Document 3Q5RZwbO2D3GqvLZY7wd1E7ey

HONS 0 1 8 3 0 3 *i-m Mi/m mn prtM: *c mm/m aoi TM Spm M MM MrlfMHNtol Lvnlt OF Kmmi ar MMUI ItaM MM--m IN tta UM CtapIllN DritMfi Lada CMaplatn ImIa StiMy, Purl ln|tn, VT.*Nm fork sm Oapt. M liaifamaital CanaarvaKan. aiNany. MlMI: Popdan, KaiaatN a. Final rapt. nwn Fia: in, aao auiTta Oat ? ittp apt Ma: ICIMI anltar: IN Franrai In eaaparalia vita Nov (Hviraaantal CaaifaallaN, OlOany. tack (Uta Oapt. a* Oaaertptara: Induatrtal aaataa. Taalclty. *aiar pailutlan. taka Chaaplatn. Mila Malt*. Naroary(Natal). Vraco aiaaaanta . Ffahaa. Faattoiaaa. CNIaMHypaairaana, eipnanyl. nw van, Varaanl, Taplaa(Oata). CancantratMCaapaamawl Ipntifiara: Paiycniarinotad oipnanyla. ipnanyi/cniara. Trace aalala. MTISNtOOC M-m 411/m ntis Praaa: pc mm/m mt >--ry CMraatarlatlana af SalaaM Chaalaala af Naor-ter tnvlramantal Protection Apaney. Veehinpten. Toatc Vdmtaneaa. Final raptFIM4M4 FIN: OT, W, M. IN. 077. ITU. ft Sap 70 Sip Oapt Na: taA/*0/4-70/000 Nanltor: 10 _See alaa rapart data* tap 70. a0-340 >M._ DC. OFF tea OUIT7I3 aF Oaaeriptara: *Ctwiranoantal aurvoya, chlarina arpantr ceopounda. Olehler*dlf luereaathane. vinyl oNlarida. Fhthalfd oalpa. Chlorefam. Lao#(Natal), teed inarpanic cenpaunda, Load ar panic adapdunda. Catera. Kaalapy, Mt l haalth. laoNt. taaowalapy. Vatar pal Hit Ian. air pollution. Taviaplapy, fapoauro. Induatrial Nypiana. Cancantrat ien(Coapo- aitionl. Caonapiaa. Solid uoaio diapoaol IdantIF tars: 0nar/OiB<chloronanyi>. Ovtediene/heaeehlere. alyonldr inatad PipMnyia. *0 ipneny /paran 1ara. Nathane/f iuara-trichlere. Fraan If. frmm If. NtlMaapVf FO-SOO 711/ 1ST Mis Prtcaa: K A03/NF AO I IM M NlyailaPlialM HpNayl r~T~ < m FQ'MImmmI /rMuela an Iiaryv-Urval llaan ## OapNitiana Kentucky Malar latawrcaa Naaarch Inet.. le*lngton .Off lev af Vaiar laiarch ana Tecftnolopy. Veaftlnpton. OC. AUTMM: Olrpe- Malay J ; Black. Jeffrey A.; Mesternan. Albert aeoercti rapt. Foooott fio ar. f. t*. mo in 44p apt Na: M-11N <uui7ii Centred: 01 - 14*94*0001 -1077. 01-14-34-0001*7030 reject: OvaT-a-Od-KV Nani tar: omot-a-oot-kvIt) OaacrIptera: Tevlcelopy. *Fl*hea. Mpfitaia. Oaypan organic caapownaa. Biaaaaay, Chlorine organic coepounda. Cancantratlenlcoapea11ton). lethal deaagv. Toateiiy. CMryoa. Larvaa. Orevth. I*perlaantal data. SanaMIvlty. Slllconaa. Fropc. Toada INantlftera: Oatar pollution of fecta<*niMie). Foiycnlorinatad otpnanyla. Pipfionyl/perch loro, Tarataponaata. Tonic Matancoa. Oaifttev traut. So loo pirpvrl, Chatvwl catfish. Foalara taao. BuFo fovlerl, Anar lean toad. OuFo aaarlcamia. Fnthalle aeld/dioetyl. antnai ic acid/diiaenwtyi. ictaiurua punctatva. OoldFian. Caraaaiua auratus. Oadaar aunftah. Lapa*ta alcralopFiua. leopard frog. Nana piplana. MVISOIOMF P0*39f tSt/OST Mil PTMM: PC POa/m OI (MlfMHMal lclM mi InflHMrlni, H.*(iwiraanui Pr(ttw Mmey, Tests WkttaMM. Ins.. SalnMvIll*. DC. Office af MfTtM: Stratton. Charles t.; Tuttle. Mrtn t.i 4Hw. *1. hark mrnumrm rapt. ns. 4 (UmI) P0909l tl* ta. u. MO, 914 99417909 39 May 79 4pp Centrist: fN'M-OI-SMt awl ter: CP4/990/9-79/009 Otter liters: *Moter pel letten. Sell* state disposal. Harth ftlte. 4lr ps I let ten. MrSan erees. Surveys. Atsmiic hiruartiM, drswd ester. Ssrfees esters. Caneentrsttenfcaapeeittsnl. Sell enslysts. Seetnente. Strews, sessile situls, Petaftle setsr. Bteeeesusetts. Chiertns trtsttie lesnMMera: tpnanyl/perchlere. *Pstycftlarinatcd Siphenyls. tSTsrslfssBtustttsI, *Path ef pel Mant*. srecier itia, srester loti, sreeler 1394. NTfSCSSOTS 90*109 994/SST OTIS Trices: PC Ml/a 401 ierttttsntno 9 teleeted Petyehlertneted ttphanyta ts NsU Cnvlr ntsl Pssssrch U*.. 4ttens. 44ITMD9: Stesn. V. C.j 9srls. 0. . On 01 in. 9. L. Jeurnsl srtlele F09TM4 MS: TO. 9H. Ml. 990. 999 . 490 994IT909 1979 Si set Ms: (PA/900//-79/094 ttsnlter: 19 ,,M. In Meter Oeeesrcti. visit). p999*497 1979 Oescrtiters: *940101019, *Mtt#r pollut l*n. *NslIclSss. velar sheeistry. Chlsrtns arpantc ewpewds. ASterption. rsrtwn. Psrttel* site eistrteetisn. frsnspsrt prspsrttss lesnt 19 isrs: PeiyeMsrinatse aiphenyia. etphenyi/perchiore. sreslsr tots, tsprlnts. Sreslpr *343. tipnsnyi/tstrsstilsre. Mtts et pel lutsnts. NTIMPS990 rsiieHO IMP if vs oistrieetten m PelyWlertnata* etthsnyla ena Oanesnss In Set* aster Saal After m Aoetemtsl Spin e# Trws< 9ste ef r Mels (iwIrtHHHMI frttKlIon tpsncy. tllanli. GA SeeI on IV. MfTMi: Moeln. Seorps 4.; Seltti. 41 J.i t-iy. Silt; teteu. ten 9044141 FIS: 139. 99 ton 79 !4Se 69417909 9spt MS; (44/904/9*74/014 nle IS lltlan*. Kervnth I.; Osecripters: Ineutactnp ell. Chlorine orpanic Cenosntrst lanCCeapsstt ton*, Ciwd ties. 9 isle tests. >tst smyt. inching, Orswe vster. Sell snslysto. S<eli<9. Meter analysts.' Seetesnts. Oss chr--tepraphy. Msss apectrecccpy. snelyala Cheetcsl ISantlftera: Pelychlorlnai*4 Mlpnsnyls. *Htaresua estertsla apttla, Oipftanyt/perchiore, tans pellutIan. troclor 1394 Path ef pellutanta. NTlsctai, mtis(P40m9 99-aaa 4tO/4ST MIIS Prices: PC 407/N9 401 4 Mathod for the Saspllne and 4nalyala ef Polychlorinated diphenyls fPCPe) in Mieit Air (nvlroneentsl Science and fnglneerlnp. Inc.. Gainesville. fi.*(nvlranesntal Protect Ion tpsncy. Msshlnpton. DC. Office ef TomIc SeOetsncos. MIMM: Stretten. Chariest.; Mark final rapt. 4up 79-Dec 77 IOMMI 914 : 70. 994 . 994 Aus 79 tSO Contract: tPA-SS-Ot-3979 Monitor: CP4/900/4-79/049 mtt lock. 69417909 Stuart A.: Allan * J Doscriptort. *Gas analysts. Chlorine orpanlc cescunli Chselcal snelyala. SeepI log. Air pollution. Concentre' lontccepot It lan), (tele testa. Gat cirowteptgiiy ntlflera: Polycniortnatee gipNnyla, >4lr pollutlan set ten. ttphenyl/perchlere, Arecler lOIS. Srocter *343. res. NflSiPSOSO HOMS 0 1 8 3 0 4 P0*9M 494/997 MT1S Prle PC 407/or 401 PI-IN M/HT MVIS PMm: K MM/V Ml NtMUMM Omn ItinpiP IN., Annapafla. N.*|mtrnnMal PnUcttw Money, PMlaOilpMa. P. nwapooko toy Prayon. AVTKM: Pom*. Joa^n P. PIMl Mt. <1 IfP-tS Ml N PWMI PM: OP. MV. MO Ml TO 13p Monitor; IPA/OOB/O-TB/OIO MAI TOOT OeeCMptero: Mn-blClMo. MWIIcMn, *PIMa. MIotipHln My* IMIMNUI, ClMIMmuMClMlUlNl, PlMlM, IfMChlorine orponlo ooepeunM. ChanIcol anoiyoie. voter pollution , Mm elver. SeepI In#. Preparation. Mont look* Oivor. Chopin** Olver. Ilk Bluer. Tetenee aiver. "appifianmuTi Oiwor inontlMero: Oteeeeuculot ten. StrlpeO Mooe. IfllSCPM. Pelychiarirwtod btpnanyle. PI-IN 00P/4ST MVIS Price*. PC AOO/NP Ml Molyelo for Polyohlor Ineteo Biphenyla in Uho Mnitoie lattea State Univ.. feet l metnp. Inot. of eater i Cell.. Mol lane. |. Oopt. of Chonlatry.Office AUTNH: Brli*. Irvin J. Copylet Ian rapt. POIfNI PI#: 10, MO. 0M 00AIT0M *e TO lOp Cantroot: 01-14-S1-O00I-4O3S Pre|ect> OOTT-A-OTT-MICM anter: OMBV-A-eo'-eiCM<t) PraparoO by Mope Cell., Mol lane. Ml. Oept. ef Choniatry. Ooeertptere: Oieelcal anelyaie, HPe Moceteea, -lilinnu. Peetleieoe. Chlorine aroonie eeapeieieo, CenoentrotienICenpee* ttlenl. Sanplee. forth fine. Meter pellet Ion. Meter anoiyoie. Si tee leant I flora: Polychlorinated blManyia. Motor pollution ceteetten, Point eeureee. Mtphanpi/pereMere, nilSblOMPT Oe Paul Untv.. Chtcape. ll.<fiwlrMnt8l Lab. -Duluth. Broeae lie. Ml. terpa l*M Pwwrch Station. AIPTMM: Mrphy. Theeaa J.: Imrutfeo. Chariot r. final rapt. fOI4MI f 10: ISO. 4M. 114 01*17003 Jul TO asp Orant: (04-0030IS Monitor: (PA/0O0/3-T0/O7I Oeacriptera; *tr pel tut tan. Meter pal lut Ian. La*e Michlpan, Chlarlna arpanic coepaunea, MyOralaoy. Cancantratlan(C*apoeltlan). farth filla. Paatlcteaa. lanplInp. Chanlcal waiuali. Part idea, Oatn leanttf lara: PelyehlerInatad blphenyta. *ir water mtariacaa. 0 iphany l/parchlara. NriSfPAOPD P0-300 040/4ST MIIS Prion: PC *03/NF *4t Polyohlor InatoO Olphanyla. Chlorii*oO Peotleli Natalo in toll* of the IvorflaMaa NoHomI Pom < Aprloulturai Ami an* Trace Adjacent Mattenal Oceanic one Alnaophorlc AMtnlatretton. Mtaal. fta. At tent le Ocaanapraphie one Mateareleptcel Lana. (400 300) AUTMOB: Be**Jo. AOolfaO.: Meat. Ilclarf N.; Harvey. B.; Matcher. Patrick McOnitvary. Philip *. Teekniea* awao. 1301*3 f 10: ISO. Of. OM. S7P. 040 00*17034 Oct TT 40p Oept Mo/ MOAA-TP-COL -A0ML-3S Manlter: to**-7000070* Oaorea Oeacriptera: Biphenyl. Matela. `Voter pollution. Poottcteea . Seepllno. Sella, feraa. ChiarahyOracarbona, Source*, frepor. Canaan! rat lan(Caepaa It ion). CMoroOen. OOT. Chlortno arpanlc raapiwmoa. MalahyMacareowa. National parka. Aprlcultura. Pleatlc*. Maichao. rioriea leant If lara: (verplaOea Mattenal Park. PelychlorlnateO Olphanyla. 