC^ CP^^-0 TABLE II T0|fi-------- EIGHT-HOUR TIKE WEIGHTED AVERAGE (TWAJ EXPOSURES OF SPINNING MACHINE OPERATORS AND TUBERS Subject Social gecurity 8-Hour TWA , Exposure to TBA (mq/rn ) 1.2 0.9 0.9 4.5 2.1 HLR#704-82 6 - QpfflP^,y.,e^d' Oc^00^5^081 APPENDIX I Lognorroal Probability Plot of the Personnel Eight-Hour TWA Exposures and the Area pamples Collected Around Spinning Machine 35 ^^t^X:X;!;:^^X)|CXXA)i!N!^}|!^ 9?<.';';.::t' 9?>g!(;-!? 99. 5.^ 99HC)i * 98^'ii! X; 95*s(; * P 90** - R- 0 SO** 5 ^ 70 B * I 60 JC '.*. ' ! K! ' if; 0 ; * * 0 * 0 0 L S0* I 40!f5f; ^ <( * T Y 30lMi 0 - O* 20*^ ^ . ^ ' ., _ <; * ^ * 10* * ^ ' - * * 0 * 5 * * ! * . AkW Of A T- . 1;{- ^ 0.5)(;$ . ,); * fc ^ 0.2l|i); O.I** 3); * i(;*iS**^^*)p^$-*)(i^^ K. * * ik it; 0.10 0.22 0.46 ; 1.00 21S 4.64 - 10.00 /H()l.EVEL5 IN JSEAFORBOCF 9/2^82 LOGNORMAL Data is log normal. 3 Probability of;exceeding 5 mg/m is less than 5%. HLK.704-82 ^con^^06' . , -^p^S;0?8'-00" ^ APPENDIX ZI :ocretBeotaJ exposure time. T- Ttee, Ti. Ti, Ti... T, are the incremental exposure times t average cancenuitfon &,&,+ C Kight houn is used as the denominator sine* OSHA {tandai^s aad TLVs are based on an eight-hour wori: day. On 2ril m) (o TuMi work time - TWA SA) 25) :fl Tun>wightd avrag* xpowjr* (TWA) To determine the timo-weighted aveng* exposure of an individual to airborne COflCiUlu^ Euts, a detailed description of " tfcVVh"ere he is iiea~ must be obtained, a* describiead earlier. la iddition a sufficient number of lir sunplinz aeasurementt at the breathing :OonM>level at positions occupied by employees, i oder various phot operating conditions are nee essary. In a typical work .environment, tbe employee say be exposed to several different inon-tenn ivengc concentrations during t r workshift ie te changes is job assieasaei t, workload, Bttflatton conditions, processes. ) od the like). " tiroe-weightBd average (TWA) xpofun "oived as a method of calculating daily or fall' "ir; average exposure by weigbUnj the different hott-tecm average concantntions by ezposuie "ax. It is the equivtient of in tgrating the 'roctairarton values over th totaj tiae base of ^TW/L ItinaybedetenniriBoi'ByJfcf-'lbwiag amiula: nvA 0 T. < C. T. 4 C, T. 8hr | tee TWA - ttae weighted iverajgc ceneensa- ^ USUtHyppo) or g/B*. , '' concentration of contamJnarit during the ilme-weighted average concentration (TWA) for this particular material. Whenes T| -- Duration of incremental exposure. C, Concentration of 2 specificair cootuam. nant during the incremental time period T, T^g, Total worfc time per shift eight-hour workday Seviral samples (eoual or unequal tine duration) are obtained during the entire period appropriate to the standard. The total time covered by the samplesmust be a minimum of sevan hours for the needed eight-hour TWA. Exuina Penonal samples for partlculates are collected on a foundry worker as follows: Safflpto No. Tlm 7:00 ajn. (ftart o( shirt) to &00 p.m. tOO t-m. to 9:30 a.m. 9:30 jn. to Tl:00 s-cn. T1:QO a.m. u 140 p.m. (turned off and eoyend tor 30 minutn during luneft l:00.p.;n. to 3.30 p.m. Tlie aeaxurefflent obtained u a ruil period consecutive sample measurement because it covers the entire time period aopropriate to the TLV and the OSHA sandajd ieight boun) and the samplesare taken consecutively(or serially). CjtC HLR#704-82 Compa"^ Sanded. Doe. not contain TSCACB| APPENDIX I; (continued) 17--Methods of Evaluation EJUMK& A personal fampling pump with respirable dmt famp'ing head if anaehed to an employee at the slut of his shift it 9sQQua,, tuned oft fsw U: iO UB. to 12:09 awn (lunch) and ticud on again from 12:00 noon to 4:30 p.m. The sample coTlecxd constitutes a nill period sample for the deumination of respirabledust exposure because it! coven the entire time period appropriate to the TLVor OSHA standard {eight bburu. ; In some cases (t is Impossible, because of limitations in measurement methods as with direct-reading meters or charcoal tubes, to collect a series oil consecutive famoles whose totat-duraflon apprbxtoates-the period for which thestandajd if defined. In this case, grabsamples are taken over some number of short periods of dae arranged to ba representative of the entire work shift. In general, in using tImfBr-nula. tnctinc,_ by a worker at various JOBSjhouid bedrtcflaaZ to the neafot thirty-Biicute interval, if ' ..^ considerable variation in the ievei of air ..',-' w^ti^ natten, shorter time Intervals will have ExAMfL&For example. au<n dui eaployee spendsthe fiat four houaafuaBx hour shift in the vicinity of a hcu^res-- operation where the measured carbon aoaa* coaeeatntian ia ir at hMffareataalK xone fairiy constant at 50 pam per nuilion. Ifte, For the remainder of the shift {four botti assume that the operator worked in a dMvsvc part of th plant-where htSOtpMure lo cA monoxide was essentially tcro. What if his time-weighted average exooAUtte carbon monoxide? Solution: EmMrLZi It if necessary to obtain an exposure measureaient for penzene using eh oal tubes. Each charceai fubfe saapie tate 30 minutes to collect. It is intended to collect .10 saaples out of the pooible sixieea 30-minutc periods ia the eight-hour pehod. Tnese ten 30-oinute duration samples constitute 10 grab faaeles of the worker's exposure in the given day. the tstimate of tha eight-hour tWA exposure obtained Jroin analyzing the readingsof the 10 tubes would be a grab sample measiucmenL For example, supposea worker is exposed as follows: TInwof : xpour(T,) Ang xpour canentMUon (ppm) (C,) (* hrX50 ppm) r (4 hryo ppm) 8 tu. 200 ---Z5ppm(TWA) - for carbon monoxide. ^ EXAMPLE; In another case assume list > machine operator (workingthe 7:00 a.a. to .W p.m. shift) tending aa automatic ferew sacssM was exposed to average levels of oil nuts indicated below: hours : ISO Total 7 a noun Tune i Away Lcvfl iff Oil .Vitti [msfitt) ; Then the TWA for the eight-hour workday wifl be TWA: (1 hrX350 ?nre * (3 ! (;00 ppra) +-(4 hrX HO eon) 8hr 7:00. 8:00 &00- 9:00 9:00.10^10 10:00-11:00 11:00- 12.00 12.-00- 1^)0 1:00- 3:00 J:00-. 4:00 0 LO j IJ 10 / 0.0 4.0 1.0 i1t5t5n0 Jripm --^---194 ppm lunch period, no exposure 546 HLR#704-82 ^^d.Doesnolcon^TSCACBJ Company 9 -