0(phonyl/cnlra. Path at poitutenle. NfISCOMNO* HONS 0 1 8 3 0 5 PB*fOT OTS/Ttr MVIS pneee: PC AM/Mf Ml PelyeblorlnoteM llphpnyla In Preelpltatlen ip the loop n-M4 n/nr writ W'lU OOO/OSt Milt PC A02/df AOI twllwlm Nr NlyWIirlNlW UrNwyl MmIm fn* m INWrtlytN C^nHr MMl Ntjwt Polyoftlortmtoo OlpAnyla la tfa MaarAtra Marla Iwaytta off San Plage. Callfarala (iwIrmMiMI HMitrlni aM Iwiart Lap.. Aaaarcn Irlwgla NN. M.C. IwlranMNal Nnltarlni IrancA. WDCi: Imn. OarlM MMan. Nrrlll 0.; Imu. Mart 0. flaN prajaai rapt. IIMM PIP: 70. OOC. 00A. 00* ORAI7034 *y to tap apt Na: CPA/OOO/4-TO-OtS Man!tars 0 Praaarap fa aaaparaaIan aim AoltH (ffwta OaaaarcH la.. atareh Trlaaipla Parti. N.C. (notraiaantat laalcalafy piv. Oaaartptara: *1*110 aaata llpaaal, Nat AAlyels. Induotriel waataa. OitortA arpanic eapaiAi, air pal tut lan. CoPuaiien praducte. Capaettara. Owatcal anatyala. twaintratlawlCapoaft lanl, Pant tar lap Nanttffarai >Ip pollution Ptwtlan. traeiar lit). lipaayl/eMara, Polychlorinated otpAnyia. NTitfPAOeo Sautiarn Cal ifomia coastal Malar Manrcn frafact, Segunde. *Cal Ifarnla OagtoAl Malar Dual I ty Control Ooart, Diego. tan Otapa aopion. ci tan MirMOO: Tounp. Oavta a.: mmmh. rmifin c. f Inal Apt- Oac 7S-4ul 77 (33*303 f 10: 130. OOO OOAI7022 t sa 7.r stp lai Ma: tccvap- too Monitor: to oeecriptoro! OipAnyla, <Mata voter. *Ater dilution. CHIortna orpanic coapeunda. Arpora. Outfall aavaro. CraPa. Viasuee(Otaldgy). Contaainat ion. ConcontretlonlCeopoattton). taaioonta. Assets. fiaAa, OOT, California I Pant I flora: MfIttOLO Polycblor Inaia PIpAnyla. San Ologo Harbor. PO-303 I70/3ST MTIS Prices: PC Mt/W AOI in P0-303 att/4tT writ Prtcda: Mat aval IAla writ (valuation af tfa PreOlA PaaaO Py In-Pteoe NMwtMtt In Oaltlaara Nftar an* Oaoaanonaattan af Cartatla Action Iffaats a# Nlywlariaatal Otpnanyla. NlyahlPlnalad NspMHelenA. aM PHtAlat# letara a larval BavaiapaAit a# Indent Inglaarlip Iwoclalti. Inc., Annapolis. Hd. Nary tend tup M CraP *IPMtPra>awip aat Merrlali' Untv.. Caaprldpa. Marn Point CnvIroAentet LAS. (nvlrenaental froioclIan Iponcy. MMlngiM. O.C. Office of Valor flaming Teaae 1 and W Unlv.. Callapa ttatlon.*Aitonal Science nd ttandarA. (404 033) fwnatlan. MtMipitn. O.C. Office far tfa Internet lantl f Ina I rpt. Osnsda af Oeaan (A'orotten. (tar tool 1211343 fid: 04. OOO. 47C 60AI7020 top 77 07p aVTNOO: Laughl la. 0. 0. P; IPff, 4. M.; OtA. C. S. Contract: CPA-OO-OI* 1000 laniit pto; p, tao. or. oa. ooo. ith. ttv. 4to ooaitoss Monitor: CPA/44O/0-T7/O!M I0TT ftp ProparM In cooperoI Ion vitn MarylaA Unlv.. CAPrtdgo. Marn Pant: Sf*10070-04000. PSPOCf73 00747 *04 Mint (air Aiwtal Latoa. Anftar: MOP/IOOC-TO/TO tup. fa Pal lutant tffacta an Marla OrpaniaA. pOO-ttO 1077. Pager Ipfora: Ala pollution control. OaltlAra Arbor. tadiaonta. MarylaA. Oioeasayo, Twicily. feasibility. fiaAs Oaoarlptoro: *CraPa. M<P pollution. 'TMicity. CklalM . Pontboa. Coat analysis. Concentretlen(Caaaaaltlon). Plankton organic caaowA. OipMany la. Larvaa. cniorla, . Sites, Atala. Aaana, CHlorlA organic compound*. Ary land PapAduettan<Otdtogv>. tapoaura. CcAentretionfceapaemen). MapntMolaaao. PHtAietA. (Hat, azotic aiAia lOanllflora: Veter psllutlon lupl la. Vat#r paallty PelycniarinatA pipAnyia. MVitiPAOVt laaattf lara: lataraattanal Oacnde af Oeaan lapleretian. AlyeHtariAtdd Plpanyli. ipAsty/eHlora. *OHitHrapeenapeue Harriott. Wta pallvitta affAtataniwlal. Areolar toto. *Nlytaialiaii aapHtHaitnm. ialma *000. Hatouas toto. NVItlOOC HONS 0 1 8 3 0 6 D T(/>. > u> o io-jii ooa/itT writ meat: pc toi/ia *o Slas MhiIpiI Renal Maaamaua Mtlawii In Asiatic faad Trident (nilnaarlng Inhimm, Ins.. Annapette. N Ikilv., (!. Cww Nr liwlPMwUl and estuarine Shfdtee.twrlrswnm IismIMm ln"|. NMtiln|tOT, O.C. fflde af Mtr IImnImi am Itwsirn (M on) MS: l. W. PA. MO. 470. 47C t|TIW in ti tno CsrtPMti CM-n-OMNO anltv: IM/440/I-T1/0IM Priparap M Cooperation with MrylM Ihlv., f~`--------t Center )w Iwlrwmt| nS lituarlM ttwSlss. lltCPlIHHi Mtasitl. Water pellutlwi, *enltaring. Streea flaw, hntlf. Ctrewlatlan, Praia aurrente. Oethyaetry. leSlwante. Cares. teaming. Particle Hia. Arsenic. OweryliHil). CaSalun. Chraaiww, Caspar, nangeneaa. Nicfcel. laeOdhtal), line. PwetieiSee. Cancentrat len(Caapeo 11 tan). Invertehratsa. flahaa. Oteeesey Identif lere: Seltiaere Marbar. Polychlorinated biphenyls. Piphanri/ehiare. Maciaa diversity. MrtUPAOvs n-t ttT/SST writ Prlasa: PC AOO/Pf 401 sis of Physics Otanlaal Prepartlwa #f Araalara MIS ns last In ^Petamlolng Tlalr fata anS Tranegart (it Matn AUTHOR: Paris. Darla f.j Staan. vtllisn C.j L. daunts I art tala iiaaoio fis: m, to. aac. sao. dm. dtp eseiraia 1070 Dag Na: CPA/4O0/d*7f-014 Manitar: M .pwd. in nw--pun v7 m, p)H*l, Wl.. atlaisaa. *Watar analysts. Chlarlna r~panin tael analysis. Sae enreaefgrapi. Sarptian. wepirittnp. toHOillty, CencentrstfiilCaneeilnen). peaciian hiiai laa ISestlfiara: Areater MIS. Araelar 1343, Path af peiimaiii . Water pettwtien Sataatlan. eaprtnta, Poiychierifwted Wlpaanyla. MTIUPAORO MarWwttan Call.. lah.. -Ouluth, Minn. Irom Minna: Tnneim, Aahart v. 1174914 FIS: 190. Of. MO. S7M Apr TP ttp Cantraat: KM-I-IOMIO nontier: tP4/00/9-7e/09a CRAI7SI7 I Aaeaarcn Oascrlptara: Meiarnaue aatarlala. water eoltutlan. -laeae. Sathaaatlaal aaaals. faaS chains. Marina alcroorpenlsae! rW4i. Satarainattan. Bloeesey. Absorption. atoaess (acritlw, ttphenyl. Hydrocarbons, Cancentrat on AcounulatIon. Lake Ontario I1 Ion)' ISontlflare: Iphenyl/chloro, Polychlorinated biphenyls. PS-1P0 M9/DST MTU Prices (Order a PI-300 Ml, HP AOI) * CMirrtlte Study al Tww Pwlyahlarlnataa Blphpnyl Riatiree (Atm I are 1943 and tatO) Cantalnlng m Oilarlna an Inductlen al Mepatle Porphyria end Drug MatMellstf* (wym Mettanel fnwlronaentel eesearen Center. Perfc, M.C. eeaerch Triangle MfMOP^SalSstetn. doyceA.; Hlctraan. Patricia; Ouraa. Vlrlyn 174111 IIS: ST. T. SSO. SPC 31 Mwv 14 tp Manitar: is MAtTCIT In Tealcetogy and Applied Phamscolspy 93. p4SI-479 t7._ Included in the report, dournel Articles on Voslcolooy. (roue te. as-aao aaa. Oeeertptors: Pesticides. Tostcolagy. Olaaesay. laboratory anMaia. Chlorine organic caopaunde. Sate. Ingestlon(aiaiapy). Matahaiiea. liver. Porahyrta. Matanaitc aieaaeae. Cntyaae rug. Phyetaiagical effect*, fspertaaniAl data. Co^er leon. Cancentratiaw(Caatnt lan). laelestOata) IdentIMara: Palychiarinotad Wlphanyia. aaprinta. Araelar Oig. *faeic aubalancai. Araelar 1343. giaiagiC4l affacte, staaaciamtottoo. Paettctda reiiaat, Stpheny 1/cMare. MtlWPAt IN/m nil PrtaN: N IN/ Ml Mwm VMM qHTlWrt-- NliMMMlM M CMMl HI* CfwtrwwnUI rotCfl8W tarvlM. MwlrNl (QwXc ). *ln Ir-- mMI *raitpn IfilKy. Milifnftwi, D.C. WMm of SIW M/INM: MmM, &.. O.s thMnor. D. *l.i l^ton. 1. J.; IhMM, . N. fInal r^t. (MM) Mi: I3D. U, CM. CPC flMITIII Mi n tap Contract: Monitor: (M/M/-HTC Oeoortptars: *ir pollution. KMlorina orponie oomounoa. Inetmrotprs, Peotlciooo. Portlcloo. Chloroforo. Caroon totroonicriMo. CanoontrotlanCcaopMltlon). Kllno. Porftrooweo valuation Idantlftoro: oooto disposal. Toluono/chloro. MlootooouppfOntorlp). PotycniorlnotoO otpnanyto. Ithy tono/dlc- More. WTI9CPASO PP-2TP TV0/4ST MI It Prlcoo: (Order oo M-Jtl T2P. OP IOI) PelywMIorfMitoM Olphonyta (MNlor IHI): Ifftrti M t. Poll Prwth M ModCOI Unlv. of South Carolina. Cnorlooton. (OOP MO) Atmow: Kell. Julian (.; traeor. Cnorloo 0.; Prlootor. Laaar .; tenet tor, taouol H. (miiu Plot or. m. 919. iw. too. tot omiths tort to Monitor: It Pub. in tnrfromante l Malth Perspectives. nl pITt* ITT. Apr H. IneluOoO Mi two rapart. Journal Article* on Toaieolopy. 6rp I. P|*|lt T. Ooocriptoro: PooticlOoo. *Toaiooloop. Motabollan. Mclorto. tooHarionia coil. CMIortno orpanic eoopotnoo. troutn. In vitro analyolo, Tabloo(Oota). (hootloontoI cot*. Wicroarponiaoo. ConoontrotlanlCtoQ tall Ion), DOT leant IP loro: Poprlnto. PolponicrinotoO tiphonyia, Aroclor tsoa. *70*10 awMotcnooo. niisipal MV one PolpaHorlnatoO tlphony I (Areolar 1742(Trada itaol) Cffootc of ipieo on C. Coll Proutn Maoical Unlv. of tooth Carol tna. Charloaton. (Ml 447) MTMM: ooil. J. landI far. S. H. t M7M| PIC; OP. *. CM. S7M. S7T. CPC. STM M4I7II9 I Pao 72 7p ManllPr: IP _PuP. in Qatar Paccareh. vC pp27-P4l l72._ IneluMaO In tho ropprt. Journal Artlclos on Tostcolopy Croto T. PP-27P 70#. Poser Iptoro: OOT, *Pootlcieao, Piodotorlorat tan. Growth. Metaria. Cacnortenio coll. In vitro analysts. lat>ta(Oata). Inooct teteea. Poaieuoa. Nucioic ociea. uneino. Concontrat lanlCaopaalI Ion). fsporloental Cota. Metabolic*. Cniorlno orpanic caopcunea IConilMorc: Poprtnta. *Pol ychlor Inatod blpftsnyls. DOV inoocttetCo. DOC inaocticico. Pocticiea rosicuoa. Arocnior 1249. Arcehlora. MTISIPU Pt'27 C10/OST NT It Prlcoa: PC A02/MP AOI A MaeiPloe Porchlorlnotlon PraooMro for the Dotorntnation of Polychlorinated atphonpla Viceana In Unlv.. Madison. Wator RnourcM Cantor.OPflco of tfator Poaooren and Tochnolopy. Moaninpton. D.C. MJ7M0P: |ur*hard. l. P..- Amstranp. 0. f. technical coop lot Ion rapt. II4MC4 fid: 70. PCC. 440. OCA GAAI7StS ter# it opt No: Ptt-POC-Tt-OI Contract: 0114-74-0001-SOS2. 01 14-34-0001-7I0A Project: OMPI-A-OC7-Pit Monitor: OUMTA-OP7-OI$(I) OoacrIptera: Uator analysis. Psttlcldo*. Chlertn* orpanic ceopsunos. Cnaolcal analyais. Concontrat lsn(Coaposlt len). Pater pollution, Chlorimtlon leant ITlars; Polychlorinated biphenyls. Craclor*. water pollution detection, erector 1271. Aroctor 1204. MVIsolObOV HONS 018308 PP-2TP 7ia/2tT writ Prli OO Pl-270 TOP. P AOI) M-m M?/? MTIS PrlCM: PC IM/W Ml rpnM IMIym tn Mr Crlltr OHral Pragraad. Tr*Mi NMMMl frilnini pi fltfrattaral CMKlntl, MM. IMMfl Mtf: VO. MO*. M*. CM tfUITIIf DM TV *>p* MM Ml (PA/AM/l-TT/OtA aritn 10 htfVNM M'MI m. M-MI 3M. M-a4 SIS rtf PO-tM M3. orrOMPai oitar ralyai*. MmIi, *Ot|mIc oarawMi, CMII Mlytll, IlNtlMtf |NN, Osypn. IIMNalwl Mygan Mtf. Mmli. (rpnla MMtN. CrMn. SirfMtrM, Nwcli. til*. Or--Mtf. m BhraaaiaQTtfpni. CMMm rpnic " ntpaiMHCMMittan). Nltni _ tf, NIIMttftf. Mlrttry. NltlBltfN, Quality litfi rslytitf ItfrtlfMrt: Ctfrlcal aaypa" tfHMtf, NlyCiIrtMiatf piphonyis , atr piiuttr aitrtir, Mir wat, ajaiari miim. Matr parny. ntiscpmss PI-STI 19S/OST MTIS Prlaw: PC M/W Ml UOaPtfMry fvalMStlss f NI#*TMVOr* Dmtrust ln # NlyaMMortatf Ofphonyla rtf MlatM OmM toytr n. OKI*. Saoaarch Imi.Miniclpal Inviranunul Clnatmatl, Ml*. MITMM: Bwvoll. S. S.{ Ml>. II3M00 Pld: IAS. OP. SVP. DM TV T4p Srant: (PA--ao>04O Manltar: IPA/SOO/S-TT/MS . A. MA . SBAITSIA Oaaertptars: Pesticides. Chlorine arpanic eoMaunda. Ladaratary aaupnat. faperlacnt*. Oosradatian. Staaility, Pyralyaltf, Cm chreaatcpraphy. Oaaipn orltaria. Chao tea I analysis Identifiers: PalyahlarInaiad Sipnenyle. Ouarta not apparotua . Praoatfyraa, HIM taaparatura, vriSiPMOO Mittanal Imi. far Occwtlanl Ufaly antf NNlth, Clncimatl. Mis. Induatryutdo Statfiaa IrrT. MINOS: Nil 11 Ipc. lab; toltb. tarry; Jowai, (iwtai ms: sj. si. sni. stv. sao. aaa 3t NW VT 90S BMltr: 10 Bart maitsi* Ostfcr Iptaro: fiwlramal airvaya. Inaialrlal byfiam, C lactrlcal Iwtfaatry. CMarlna arpnle CMpounat. tsao palartni, Tin. Use. Air plMlan. Industrial ataoaphoraa. Tsaleslady* Cancsmrat lanlCaapoa 11 ion). Standard*. Physlologl cal effects. laeaMSattana, TaSlstf(Osta). Netfsachutfetttf Identifier*: Indoor air collation, Polychlorinated blpbanylt. Areelar 10IS. Ktltylana/trlcniara. Occupational safety and Noaltlt, Aoreves Industrie* Incorporated. Maw Sedrord<Mes*ectw- alts), Vaaic auMtanaatf. 4lr soapI tng. Saaiatr para I as lb la aipaura level, Threshold Halt aiat. mtISMCwosh M-3TB M9/3SI Nils Prices: PC A09/HP Ml InMatrlal Niflaw Survey a# Carpers!ten. Olaaalnstan. Indiana tfMtlittfwaa Claetrle National Inat. far Occtpdtlonal Safety and Haalth, Cincinnati. Mia. Olv. at SurvelIlance. Studlaa. Nasard Evaluation and Maid MTNOS: Sanaa. Mart (>914 Md: Sd. 87U. *40. IM. Ul. ME i Oaa VT >tp Monitor: It OMI7II4 Oaacrlptortf: Industrial hyplens. tnvlranaantal ourvaya. Oralcal Industry, Paatlctdatf. CMarlna arpanic coonouoai. Air pollut Ion, Industrial plant*. Cencantrat lon<Cor>Q I tlan). Industrial ataaopnora*. Hotardt. Parsonnol. Haaltn. Indiana. Solvents. Punas. Oiona. snpineertnp. Standarda Pravantiva oodicino. Safety Identifiers: 0coallonol aafaty and noaltn, irMaor air pdtlutien. Air saaplinf, (nvlranaant*I haaltn. Tecic auPtftaneao. Meatinpauit Claetrle Carparattan. Slseeinptonlin- atonal. Palycnlartnatad biphenyls. Thrasnald Halt vatuaa. Mesiaue perolsaieie espasure laval, Araclar lOitf. NlISHfaOSM HONS 0 1 8 3 0 9 PO-tTS SSS/SST MTIS Prlca*: PC AOf/HP AOt MMtMlal Npplane Sarvey a# odferd. MasssMMStts IntdtrlN, ,lno., Maw HONS 0 1 8 3 1 0 P-*TT 4T/IH NTH Price*: Nt (Mllttl* MV IS Unlv., Ihfittn. flrMMtt leita liat. a# N|f*fei)<i|lc8l al.Nlet tenet Ml* KMitai. D C. OfrtM far the InterfwttaMl i K-pteretten. (4M ONI drant: W-SI-nm. MV-OCIN*IN Nnllar; NSf/IOM-TP/S NafN In OMfarttlM with NMa iMt. Nnafih. TtnNt (NtiarlaM). Ps*. in Marina CNaliOt. f fllt-M NTY. Oaaorlptara: 0aaan awtrwaaiu. ariaary Mia productivity, Meter palhrtlan. naiMyrttafia. Oipftaeyl, CMarlfa arpanie eeapeunda, Cancantratian<c an), Surface uetara. NatacMalMl raactiana Identifiers: Ooprtnte. international Dacaaa I aploret ten, felyctiler (noted Miphanyla. WTISIOW af !! 144/IST MTIS rrtcee PC *Ot/m 101 Cnvlr i iaa. *0uluHi, Nlm. laaa. O. f.j Sira an. w. . |.{ Milliard. a. . f. a. I.; Kalaat K. 1. (. f 14: IN, MO. l aaanato 7T aop eat Mb: EN/NO/i-77/049 Monltar: to M*. in Tna Matara af taka Huron ana Lake iipar tnr. vs HI. taka Naran. Oaerptan tay. ana tna Morin Oawoi; ch. 4 oin-aao. N1*I10 lin. aiforl ta tha Intamot tonal Joint Caanleeian*Mnttad Stated ana Canada, ainaaar (Ontario) ay Upper Laaao Oafaranea Iraa ff aartiino Brava 4. Paacrtatara: `Orpanic eeapeunda. *iafca itrai, cmoraaonionoe. tracetie pelyeyatte aydraaardana. ananala. Malar pollution. Waiar analyala. Chaataal analyala. Oder*. Chlorine arpanic eapauMa, Cyanidaa, Chieraan. Oialdrm. Alar in. aaoticiaaa. 00V. Cancantratlentcaapeeiten), Sadioanta. Ltaneiepy. teurcee iWNHtM, Marparnanaa. ttphanyla. Orantna orpanic Motor pal l< falvdilarlmlMfepaaif la. aeetlelde, BOC iro;ticiaa. tan. iMptacniar onooiaa. . . acn.tara. t - Melhasychler. Styrene/ectechlora. tHtapana/MtHyl, datar pat tut ten offecttAntaale). N JM Mt/W NTIS frlcaa: PC AI1/MT AOI Crltarla far a Maaaaanr^d Sta__ ta FalyaMlaMnatad atphonyle (PCOe) Mat Ianal Inat. for Occupational Safety and Health. Clwtnnetl. onla. (no 7ca) foaou I fid: 40. tl. S7U. SIT. 440. 404 44417404 Sap ft Nf Oapt Ma: 0MfM/PUP/MI0SM'77/}94 MonI tar: ip Oaacrlptara: Industrial nyplana, air pellwtion. Industrial a.cniorine arpanic caapaunda. Crltarla, Itanrtaraa. " Cancantrat lanlCeapna man). Physiological ffacta. Preventive aadiclna. Safaty erplneertnp. nodical waatnotian. Banitora. tacarda aanapaaant. Protection, faraannal. Toxicology. tnvlronaentel aurvaya Laboratory anlaala. dioastay. laonttflora: Ocevpot tonal Safety ana Maaltn Act of 1470. Polychlorinated biphenyls. Btphonyl/chioro, fhrsstwtd Halt valuaa. Mautaua Permissible exposure level. Cerclnopetpsle. Nitapanaaia. faratopanaila. Air tatfIio. Tosic substances lalapicAi affacta. MVIShCmoSM m/nr mis mcm: !< M n-m m. v too tw Naim* MMM in Mam mpm Tit InvlroMnui ProtectMn Ifici. UNMigtan, O.C. (mo (Ml WMI: Hots. P. O.I TOM. A. t. $ Striuai, S. C. COTptdt MO: If. ST. Ml, MC. ITT 60*17600 tors M aiMri to Pop. to ttie Outlet to of Me Seotety of Phoroooaiopleel one (mifowRUt Pttit|<ttt, 4 ot piT*it, tar Tt. InetuOeO to too report. Journal Articles on PeeticlOo Content in PooO one Men, ft-lTt in. Oeeertptore: Peetictdoo. dedy fet. cnierine erpnnic MMPMt, Tieeveeitieiepy), lunar*. IneoetletOee, Saopltnp. Choetoot enelyets. Pstnelepy, Taniee(Oete), Mptecntor. Cenoentrsttan(Ceepeelt1*n). DOT, ototortn. cniorino organic Idonttf tore: Poettcldo roelouse. Ooprlnt*. Adipose t issuo. Polyeetortnotod eipeoniio. Pomeno/hosocnioro. Ovycniereene. Toole eupoieneoe. MISIPM. PO-tTO 93O/0ST writ Price*: (Order o* Pt-376 IM. OP Ml) iPdla *# Polrofilorlnotod Otphenrlo tn Mlpeeo Tloouo of the tenoral Population of tla Nation tnwlrsnoontol Protection Agency, OtoaNloo. Pa. MfiWR: rone. Amo i. IOTOI14 fid: Of. 6T, 6M. IU. 171 6PAITP06 Apr TP 3p donltor: to fuO. in Inwlronnantol Mol to Poropoct iwoo. ni R7t-ti, Apr Tt. Included in the ropart, journal Arttcloo on Peaticlde Content In food and nan. Pp-tTp pm. aaerlptoro: Mdy fat. Poottcidoo, Tioouoo(ptolopy). Ottorino organle aaopoundo. NHoano. lo>lp. Ooioct ion.- TaPtoo(Poto). Conoontrot lon(CoMOOttlon). Surveya. aanitere. Moo apoatroooapy. Potoolopy united Ststoo ldentlftore: Pesticies reeldue*. Potyenter tooted ptpdonyls. Oeprints. MTISIPAL Adipose t tsi loale sudstwv *Mla*ta of tva MJor Brslnapo bain of tta United states (wlrwMnul Protection Ifancy. taoilngion, 0 C. Office of PoeticIdo Proprsos. AtflMOP: Oannil, O. Stowe fCtOtfe Fid: OF. ISO. STM, Ml 1074 tap 60*17000 Monitor: to PwO. in unleant If led Jnl. Inctudao in the report, journal Article* on Peoticie* OoaiOuo* In the fnwlrenoont. tree t. *0-976 112. Doaeriptore: *600ideas. upwifli. Peatieiooa. cniorino orpanic coepeunee. Surfaco waters. Cencentrat lonlCeopoe 11 ten!. Maiards. Olvors, WateronoOo. united State*. Puerto dice Monitor!^), Sodioonts. Stroms. Idsntlf lor: Polycniertnoted OlpMsnyls. Peetic Ido residues, NVISCPAi 0 Ipfieny I/cMoro. po-pt* 004/aST NT IS Prices: (Order so Pf-271 pm. m *ot) orntloo Cdnoentrstiene of Polyafilorlnotod Plpnenrle end OPT In Led* dlelilpan Men, lost Nst Ions I Water Quality Lad.. Oulutn. Rim. AUfMOP: Woith, 01 loon 0. somtct fie f. oil. ooo. stz. stm ooaitoop 10TS pp donltor: IS PM. in Pesticides Nonltorlnp Jnl.. vt nl p)i-2t, m ?|. Included In the report. Journal Articles en Pesticide Oealduss in too tnwirenosnt. Croup i. pp-tTS MO. Descriptors: fiedes. Olpnenyis, OOI, La*a OicMpon. Poatlclds*. Cftlerlne orpanic cenpeunde, Arens tic eoooundt, Msssrds. donltorInp, CencsntrotlentConpos11ion). Trout. Soloon , Preen voter Mono*. ToierencesIPnysiolepy). water gusiity. Opelduos Identifiers: Oeprlnte. Polycftlor Instod ipnonyl/enters. Posticios roe loves, miSfPM. Olpftenyle. HONS 0 1 8 3 1 1 fP*tT0 *13/4*7 mis prldoo: (Order ee PO-fTO tit. Nf Ml) Potyentertnoted Oipnanyl* tn tno turfooo Uetere end totton 08I/MT MIS Prteee: K M9/W iOl (fwlrMaMal Pi muln ipMir, MHm, imirtia . MIN--: arwar, t. |||; Mill. tovM a. OmI rapt. --IS-- Ftp: or. Ml, D. STM 00AI7S07 --t 77 M ManpMt --ar:i ira/aoa/o-TT/m Oeoertptera: mom. CM--leal mmly#a. l--tic ant--le. TiMM(CMlair). CencentratiiKt--man). --tar -- iiutian. --tar anelyeta. La-- --lea. La-- Martea11, a-- t--. MImhu . la--l--. Menttartnp. --at tat--a. Mart* Cerettne. South Carat l--. Ala--Me, T--awe. Han--y, Miaalaal--i, operate, nan--. -- c--re-- --a-- I--If lore: -- lycniarinet-- atpMenyle. -- tar --Bitty. --tar --I lull-- --tact I--. 01--oc--ulat lan. Peettct-- r-- I--. Southernt r--laH--tt-- Stetee>. NTISSPAL W/tST writ rrlcw; PC W7/ AOt jjjjjjj -- Coll--lien RMIa tar IM Levels eF (irMa , Ta.>HNlih (f(cu N.C. <230 900) UFH00: OWHII, -- a. ; --eon. OonelO c t--I--t no: MO, 004. M 0**1)MM Oct 77 l4Qp CmlrMI: (n-M-01-3S IPA/4O0/1 *79/090 S-- el-- report ottM May 7*. re-3i ooa. Oe--rlptere: Peattcl--a. Gee enalyele. Gm -- lectori Ca--trat lanfCaa--a 11 ion), v--iea<0eta). --a chroaetooraphy. C--alcal anelyetf. Concentret len<Caopoa M ton). Sao^n--. Perforaence evaluation. Oeaipn criteria. Foe*. Polyurethane repine. Sara--to. 4lr pollution. Chlorine organic coopounea Orpanic p--ea--tee. Cera--etee. Sa--lers ' I--ntlftere: *Atr pal lut ion detect Ion. **r pollution ee-- lino . Pelycfitar Ineted atpnonyla. Chre--sora 102. Tenea-GC roatne. N --'>70 M4/9ST will Orta--: PC AQO/NF *0t --all--titty a-- Oaneantretl-- -- Palttrt--ta r-- --arte-- falls --oop--Ir t--la--f to Ferepe a-- --a--oaaua n-- I--ha Untv.. --ec--. --tar oourcoe aa--arch Inat. !-- State On tv.. Peeatelle.Offleo a# --tar --soar-- mm MITMOP: --Ban. PenaI a a.; Kant, --a C-; Ca-- ii. K. Technical oaapletten rapt. --I 74-Jul TO KOCOIIS FIO: I3P, OF. Ml. STM 00417007 Mar 77 tOOp Contract: Of M-94-0001-000 Fro)--t: OMT-I-OO-IM Monttor: o--T-4*--S-|p4fS) Proper-- -- iMa-- State -- tv.. Pocatello. Oenaia --tar --tlutt--. -tart-- erpanic < ana. 0--1--. Otolartn. --T. Plphsnyl, Mercury!--tal). Ca--um. Trout. Fra-- --tar f tehee, Marina elcreorpani--a. ntratt--CCteputtien), lieir--Mil tepeete. are--te. too--tner*-. --aria-- latte --ear--tr. rei yentort--t-- aipnany le. MIIS0I0--T lahenyl/-- lore. HONS 0 1 8 3 1 * Pl*m 4IS/JST OTIS Pr1M; PC W/ Ml nl MftHkHth CiHHmU a# ChtarimM Nfi IwrtNrn Cal Ifornla CmsUI tl iMhnlwl rat. ltrt-74 I0MM1 dm: in. u. or. oos*. ot, sot. mo Mr M lip* OT Hv: |CCMPIMI4-T4 omaitooo BucrlpUri: KHIimH)OhoIbb. M1. *Mtr glluiin. HOTf. MOT Wlr, IlMMlrlM, NnKIpRlItlaa, Mtlfwllng Mllngi. OlpDtOTg U. Dumlf. MrcMnl Mlga. DmMm. ChUrint irgwK ootmrM. NbIM)Otbctobim. {whmImhoMC- OTMIIIdrI. MMla, Mll otIot> QtatrlOatlanlPropOTty). Mlirarnli IMRlIflari: lot OTgolM Harear, long Mm* llartoor. Mipiri HarOar. Sot Dlag Martoar, Palychlorlnatad tolptoanyls. HOTMl/MlOT. NfttSOLO P0-3TS 413/SST OTIS Prim: PC *03/1* *0 OTrlna lnpOTi of MlyMIOTwtM Olphanyla an* CMppar fran Vaml MtlfMltng talnta Saillwii California Caaatal Mir Oaaaarcn Prajoct. ligmiB. Cl AUTHOO: Mung. Otvltf R.{ Maaaan. VhaaPara c.: Oatrpra J.; Saahtar. Paul I. C0MU4 DIP: <30. M, V, IM*. 470*. SIN, MO **y 74 33** 0a*t Ha: SCCMP-TM3t3T4 HotItar: to acOaaau. 6**17004 Daacrlptara; Antifaullng aaating*. ***lar pallution. Marina* . *C4pgar> Chlarin# arpantc oanpauiPB. RarcRant OT*a. CancantratlantCaapMitian). Marina alcraarpanln--. Icilogy, MarOTra, Mlatura*. Cnvlranaantat inpacta. Maraarp. California. IPantlf loro: PalyahlartnatOT Olphanyla. San Olaga HarMar, Araator 1343. Long Oaaah HsrOTr, Lot Anpalao Maraor. Araclar I3S4. Otphanyl/ahlara. OTISSOLO Traao OMtMvwta During PCS -->t)i Ming DpMttPa: Mb--DOT mtvwr ' (iwlraMMlil Dmiun tgancr, Saattla. Mm. Survail larva M Malinli giv. aifno*: oiaiavlcn. Jeaaph M.; Cahlar. Arnata B. ; Vaacarvaloa Oaarga 4.-, Otacfc. BoMart N.; Papa. Stapfian v. . fOMM) PIP: 130. OH. 440. S00 . 400 00*17000 Aug 77 I4p Oapt M: CPA/StO/S*77/03S Monitor; 10 Oaaerlptara: Otpnonyla. Vatar pal lut Ion. Monitoring, fefoaatan Olvar, OraPgtng. CMartno organic coapaunaa. iraeo alaaanta. Caneantrat I anl CaMpiii I t Ian). Oaeavary. Sadlnanta. Spall. pH, Matala. Conductivity. Porfaraanca evaluation. Iranafaraara. Cal Ifora Sactar la. Nltragan. Oxygon. Irorgantc phaapnataa. Inorganic auifiOTs, aaningan<staia) IPantlflara: Polychtartnatac b Iphony Is. `-ni dradpea. Saauia<aantngton). Arocior 1343. NT I SI pal *0-374 00O/7ST Mf IS Prieaa: I OrOar PO-374 #40. Mp AOO SaaalIna Caneantratlana a* PatycftlarinataP Otphanylt aid POT In LOT MlaMgan f IOT. 1071 Mat IonaI Valor Ouoltty la*.. Ouluth. Mlnn.laconaln Unlv.. HaPtaan. Oapt. of Civil and Cnvlranaantal Cnglmartng. AUVMM: faith. 01 loan 0. I04I4C4 fid: 130. If, OC. MC. STM. Mf. S7Z IS7S S* Mont tor; to COAITOOS P4. In Pastlctdaa Monitoring Jnl. . vS nl dun 7S. Sponaorad In part toy VUconaln Unlv.. Nadlaon. Oapt. of Civil ad Invtranaantal Cnglnoarlng. Inciudad in tha raport. Journal Artlclos on Pastlclda aaalduaa in Antool a. PO-374 a44. 0#4crtptara: *fraah valor fiahaa. Maatduaa. *001. leaa Michigan. Olpnanyla. Chlorina organic coapeunda. Concantratlan(Caapoaltlon). Trout. MatMafwa. UalghtlMata/vo- luaai. CMarahyOTacartoana. Maiahyaraearpona. Saiaan. Taaic laiarancaa, Oaa chroaategraan Moat apaetroacopy Idantlflara; *Paaticida raalduoa, aoprlnts. Polycniorlnatad Biphenyls. Otphanyl/eMara. Paaaltna studlaa. 0 laacoawlat ion . MTISCPAL A-Z2 HONS 0 1 8 3 1 3 PO-374 304/3S1 OTIS Prlaaa: PC aOO/Hf 401 m-tu w/vst rnt% Prlass: rr M fl'IM 04. m At| In ItirltAp. (fit |tw<riHMHUI nnc<wi tmty. WmIUhHw, O.C. r(trla m InlMiMn Olv.*flah and Wlldllfa Sarvica, WsdMngtan. O.C #f TMnteal imIiimm. MIHM: RMmtmi, NhI O.j larMtam, fyts I, cottoos nn m, . c. cog. nt, n huitm ioto gi Mnlttr: to 0w. HI NatMina Monitoring Jnl., *d r4 9947-904 Mar to. n-prrt m aannatm aith flan and anaiifa tarviea, MOtlnttaN, o.c. OW. # ftowtaal laaiaima. inalufM In tha raaart, nurmi ifinta# m Natlcm naiauM in miaali, pp-974 040. Oaacrtptars: tiros. muiwt KMariaa ar^ic rrr--ft. OmaetiaifM, faiwmriUntcinimM, tor. oiaidrm. CMdrlna Aliphatic aa^aiMa. Ipaay aanauMi, cMarim PMOtls Mi Mi.......... finwvll. Chlarnw, 4y prateli. Iialaidwiaf Itataa). (nplIng. iniaa(Oaia) IfMtiMara: faitlaifi ratitM, taprinta. intma. NkMalHiMaa. WUNawlHnw/NpualilTa-laiHiyna. laniana/- hawoMara, lifwawyl/awara, NlyOtlarlwM feiphanyli. CMirnw/aay. MaeamlaitM, NtlMNl fO-9T4 400/4ST wn$ frleaa: K M/W 0I OMital Mir lonro Prajaal Mval Mpart 1*74 Vwttrn Caltfamia Caaattl Niar iiaaran ra)iei. Intarlo rapt, jut T)*jw 74. , IO400CI MO: IS, Of. 04. 440. STH. 470 Sap 74 14 tp apt Ma: CCWdP-A*t-T4 Monitor; to 04417400 () Descriptors: iMriM hlolapy. 'Ccology. Watar pollution. Coadts, Imlraaaantal laraaf. Surveys. Mtaii. casts watar. 00f. SaaMarts. Samps atapsaal. Itpanyl. CMarahydracarMona. CsnaawlrallswKsMpasltlen). liar Sirs. north Pacific Ocean, Oanthaa. Merchant ships. floras, Aniaal aisaasas. Invartaaratao. Outfall ocaars. California insntlfiars: Ocstw *ota Cispaaat. OtphMyyi/cMara. PalyoMortnotad aiphanylo. Franc aatalo. MflSSCt.0 Oa.yjMTM- otphanyls In Hart*. Opstm 0ft Southern SMthara Cat Ifamia Coastal Water Oeeeerch Project. (I 4OTM04: McOeraett. Thaaaora c. OalrOra j. Iiaairy rapt. 1071-70 9040949 Ilf: 44. 4f. 7H. 470, Ma* 79 4Op Oapt Ma: SCCUBP-n09J-79 Monitor; to Voung. Oavta ; Maaaan. D 0*417409 Oaacrlptara: Wetar pollution. Chlorine or^nlc rnrwrUt *04lt ahlaala. Cencontretten<Cenpositlon). California! TSMaa<Ololapy|. Ocean awlrdiatntt. Marina Ololoov leawMltilaa, flatflohas. Crahs. KitMli tOanttfiers: Polycntorlnatae biphenyls. water pollution Ottacilon. traceiors. Plphonyi/chlora. loaccunulat ion. loaic suhotancaa. fin nocrooia. Marino ocoiogy. NTISSOLO fl-979 474/09T MTIS Prlcos: PC AOS/MF *01 Cffaots of Ooaan Ouaplhp activity. Nia-Attantle - ip70 liwtrsmnul Prolocllon Ipancy. Phi loCalphts. Pa. Papton III. 4UMOO: iaor. Oensld W.j O'Millay, Marrta L-; Saith. Susan it Interla rapt. CO90II9 f 14: I3P. 44. MO. 470 01417403 4apt M: CP4/003/0-T7/090 Hanitar: 14 Oascrlptars: Savapa slud*a. Saapl Inp. "-------------------------1`ipuni lanj. Matalo. flrpanic caapaunda. Caroon, Chiorins orpamc caapniMli, MIC-4tlantlc lht. North Atlantic Ocaan. Sedments . frsnaa. Halopan srpanic coapeunaa, Sactarla. ciana Identifiers: Solid uaata disposal, Ocaan wasta aisposal Watar pollution Maphip, Poiycniorinaiaa aipnanyis. Arctic* slandiea. Arocniar I9S4, watar pollution affocts(Aniaets). HONS 0 1 8 3 1 4 PO-974 444/7ST MtlS PriOOS- PC AOD/Mf AOI 70-979 Ma/HT MTIS PpMn: K 40P/HF tOI art ItaMlInttai oF Nikola IXM UpfyU mo imii lit. a cm* Stuoy. rin* ^rttMtln Ipncy. Atlanta, a. tofim IV. Mina*: VltMfMn, Opyuan* T.j TMMlMl r*t. 4un Tl-M 77 INIIPI M: V*. M*. f mi n a * Mltar: * Stroup. IrM I.; flttum toltn. NMrltrt: * allvtlM orpaol* MMMM. faint Mm MwitM. faMlN, Mtlar *011 Mllli. CMrim tivor. lellvdM Mn. OmimI lr*i IMittftari: HlychlarlwiM itphmrl*. MMtlM. Mil *lt. MflSCPAL Malar pllu< ion a-IM I 10/OST MTIS Prlcoa: PC uva *01 MT*f C*r*.. Qelaan. *-- -y--`-rmtil Tniartlnn npariu. M*a IrlMflt IM, N.C. <40* 904) WTIM: Hal l*r, B.f OarOan. 4.: Kamraldi, *. Final rapt* (0170*9 FI*S T. 44. IM*. ITT* OUlTMt *pr TO TTp* apt da: m*TIM*MM GWltmt; 104*00*09* 14*1 ant tar: 104/400/9-77/040 Oaoerlptora: *ir pollution. CHIorlno rpan in Pttyalcai prapartlao. coaaical praparnaa. nanitarinp. uwren. 4ninala. InlMtip. Mile nooitn. 4taaapn*rte eirfuaiai. Cbaoicol analyala. 4tr pollution control. Carclugpim, leoiopv . faMlIno. Ooa aalyali * logntlflara: PolyoMorinatoO ptpfionyt*. potti of pot Ivtenta. Atr pollution oFFct44nioota). MTIMF44M MTMM: ncato. jaan P. jaornat orttcio 09009*9 FI*; OF. 0V. 0C. 130. 7M. 07V. 00F. *00 OMI7790 17 4an 77 top Popt Na: (04/000/4*77/040 Mnttor: 10 Pi*, in *11. of Manor!** Ooaoarcn Ooar* of Canto*. V34 no pi 140* 1104 1077. Oaoerlptora: *40*1101*0*. Toalcttr. MMoa. vaiar pollution . llfo cy4lo*. Nttalg, Snap*. Oipnonyl. Ctitorirw orpanic eotpwnn. Survival, (valuation. Oroutti, "--------------11 iTnlrmpiot It Ion). Tloo. lupoturo. Sonaltlvtty. Fra*let ton* IMt I Flora: aoprint*. * Ipnony l/cnioro. btphanyi*. wmtPAOOO Potychlor iratM P0-979 447/407 MTIS Prlcoa: Not avalloblo NfIS *** *f TCS'g an* BOT in tfa Maotarn Ufco i-prrlir IcatyatM ^ iwlfpwntal Oaaoarch Lab. -Ouluth, Niv>. AlfTMO: Volt*. 0. 0.; Wuahl. 0. *.; Eaton. 4. O. ; Pu*ll*l. F. 4.; aiaaa. . 4oumal artlcla 09794P9 Ft*: *F. 13*. 07H. 1077 I4p Oapt Na: (04/000/4*77/040 Aonlter: to 00( 0PAI773S Pi*. In IrcMnt of (nvlranooctal Cwttaoinat Ion and Toalcolopy. vl p407*4*0 1*77. Oaoerlptora: *Poattcl*M. 4l*ai, *La4# MtPlor, OOT. failOai. iphonyl*. Cfilprln* orpanic coopounoa. Trout. Cencantrat lan<Caopo> 11 ton). $ii Oattrotnattan. Cnioretfan. Hapmnalana coaaounOa. Boraona. 0l*l*rln. CMoronydrocarbona. HalonyOrocorbona. TolarancaalPttyaielopy) lUantfflora; Folydilortnato* btpMnyla, anaano/fiaaacniaro. Monaclor, NT (Sir*040 Otpnanyt/cMero HONS 0 1 8 3 1 5 70*971 TP*/1ST MTIS Prlcoa; PC 409/PF M>l (valuation f TPota vita forly UF* Itapaa of Flap far Pro*lot 1tip lap Taro Ta*lolly (NWlr< Hal Paaaarafi Lao -Owlutn. atm. HONS 0 1 8 3 1 6 *-*71 TM/m WTIS Prlcw: PC AOO/W'Ao rywM CMMiwiti UP. -Ouluth,, Minn. WW; IIm, . I.t Stracfan, . a. i. 4r--Ucw>. P. I. I.s MINT, K. 1. i. ilwnwt irttclp Masit pic; ia, cm. mo timi 1*77 9Q M Mo: IP/0/^TT/OI> Monitor: It PMT*MI 1077. i an vJ rlptorp; Orpantp coMewnta. wtroUwlCoaMUlM), Olpfwnylo. *Lna Motor SumtIot pot lot ion! JSlTi!?* . 0t~m. IWH, mwxii.. CmnMM. Ittw. mnitua. Mmimhi, mariw r|Mie r--111*' --f. Hmcwi--. OlaM-in. lntK palyMelw IMirian: M<w Ml Iuiiot mpHnp. 0 lor in, WnklvMIM MHWIII. MB HMIttM >. DM tnooettcioo. DBaltaMMpliHialMM, Iwwi/Ni __ ... CM llnOTne. CytlOOM* Styrono/octocnioro. MptooPilor opMlCo. fMtpoM/oot%l -Ponte, r Into. NUSfPAOOO M0-97I OI7/0ST NT IS PrlCM: PC A04/W 0I PCM iNftlMMRt In to* Pulp i Pmm liMatry Noroor, Inc., Sprmpfleld. Ve.(nvtreneentat Protection Money. Moehinpten. i.c. Office of Toole SuPetoncee. oMOrlcfc A.i tarfee, AoPort Pine) rapt, on Toon 4 09S94M PIN: OP, 0T. 190. 000. M. S7 90 POP 77 IMp Oopt MO: 474.SA Contrpct! IPA-M-OI-39M MrI ter: fPA/SOO/O-77/OOO Sot ole* PO-909 Olt. t.; McKay, OOAI7799 *^ fdoerd 6 . Cnoironoontol lopocto. ,, ** tOTOrM, StaTOTO, Coot OTtlWtOO. Motor pollution oontrel. Air pollution control, Intaotrioi ueotoe Incinorotlon. Co rean. Aooorptian. Pracooa anar tin*, ruiainp, Coitaotion tfoApto, MOtNOMtlWI Mill oelrouloiten, Coot anoiyoio r' IMtlflfrt: Otpnonyl/onioro. Polychlorinated pipnonyio. Pam f pollutants. MriSCPMTS A Plrot OrOor Nn ,,M^llor tho Sourcoo. DUtrioutlon oM Poto o# PCSo In Oo Cnvl Viriir, Inc.. Sprlnpf told, Vt.'InvlrmantHl Pmiart aM Aponcy. MMIngion. O.C. Office of Tone kbitm*!. *UTMM: IO Itnor*. Pro** C. flnol ropt. 0990109 flo: 190. M0. M* >7 0ul 77 100 opt Mo: 474-M Contrect: IM-U-OI-33M Monitor: fPA/40Q/-77/000 00*17732 DMcrlpw,: .ii, poll., ion, .Mt- pollution. .Cm or In. orponic co*powi, *teke Micnipon. Greet least. nemoMttcai AOPorptlon. rollout. leufcn. (tlleoteo **o evaporation. Coneontrolon<Coepeeltlon), |rput Id nil flo o: Polychlorinated Otpnonylo. 01 lotion, NTIMP40TS Olpnanyl/chloro. "SM 9SO/SS7 NTII Prlcoo: PC AM/NF |Q| Methodology for MlNtl Air and stotlo Polychlorinated I - A Aovtew In InvIrofManlol Mon I tor tnQ ond Support top. Pork. N.C. tael I ty Aoowronco ironen. oooorcn Trionpl* AUTM00: NarpOAOT. JOtn H. final ropt. 0SI04G4 fid 7C. 140, Ml*. *#r 77 30p* mi N: CP4/000/4-77/091 Monitor: to M* p*17770 Ooocriptoro: *Oovlou. Chlorine orpanic roirnomim Gao onolyaio. Cheolcel onolyoio. Manltorlfw. Al< Polyurethane reoino. fPOM. f"reelIon. Goo dn APaorpt it CMOTlCAl Idonllfloro: Slotlonory aourcoo. folycniorinotod OlpMnyla Air pel tut ion eatectier. Arocloro. electron copturo ootoctora . Oiphony 1/cMtoro. MUStriOM HONS 0 1 8 3 1 7 w-wr --/opt wmm--a: tot mis M# tola-tor Slim is*wsm in Mr m* to: toto m too--a-- to Alr/ta Tr--Hr Mito laiMi M.. R(fpto. tot. to 9mm to to--arcs cmiitnr.tottMil IttoM Fw--iim, toMn*to. O.c. Off to* far to Onto to Pcasw f--tarattsn. tolMOK: T. r.s RIOT. C. P.i Pin--. C. (. MWin FIC II*. ON. um, WO WO 17710 (IN IN rant: NPF-X'*07T7 tonttar: W/IM*n<M too. In tort-- Nilatot Tra--far. c--ptar to. pias^Nt iota. Oaaertptara: M>>tiiH>n, --tict--a, totar pallutlon, *(p oaltutto, CMtart-- orpanto aaaaaunto. tir --tar tntaraetlana. CawampitliwlCtoiiltin). Trapaap--ra. nor. Otaaaptoria Olffuslan. Saa Mtar lOTnttrtara: toprtnto. totn mf pollutants. Poiycniort--t-- Blp--nyla. Intamattanal Daeaaa a# Ocaan l--loration. NTlSiOSf . NTlWrt to-007 OM/Otr NT IS tolCOTS PC OOP/NF AOt Itoto Stata totv., oaeatalia. Oapt. tt lMiatr.omot or totar iaaaanan ana Ts--(apy. to--t--tan. o.c. MlIHM: Kant. --a-- C. toatar'a ttoala MM0M0 IN: to. ON. SOD. 4M. STM. ITt. STI tTS If* Contract: lf404000t0t^ Rrajaat: MM*00< IOA tonltar: --PT-A-O4l~l0*(t) ORA!77IT toaarlptara: *toattal--a. *totar pat (at tan. rtatoa. Iran aatar flatoa. Inaaattcttoa, Cttlartna arjanta aanpaanOT. totar analrota. Ctonteal analysts. WT. li--alopy. D latar in. torouri(total). Ca--i--. Ca--trat tan(Caop--tttanl. Sostaant* . Btaaaaay. tool--. totala. arsonte. Fartictos. Stan----a. Saapllto Itonttitara: FaiyaMar <--t-- a*p--ny is. imrcwiUitan. totar rwnaf. H--m aata*a. BOO tnasct tataos. aaattatto rttiam, MTISBIOOTT ni*7aa aw/asr Mils Mien: rc aos/MF aot I--Ira--antal toltoKaa to Mvan--P S--tn--al Mwiyaaa: Paaiatanoa Fra)--ts FT 7 -- |totranaantal Baaaarcn tab., at--, to. analytical Ctoatttry attiMOT: atfara. tm i. D7--IO) n; I3B. TO. OM. MD aat7719 ton 77 oap Root to: (aa/aoo/o*tt/oos Frafoct. (M tlOIO atf Monitor: ts Saa also rapart aataa ton TS. Not) OM. Oaacrtptars: --tar analysis. CMIari-- orpsnic ca--aun-- aoaarottan opoctra. tooto--try. Chontcal analysis. Ora--te esap--nto. I----trial aastas. Traca alaaonts. Fionas. Poultry Mtttt, Fat--la valor, atonic spactroacopy. toss spactro--try tos cnraoataprapny. torcary. Saa vatsr. Flsnts(totany). Son analysts, (lactrie --r plants. Neutron activation analysis CancontrattonICeapos11 ton) lOantlMars: *totor pollution totactlon. aipnanyis. ntiskfmmo Oolycnior Inatad BO'MP 7M/SST MTIS Fries*: PC OOP/MF AOI (#--ts to Oroctar (Tr--irti) 'lalvsil--a (anti--Its' tPM an Orask Trout ' (nvlr--tal Pasaarcn L--.-Oulutft, aim. OOTMoa: Snarafet. Vtrptnta It.; Pupils'. Frank 0. Final rapt. IS73-74 DSPSSPt FIS: PT. PF. IIP. PPF. PPO. STY. S7H at TP 4Op apt to: IP0/P00/l*?P/iia tonltor; IP WAI77I9 tocrtptors: Trout. --------t r~7Tttr ci--........ la. *410--0. toystalspiesl sir--ts. TMIstlOtuI. prswtn, Paprotoct lontato* topy). Ptaassoy. (--uro. toco--anas Hons. Toaleolopy, Survival. Its--ostplolopyl, Anslyttnp. So--I Ing. Fraotoatsr f ts--a. Past--. Cancontrat ionic--as It ion) ItontlTtaro: Pip--nyl/cnlora. Aroclor t|S. piaacnawlstt-- tolar pal tut tan oMaetstSni--is). Solvaltnus I--tlnslls BaiycMlari--to# kipanyii, NVitcrsoao W*N> IMMT MfIS Prli i kr 'Mbtipm* ap rt: m, m, sts. a, Mia , MM SUITTM Nat Nat aifM'H'MI Mtltar: WMWtllW M. Mt il. al *fM<alur8l ani NaiCMlaUy, *14 ant*iM DaacF tptaro; *ll*itarlarat tan. lactaria, UpMnyl, NiyaNnyl MNMN, OilariM arparia NapMnM. Oir*l laa, NiaktUM . Ntp pallutlM. CaraantfatlanlCMaMltlanl. Surface aatara, lams. infanta lOanttftart: aipnanyl/cMara, Hlhallsanaa, NTlSCOtaMA N'2M aSt/TST NT IS NlCN: TC AOS/NF AOI Natraatlan a flyflarlaiatNl Hfftanrla In fauapa Studpa Surln Inalnaratlan Paraar. Inc. Sprtnpftala. Va.*(mlrgfatnttl Protactton Afanci. NaMaaian. D C. 335) NfNoa: Wiltaara. Irwa C. final rant. ooosaao t ia: iaa. aaa. aac tm sop Contract: (pa M-OI-lUT Mwitaf: < out 743a Ooocrtptoro: fiuepa etapooot. tnetnorotoro. atr pollution. Salta wata Ntaaaaal. Ia*aga aludpe, cniortne r~rrrritc ca^Mwnaa. Peceapeeltlen. Plua paeoo, Saa seapl ing. Na anaiytia laantiftara: Haianyl/ciiiara. Pol yenlor inatad btpnonylo. NIIUPM . PI-NI mo/1ST Nils Priaaa: PC 09/ SOI PCS IMaaloata fraaa Stationary tairaaa: A TNaaretloal Stucy Nonaonto SaaaarWt Carp., Ooytan, Ohta. Oeyten laa.Industrial Invlranaontal Paaaarcft laa., Saaaarclt Trlanolo Para. M.c. ( 401 SMI AUTNM: Knlarloa. Nornan Jr Final rapt. 0MHD4 FIN: TA. Ml*. MS* oct h lap* aapa Me: npc-Oa*5T7 canlract: fPI*M-M-i)IO anttar: pa/#oo/T*TS/tt MAITPM Oaaertptara: Aon content, laoaara. `Maeeaaanta. FaaaM rala, llactrtc paaar planta. Oaldatten, TaPioalSata). Cnlerlno erpenlc aanpaunCa. Air pollution. Caoi, Natural paaaa , Fual ail. Fumoeae. Oaactian ktnattca. irauue polycyclic nydraaarOone. Thamadynoalca. Sallara. Cnealcal anoiyete. rarT ~T-------- pracucta. Inouetrtol voFtaa, Saa anoiyete, CanaantratfwUaapaa11tan). SaapMnp, Fly can laanttFlara: Slpnonyl/cMoro. itr pallutian cataetian. Caal*FlraO paaar planta. Stationary aaurcaa. Peiyctilor inetod atpnanyia. mviwpmm HONS 0183X 8 n-IH MI/ST OTIS PrlflM: PC ftlS/W 0t Ttriif, Inc.. IprlnfMtM, Si.*Swrli w--wUI Prttactln Hwiy, MNHInytw, I.C. Wflea f MMr Mamtflf and ItanOTr*. (M SMI OTINM: OOTfN. Mart I ImI rapt, an Task S ciwiK nt m. ta, as*, fts* I M N MS* Cantraat: IN*Ot*aN Mnitar: ta/MO/-ra/OM auras Paaarlptarc; *at*r pallutlan eantral, Intaiotrlat vasts li safari. assign crltarla. Aetlvatsd cardan. AdaorpontsfMatsrlsls). OtpanyU. Catarina organic capawaa. NanufMiata* Craantcal tnaatry, Capacttcra, Trane Forarc. Cardan. Capitalized oaata. Operating caata. Coat eatiaeta*. Praaaaa atari lap, ifriwata, careantrat an<toapaai t law). Settd aaata dtapaaal. Air pollution. Cert* flits. SorForaanco avalnatlan, Osanatlan. Incinerators, filtration. Olla. Standards. Ultrovldlst radiatlan I dent If fare; Alpnanyl/ctiloro. PdtycMIertnatdd biptanyla. Aadarttta palynara. NTIIItM., ntimsamp ni'tu TSS/SST Mtl$ prices: SC A07/NF SOI Hulas af PCS lanla in Ida Iialranant CiwtrcrsHntal Protection Agency. Dallas, Tea. SagI on VI. AUTHOP: f Inlay. Oarls J.; Slff, f radar let M.; OaCarlo. d. Pinal rapt. CHWI3 P Id: P, 130. S7W*. AC*. MO QUITS It dan T I43p* apt Ma; IfA/SM/T'TI'WI Manlier: is vtneant Osscrlptars: CMcrins organic coapounde. Psattetdea, SollutIon, Monitoring. Color roaourcaa. Sedfente, Solla. FIshoe. Slrda. Lehee. Slvsre. Ocaaa awlraiaania, Sewage traatnant. Industrial plants. Food, Huaana. Cneantrtlw<CM- position), SoluSlllty. Takloc(Oete) Identifiers: diphenyl/eft loro. blpftanyls. NVISffAOTS Arochlor. Salychlor inatad 6TC8T0 SNOW AO-AOM S07/T NTIS Sr fas: SC AM/OT AOt fffddt d# MV and PotyOTilsrlftotad StpMnpls an Coll Sopulatlon PaaP dP 'QrttMdts PsaalPilata'. A rrapsllstdd Sratdaaan Arawd Farads Padladialapy Qaiaaron Inst Ostftaeda nd (034700) AimCOT: Sronad. d. *.; dadaris. d. F. Sclantlftc rapt. C700SHI Sid: ST. OS. IM. ATT. AM. 17S Hay TA SOP Oapt Ha: APS0I-SS7A-I1 Sraldati HA HU MW took: CM) anitar: A 0SAI7AIA Oosdrtptdrs: *Call division, *OOT, CHterineted hydrocarbons. Alpnanyl. Inaaatialdaa. Srataaaa. Taaiaiiy. Hsiadaitao. Canoontrat tanCCaapaa 11 tan) Idontiftart: Critnidia faactcwlats. ia*lcalagy. FasticIdas. MTISOOOHA *911 439/VST MTIS *rk *c na/v mi MVtPlfl KHHtMtl. TMk SI riTTL." lino, Ira.. HHwsffM. a.lmrtrtMvtMt Pretact let Ofanoy* MmAIn|w, P.C. Vflei #7 TmM trastraoaa. (W 9391 umiii krrm, Mart i.s i fill Orica. Kranat* rinai Npt. C9493MI III: 139. ?, 999. M9 99AIT9I3 30 ran tv tora Crarat: CPAV*04*9990 -4r pat let inn rantml. InOralrlal own . _ ____ *CMrtra irratv raramnra. I (Sambo* trratvant). tatlvaMi i*ra*n (rwtmt CvwtrMlwffwMinrai. iliirfMi. Sol 10 want* !**** I Imtnarattan, irtluanii. CoitaliM aai. 9p*rattno aai. Kara, flUHlwtlaw. Ultra*mint raHa, Air a>HutIan itral. Coot aallaaiM. liltfattan, CMalcal raaaval(ratnr miiiHon VraralMlra. OalyOilotnata* ntpnanyU, 99*990 TOO/1ST MTIS TrlflM; PC 499/IP AVI m ra ira NMWra fvoio ara 1 to nijmimimm oipranris I Prntnetlra Maney. CMcapo* 111. Vooion v. AllfM99t 9r--r. Rerl . CV393K4 SIV: 499. OOC. 09M. M0. MS ran T9 310 Manltar; 49 90AI79II oraertotoro: -rator onHot Ion, ilaktfan* VrattnoA. 9*poany< Caramrat laHCraa* 11 ton). Tr MMfM* ItiamaiH. Cpac I tan Tiara*. ifamara. fnaicity. *uta tnotana. Hitnata! rant I Mar*: iipNanyl/raiare. *ratar pnituttnn aMacts<4ni< >. Arnaiar*. PetyaMnr matae nipnanyla. Nri|(N9 !** J* ,h* raiiatin a# tnairranantat CantaiKatttn an* laalnalaor. ra nsI o03*7T9* *3S9 1973 QaacrlQtar*: (Water Nllwllan, aNalce 9ulf). (PeattctOaa. Pas lea OalH. CMarlna arganic eanpaunea. CMor In# araaatlo canparae*. 00T. Mm*tan. Ceriraaan Sea. CawaiirtHaHCaniif ftianl. CMor**' - - --*-- -- leant I Mara: 0a*allna 1 ra*. TC9, Vlpneny 1/cMor*. (OOC 09*344 799/4 Nt|f Trice*: TC *03/97 *04 Uptake or Tnale Mater Ttlkrtaili (0C9) 07 Ufea Traut Nartram atcMora ttniv.. nararatt*. o*pt. o* eioiopy- UtNM: Parajt*. teat*; John*tan. 0049904 M4: 9T. STM. 990. 49C jan 73 tto Cratract: 0l'14'O1*000*3S33 Orajact: OMM'4*OS*MICN Nani tar: OuM-A-O* l11 Aaynand 99*17307 Oaaerlptora: (*CMcrn* oroanie caapouno*. aaiOuaa). ((.afe* SOtrltr. Matar pollution). (Traut. OlalOuaal. (rat*r pallutlnn. CMarlna arpanic caapaunra). Accueulation, Tr*ra watar f 1*0. CanC*ntratfan<C*npo*ltlon|. DOT. 9a IPantlMara: *fipnanyI/cniero HONS 0 1 8 3 2 0 *0*394 934/9 MTIS Trie*#: Nat aval laOl# NTIS t tot ItMS 0--MptlM I M PCI M.PATQUilMTniVMIMN a mov iiwff a t wn 4 aoaav oiprwtr mm Mtvvwerim atwv wwiwaiTti T MM ATTCMItTION aatv MMwnw V MIM 4MIWIMTMI 10 TI4M 000* It 44 tAMOtO PrM 11/1/1-44 1--pm Tt--: 0.000 Prints: 44 ossas.: o i S HONS 0 1 8 3 2 1 MM Mint Cwtrtl IpiMir. tawvlll Pall (Mrlraii fwl- fNlMl vNnt Hr OCCTM ISSN 0007*4001 mClIPWIi (*0M0AMC CMMMI. Tr limn. IWIMHINVM TSSTSNO. leCMTIMCPS: PtlVOURIMfCI IIMNUS CARO <i(IT: MM. 00*. 411 1001 p HTI00I |p 01011000001 MOMMIMN M IMS *P1 IN HU IHfM MMMt pMSM HM. P*pl. 4. | Stop*. S. KKiirlil N*ry Mil*, Mm OelM. Ml* VIlfMMIM v It n 9 Hr ItPI p IMO COPCM: ULIM) ISSN Mf<41U OCSCPIPTOPS: (OIONCOICAL CMPINCCBINP. HIIINMnle Appl (cm Ipna). CMP Util: 401. 719 111*099 IP M,. (1010011099 CCLLISM 1WCM MU ANALYSIS ISM A Mrrm. N. .j Siae*. H. FraM Merlhrap far* In*. M Trlanpla Pam. NC CaapMt Olal Hi v *0 n 9 ipto p 109*107 C00CN: CPOMf PCSCPIPTOPO: (0I0PC01CAL (NPIMOiOIMO, *Cyf4lil, ( MATMIMAIICAL IMSVPUMIMTS. Pwfeat Calculaiora). C0MUTCP PPOOPAM. I PLASTICS. Iwlalty), IMNTItlCftS: PNOOPAMNAOLS CALCULATORS. TOAICOLOOV. POLfCHLOPOPIHMMVLS CAPO ALCPT: API. 710. 799. 017 IOIIS4I IP I1000041040 rum or amoclop ism rnnmm stump* imwwi mm mm. (Ml*. P. 4.; HIMIf*. C. Mapl, M. NdMM, O . If* (fivlrpi SCI. Ill Sin St, Anprpva. M Pwll InrlrMl Coni-- Teatepl v 14 n i Jan IMO p M-ll COOCN: OCCTM ||p| pQ0T*4PP4 OCSCPIPTOPS: (*WTIR POLLUTION. IwIrnMNUI taped). CwtlPAl). (OMOICALS. lOCNTIttCPS: MHCM.MIMTIO 0IPMCM7LS. PCOS CMP Alltl: 411, M3, KM. Ml WM9M 10 NO. - f100049*790 oltpa--lie mar op imp mnatic-iootpopic hmi nuisiriM m pm. fhlrtat. v.; NartlWtr, t. OKS. SlrMPPurp. Cr 4 PM (Ppll) v 40 n Mm *t7t P C00CN: 40PQM ISSN 0900*0190 OCSCOIPTOPS: (ClVtlUI. LI0WIO. Ultraeonle Cffpela). ( MTMSONIC MAVCS. AMPrptlen). CMP HOT: 004 . 709 1019040 IO NO.* 11000913040 MOOOPTIOM 00 UATCN*SOUMLf POLTOCOPINATfO OltMKMTL 1949 AMD USCD CAPACSTOP fLUIO 0V SOIL MATCPtALS SO COAL CHAPS. Laa. p. c.; Orirrm. a. a.; pi liar. m. l.; Chttn, c. s. k. Unlv al III. Ureana 4 Cnvlren Set Haaltlt tart A v A14 n s 1070 p 418-449 COOCM: 4CSC0U MSCPIPTOPS: (INDUSTRIAL MASTCS. TrMlnant). SOILS. CLAY. OPBANIC COMPOUMIf IMNMPIIPf: POLVCHLOAIMATCO OlPMtNTLS CAPO ALCPT: 4S9. 409. 004 HONS 018322 1079000 10 NO.* S1000079090 MTMUINN OP A OAO STPIPTIMO CONCSMTSATIM TIOPIM POP TMPCi OPOAMtC MATYP POLLUTANTS. calanwtt. o. A.; Thptuni, S- Prune I Unlv. UaMrlUpa. Ntupa. (npl Ini 4 environ Anal CM* v 7 n 9 4an 1000 p 991*944 COMM; IJ0AA9 ISSN 0000*7910 MSCOItTOPO: HMTIP ANALYSIS. VATfP fOLLUTION. CAPO Ai(0f: 440. 001. 409 HONS 0 1 8 3 *3 (Iwwl*. t. 4.; ItollM, 3. 4.: MVMI). T. C. Unlv # Him, BiNMtpHi | An Cnee We li (iwlrm Ow Orspr v t n t lTt: Prmr of Pt0 rinwWH it the aaetl Maw. cm*. Mwwlvlw, Mwm, Apr `' ` ' '" Ota ef (iwlmn Ctai, CINf Cmlrtl). UK|S, IMWimh: IIBIMNTI CM* AUlf: 4N, HOT. 444. *13. 30*. 304 (Mo) mWMW w ' Mm . witomnon* imcnu icn mm buch WfwwrMN IM. I. *.J IrMlM, A. H i tu *il of Tim. KmmvI 1la ^ Owi Tun Wt lna liairm Sc I 3tn. Seattle. Mean. M'My t tot*. Ml *y lm% a# Inviren Set. Ml. Waapaot. ttl. p 490-4*4 COMM: I ISAS' OCSCOfOTWf: VATIC MtllfTlON. 030ANIC MMMIt, (CMfPICAi tjenjl. WaatlCM Klnatica). NATMKNATICAt MOILS. CM103INI lOCMTI'IIOS: AOiVCMtOOIMATI* IIPMKMTCS CAM AtlOT: 4*3. KM **7*1 ID M3. lITtlMIMI MWII* *3 TM1CITT torA MM Cl TAW--A M-- MATIN --AtITT ST4--A3M. Klapaa. laaranea A.; teats. OaOert It. Celt' State Mater Aeeour Centrel Oeerc. finraeenu 4 Mater Pet tat Central 'ee n * t w* t*7* p soom-joto COOIM: MM ISSN 0043' I3M OCSCBIATOOSt (MTfl ANALYSIS. Tealctty). (MATI3 POLLUTION. Meter Reality). MAStlMATI*. WAVY MBTAtS. (SIAMAIM. Analysts) CAM AtlOT: 44*. Ml. 014. 4*3. *3t. 4tl OOOOM 13 M.- IIT3II30090 _____ PMO mm -- WMOIMT *KM MPMA*. tfTAM, tinwall. Mar*; tea. Aessap o. Utan State UMv. lepan Oatt liatrei Centaa Tea Ice) a 33 n 9 Aua COOIM: OfCTAO . I0T9 p 704-700 tssM cooT*4eet OCSCPiefOM: ('fSTIClMS. Irwlrementet imctl <ATf0 pollution. atani. w. oimlOcCMtvnisi'tiOS: OOWMOCHtOaiNK PfSTICIOCS. rOLVCHLOMIMATCO CAM 4LC3T: 004. sot. 493 OT*tO* IO NO.- 111904791*9 TMAC* OMAMCS NMOVAL OT AO--0 MA*T| TMATMDfT Oe*Smre. Martin: Oatce. Cerla 4.; PeCerty. prry t. StwSeri intv, Caitt ^SCI natron In* Otv a 109 n 4 lug 1ST* p !Tt*tt3 JJCOirtOOS: (*114114 TBCATNfM?. `ChMiCala aaeovall. OOOANIC IMMTt'UOS: TOACI (tIMIMTS. TRACT 006AMICS KMVAL CAM AtlOT: 440 . 004 TtOM TO NO.. 1170007903* ANALYSIS O' KttCTCO THACC 3N3MIC* SN AO--0 MASTIMATM T--TNUr SYST--. Oatre. Oeepar; wins. Micnaet: Maaetne. 4anes; Chappelte, Sen Mae Creek Meter Quel Lae, Mntttter. Call' Meter Oea flint fOTO P 4*3-103 CODCN: VATOAC | .ISSN 0043-1304 MSCOI'TORS: (MASTIWAf 0 Anelyolsj. MAT!* ANALYSIS. CMNMMTOOMAPHfC ANAtVSIS. OOOANIC COMPOUNDS. IMNTimtt; MASTIMIC* TSCATMCNT SVSVCMS CAM AtlOT: 403. 40t. 004. 449 10 NO.' 11790004TOO O' ML--*INATM OtPNCMYL ONTO SIA OCO WWWT. HAMM PUMOCTON, AMO QY7NN AO--I0INO AO--TS. Niriinet, veauont; Tahanesni, Nteaei NitMmri, msitea Unia ef Tofcye. opn f^ltajfei Set Taetata I a t> n % Hay lf) p *00-944 COOCN: ISSN OOI3-OMH OlSCOiefOOS: SC0IMKNTATION. CNLOaiMf CPOOIMt, AOSOasriON (MA1C0 POLLUTION. Analysis). CAM AtlOT: 031. 004. Ml. 003. 493 ui, r* mo ran. wi a conrii mrwm mtK'imtmm tai mtmwr. tc Min Can# m K*l Dy Cl* Nln iellvaM), 913441 I MS.* CIT9021344I iSSm***** T**,C **** W M*T*M MM tiKOOa ST Mrylll. CO Caiaaan. Maltar o.; Mir, CroriMi. Hass 4IOH 9yop 9ar y 74 n III |||. MV. Ifll a I4I-M0 COMM: 4CSSC0 0*MI *y *IChf. tm vork. CMO lull: 441, 413 UMv a# aim, Mm fnrlran Sol Too ISTHM ol la V HMMy tm a !H`IT3 COMM: tssM ooiMaai mccmictomii (uuecs. Muantotim), irurmic movcmcmti 1COSTSfCMS, I0CMT1MC0S: ttOfMNTt. ATMMPHCMIC IIMWCI CMD AlCST; 444. SSI, 449, 4SI, 4S9. Ml **"-- " . miowaiM mwimiON mn ar km t uw< miiw vMT. Thnasa.s Otaaivtfca. Cftarlo* a. Ooaaai univ. cnicaoo. IH ^ r**' VMaa Mas v 3 a 3-4 Oac iitt p 30S-3i2 COOCM: (OMGMIIC Cnviraaoontal lapactl. Ul aotiuuoM. iiwtraamut loaact). min mo riinmu. lmcis lOCNTfrilOS: OOiVOCMlMATCO aiMNTlt ' C4S0 HUT: 493. 491. 443. 444 0--OP IP 10. (17900901TO Ml Of Univ Os CarOMM, Tatanca. tr vS! IS!IT ***** T-->c* V S3 n 1* Hay 1979 p 90-04 ISSN 0007-4941 ocscalaroos: < CNCMIC419, CnylronaaMal lapactl. aotuniOM. Control ). (0M9MI1C C99WBI, ImlrSManiil (MATCO lOCNTIVICOS: rot VCNLOftllttrfO 9I9HCMVL. PCS CA09 41101: 903. 904. 901. 493 990733 10 NO.- Cl790790732 1M9CCTICIM9. aOLVCMLOMIIMTCO liniKTU oaaiCMI UH CCOSTSTCHS 9CM 00SH9 3. rrrr__0ra Idtgs .Tvanwa 4.: OratclM, llglraas; SD Stata Untv, trackings Mull Cnvlron Contaa Tostcol v 19 n 4 isr COMM: 9CCT49 MSCOIPTOOS: (IMSCCTICIOCS. fnvIronaantaI aotlUTiO*. Vasttcias Cfiactal. aim, Many*) locNTiricas: rotvcMooiiMTco 4ir***ms. SC4 COp 4LC0T: 904 . 901. 444 . 492 1974 p (pact) IN 0.: 494-441 <4T|ft HONS 0 1 8 3 2 * 2TIM 10 NO.- CI790437I49 Mt acsnciM MSIOHCS only of oya. laroata 9M fayIran Cantaa Taslcal COMM: MT49 v 2 I n 1-2 tan 1979 a 114-134 I99M 000T-4MI Mianaroat: 0MIN0CIK.4MIMC (aconciMt. PC9TICIM9. nCLVOHOB iMkTco'aiaNCMTis. a3a?%>' CANO 4U0T: 404. 901 laranaa. Man; Vasins. Hail* m. Can Cant far (mans uatara. awti^tm. ott. IITOM*** *** ***'* a to n 4 Apr 1474 p Ml - 943 Cl|)tn, Mm I. Nvtw, larw P.; Irvitnar, Nmwi f. miv af w*. Smui# iat TCMn*( v II It ? aut 1*77 a *7*-tl 000CM: 0CSC4IPT0PS: *447(4 POLLUTION. (HlOSOCAPOONS. AMorpt ton) lOUfftflfPS: POLVOP.OPINATIO IIOfNILS CAPO AL(PV: 449. 404 acscatatait: i*ria Muiman. Imlyaiah CAPO auiT; 4IS, 471. Ml amir*'*). <sianatcr. 777771 ID M.~ 11770447771 MMVTNM V KS'I 44 447*1 ON HMMM P1LT444 MH 44HI A MW AMItmt HI1. Kurts. 4mM 4. As tiata Unia. otlvaraliy Park 4all Iwtran fawlaa Taalaal 17 a 4 ar 1477 p 94I-9M COOCNi (C?AP NWIiaiMi (MNWCTICIOCS. *lMlyala). I4ATC4 POLLUTION, NitlaMa Iflaitt), UAIfl MM.7SI4. iMlallyl, | WWOCOI44, tiwlriWHial l^aai), PU7BPS. IMWirimi P0LVCML0PIMATC0 4IIKMIS. PCI CA44 ALKRTx 404. 449. 441. 401. 014. 401 __40*990 IP NO.* (1741941994 swm m iw anavrioM or Itucrra lOMMi 1MM 0M MlttAL BUMPACCS. ISSM. ScMatfpInp. o. Orap Staia unfa. Caraaiii* rotrcMooiwiTn W In*Iran Let Maaltn Part B a m n 9 1*74 p 134*197 C00CN: 4PPCD9 M9CPIPT0PS: t*HT0P0CAP00NS. *AUaarptIan). SOIL POLLUTION. IMNTIPKOt: POLVCNLOPINATIO PIPMCNVLS CAPO AUPT: M9. 104 . 409 . 449 070400 10 NO.* (174117*404 Pistaa cuwop opout pco*i. HIMr#" *Gi T,C>lno1 V lO n 9 Mb 1*7* a 199-133 COOCN: I 5tf 74MQ0 10 Ml.* (1770441904 i l.t ttak _ Inst. * 94 n 4 Nw 1474 p 441*471 000CN: <J 0C4C4IPT444: (*MT POLLUTION. 4lMla). IMPOUNDS. MVOPOCAPOONS. 400AMIC CMSM1CALS. CAPO AiCtt: 419. 404. 409 oaseaiprops: *uat(o pollution, invopocapoons. CHLOPiaC COHPOU0S. KOISLAT ION. IMNTIIKM: POLVCMLOPINAKO PIPHCNVIS CAPO ALCPT: 4S9. 009. KM. 409 To.iettyi 04444* ^jO^NO.-(174074444* CAST TISM. OMPLASTIC AMD AOJACOTT 794119 14 IP.- (1770194319 ^ . . w-lr*. o. P.; Taaatla. L.j Ulrra. a. P.s BNlUata. M.; an*. 0.; Cuea*. Stall lea; Yanimm. Oora Hau Untv. MbUasaa* Mas sen. Uarwsalan. |sr lull (nalran Camas Tsatcot COOCN: 4CCTA4 a IS n 4 Apr t*T p 414-444 NOAA, 1 Poll*. C4II7 (Mwiraa Sal tiaiwai 10 a 19 Oae 1474 a 1999*1994 lliwo C04CM: OSSCPIPIOPS: (INSfCTICIOCS. Toalclly), (MlNStaiMC. Liainp Syatasa Stuai**). CAPO ALfPT: 404 . 441 (4I0NC0ICAL m4iCw4Cp4ii|P. Vs4e4faSt 1*414 POLLUTION. pouovim. ouum niMaplywtlti.), NV0P4CA0MNS. CAPO AilPT: 441. 401. 00. 409. 001 HONS 0 1 8 3 2 5 Tyl*r, . o. * ii-1* mi;,, Vi.r^,. *S2;sn'ism-jr snsm-"*' "7V MWMi lMttwXitM,. -I-1 taelMl. (mim. CM* MMti 0*1. im, |)4 . <1.; OamtM, a. imiw if ill, mumm fiMM<pi mT^,In.'S *t**y"*";,, ^SS'^Tm^S*-*4 CMP Mt: IU, |}| o o4.ji. TIOMOMt. IMII. - --*** 10 W.r I7QH0QI4 *"* ^ HfllHaw CAM In MMt fcMtni !Tir""y '*w4 ** * MUm. (Min MM.Mil. taieTST. CMO unt: Ml. <U. MI. Ml. Ml. <4* mmvn WMM II M. - (lIMMMOa MMTMM ar Miaumm mauiM Mm - . Mttcfifi. . 9M0HIS SN Mil Cs=,ssr:.,.rw,ci- Mn 107S "" i..,,^,. rn>1m30*i0ci IOvMOM. rKlMTMKtlJIiMa l MUIC MUHIN* M Links. . |.{ luitarwiu, j, ; fUnlMulii ____- MM* s# wr*. fim * , t. CMO AUNT: 44*. 001. 004 -smt --**+*?*__ 10 mo.- ci74<o*4iaa SZSZVc'Z.Z TMjjirmimii* or ou.rn.iu Km.iM. I.sn2^. SZZ.W --. *~^.I . ** fcliwy (Ml, W Mpr # y JJ n J 1074 p lOO-ltg COMM -------OKKOIOIOMS; 0CC4MMB4AHT. 7IWIIS, CMCMICMt^MSIlCIOCS lOCNIIMItS: CML0OIN4TI0 HTOOOCMOONS Cl* 471. 004 , 003, It) -****" *0 MO - 11741000070 S5n?*" TM"or"' 9 .iouM.iiHDiit. m me mm M^**#7i CMra t.{ StslflMsusr. VII Mm o ****** **! Emilio Inst. Nan HONS 0 1 8 3 2 6 srtts. flAI, . T*r* *Mf Om iso < ouo iNssltM, lAInjutu'Mu, 4 environ HIIm v n 4 m OtlCOIOfOiO: CNVIMMCNV4L f *4|0 OOLUfMON |N*IH(C|M0. O IH-H4 COPCM fWOM #. (OCMICMS. VSSlSIlyJ CM* MIIT: 4*1, 000. 0I CMO A1I0T: 443. 4|,`o04 HI. INMCflCIOC*. nuninm: mvotMimm umiwis CMO UIII: 499. Ml. MM IMI < o MWiiMitf; 4(*MWirf<t tprmM*tiImMm. mws. min wimis. hwmi, IPCNTIPIC49: MPHWU CMO MOOT: 440. 4CM __ oiiratiM), caniM 10 NO.* CITS1010400 407441 - (17419*0449 MCUC NO ItPMWl <4C0> iwnnwin m now 0m. Cralf *,i Mil, OarlM |. CmmIIm VHfllla Sarvtca. OIIm. Ont < Me. Olv oatar. air ana wit* Om, prapr * 1} It 1 9ap far Mm lug 94-taP I 1079 p 90 C00CN: ICWW OiOCOlPfOOO: (*047(4 POLLUTION. Control). 40417*1*. cnra--fprapnic). gnowaToapapwic IMMCVICIOC*. Mlflu. (CMCNICAL AN4L7SIS. IMNTIfltt*: fOOB CHAIN*. POL7CML04IMAT(0 IIPMNfll C440 Ait*7 : 4*9. 401. 004 mm. 0. 0.; mman. o. 4.) NrrIM. P. 0. 4. 4.: CMlM. N. 0.; ClfMl I li. 0rf Mattana I 4o CNh |M, Dtv Mtar. Mp V4 Oaata Om,, Prapr v IS n 1 Pap far Mtt Pup 90-Sap I *079 p *04*144 CO*MM: 4CWC4U OtSCOtPTOP*: <OIOM9ICAL (NOIMfOINO. Living ItMlMl. PtSTICIOC*. Mins. I lOCNVIfICM: POLVOCOO(M4TC0 IIMNYIS g CMO 4if0f: 441. 004 900707 10 NO.- (1791910740 Sooarpran. 4.; Svanaaan. ).; uifttrap, *. Oipartaant af 4ntaal tcolapy, Lund. Suad Knvlran Pallwt v 9 n t oan 1479 p 90-94 C00CN: MSC4IPI04*: *04714 P0LLU7I0N. INSCCTICIDC*. (NVP4f 114*1*74141 CMO 4LK47; 499 . 909 . 914 10 (1791910470 ioiotoo chc ounmoTMN or rim mwny top pco OtPlIlnp. Oavld L. f tan-Paattalaa aaa Lao. Calunoia. no 4a Chao fad. Olv Oatar, 4tr and Paata Om, Prapr v 19 n 9 rap far Oaat 4up 9t-ap t IP79 p 79 cooco: acocau 0I9C0IP700S: (*ONNICAL 4M4L7SI0. SpactraM'Mfttc). PtSTICIOC*. (047(0 POLLUTION. Central). PfCTOOSCOP|C AM4LMIS pHtnoLf. lOCNTIf 1(49: POLTOCOPIMATCO 4IPMCNVLS C440 4LI4T: 409. 001. 404 900710 IO NO.- (1791914791 POLTOCONM4TCO OIPMOTTLS: IPMCT OP LNN0-T(4H M m rim.Airaod activity pkncpnalcs pooncus. Nett. P. Paaaian. 0.; rap. M. n. ; Cuthoap. i. k Honaywalt Paa Cant. Mopatna. aim Dull (nvlran Cantaa Taatcal v 7 n 9-3 fap-Nar ia79 COO(N: MCTM 0CSC4IPT049: *04714 POLLUTION. H9UIT4UI POISON*. IOfNT If IC4S; POLVOMOOQOtPtNNTL* CMO 4L(47: 499. 914 HONS 0 1 8 3 2 ? 1179*910404 LWmMTW OtPMONVLS MBMJMT M W1LO i o!; lp*tM.'Alolraii; Caariek. Per*e Sawtn Oafcata Otata univ. Oraafeinpa 4m Own Oaa. It* aatar. air and Oaata Om, Prapr 19 n 9 Pap far oaat aup *0-0ap 1 *079 p 0i-00 CootN. acocau MtCOlPIOOO: *IN0(CriCI0C(. 1041(4 POLLUTION. Can!rat). < ONNIC4L AM4LV9II. CNeMMrantt). Cl MONA1411WUC 40417*19. HOMS 018328 tot I tow toritit* I Ml Mill NLVOUilWflMVlIlMN s m iimw I 0 UNt 4 twinit aoinrmnwiTviiN mm dwcimmnw - 4910 4TT9WM4THW 9 41719 4 MIIM9I VNI 10 41999 9999 11 9 NMN Ortot 11/3/1*9 fiTift 71--: 9.099 Ortot*: 9 OMet.i APPLIC; TNfOOCTICAL nt TypA: JOUONAL PAPft (tp total OAACrlAtrt: NCOICAL CONPUTINO; CONPLKTK COPUKI fOCPANI lAwlllMwc DATA ANALTSIS; POOOOAMMOLf CNVIOOMCNTAL POLLUTANTS; CCLLULAA TO1IC0L06V Cltea Co--: C7990 CALCULATOR; (91 Nft) 494930 A900794A7. 000049P90 pco wpm. PLA9NA ANC PTNBLmS SNOWS POONItt POO NIC f iNMtlMart: BHINWMNINl CMMMMMI; _ .. MMUM N*HU MIK 9UALITT tlWPl HTIMV M9SN; tuttvu IQUliSMIMi MIRICi KNIMHTMT HCMNIITIT ST90Y; U: 2N; Pit MS; LOCAL MILS; LANS ONVA9IO OCCfWT SCDINCNTS; CO 5 t Mis CO; SILISt CUfli WOCIOfB SCOIMNT SMHIi KMCOIOAN COCIK; P.O/SUP I/-000; P.P/SUP I/-000, P.P/SUP 1/-OOT J HWI*OLOOIM| Nit MOM; MCOt SCOIMNTS POLLUTIONS Ml| POLLUTION; CANNON; TOACC OCTALL OfOCMHICAL OISTNIOUTION; AO WTO 00 TO TO) OtOCMmiCAL OAT A PACT00 ANALYSIS; AO *000 TO TOTOt SOIMMT OKPOSITION OATIS; 00PANIC C CQNCfNTNATlONS Clan cm: A00T0C; AOOTOCs AO340N; A93400; A0930H; A99400 OAOTON. T.O.; A4KKNAULT. O P.; 000SON. 9.1.; N000T. J O. CIUIL MONO. 0<PT. . OOTAL NILITAOV. COLL. KINGSTON, CANAOA CMS. J. (CANADA) VOL.09. NO. 40-1 PCO. '990 CotefV IrHtaant: APPilC; IlPCOINiNrAL OaeiAMI Typp; JOUONAL PAPfO (4 OoPa) Oaacrlptora: WASTC DISPOSAL; OOGANIC CONPOIM; PV90LVSIS: PLASMA DCVICCS I tent t flAPA: POLVCHUMINATCO OIPNUfTLS; PLASM* Me PVOOLTSIS i PCO WASTKS OISPOSU Cloaa Cotea: A0990L; 4097SH; 009SO; 00(00 I g 410700 000004470 1 009000 AO 1001091. 09*0940*9 mjmmmm nonommn w dm woo oono ocmaoi. J.; sum. s. --SOAP CMCCTIONS (COMOM MSI. TIC MPN tCSSION OP NOISC IN PtfOtN C0MCC7I0NS ILOOXC PCO COMCCTIONS) MANAN. O.; OC LA LLOSA. 9.0. SOCOL OP SNVIOOMCNTAl SCI -. JAWAMAOLAL NfMMJ UNIV.. NOW UNIV. AWTONONA OC NAOOIO. MAOOIO. SPAIN OCLMI. INDIA WOOD CLCCT90N (SPAIN) NO.99 M9-73 APNIL 1900 ULTOASONICS () VOL. tO. NO.9 07-90 OAOCN 1901 Caten: OUCLCN Cate: WLT0A9 Traataant: PRACTICAL APPLIC; CAPCKINCNTAL TPtettMflt: CXPCOINKNTAL OoeuteMI Tyco: JOUONAL PAPfO (40 oeo/**** 'mmm` LlMMaM* UIMI4 PtePlftte: 0I0M0ICAL ULTOASONICS; ULT9ASONIC P00PA0ATI0N; OONK loansMpA: OIN VIVOP 00M; COUPLKO TOINWOCKO; LIAO 21000NATK TITANATC; PCO-O; STAINLCSS STIU CLKCIOOOCS: ULTOASOUM VCLOCITT) ATTCNMTION CONSTANT; MPLICTC0 POWCO; Omertotors: OUSOAOS; POINTCO CIACUMS ItenltPlara: PfCOCO CONNCCTIONS; TOANSNISSION LINC; CONNON IMS COOMCJNS; PAOASITIC NOISCS; IOTAI ATflNUATION; OUSOAOSLOOK PCO INTCOCOWNCVION Ctaaa Cam.- 033100 OIONKOICAL ULTOASONICS CI999 CMC A4900; A07OOO; 070MO; 07090 HONS 0 1 8 3 2 9 OAOOCTT. M.f.l STACK. M.f. NCALIH IPPICTS OtSlAOCN PAOGAAM. MMINM7 fCAVICCS MS IOIANOLC PAM. NC. USA COPPUT. OlOL. ANO 0(0. (001 VOL. to. HO 3 *3-4? INC-. 1990 MM1 IIWWM mapimMMC IR0V V W MHN-INIMnc MMI WWIItWI fMOHT. V.; NMTWn, P. IIMaMMM&ciaM MICIMIM. WIV. LWat-MITM. 4, pwi. (rum) m.o. .i TN-tr mm. nn MW: MIM TrwtuM: (WMIUMn tMHMM Tyu: MMIl MMI ( M) liwr I|Um> MtHMC WPMMi tlDIW COVSTM MM lUWMMflMl IKfMMMC MIKItfi HUMMNIC UMUflON; mmiic uouio cmmi lMrtlf<an: PM; MIWflMIIUi MMfIC ISOTOOPK MUM IMMITlPl U mKITIi IM HWMIWI CIM CMm: M41t MMOl MI9H rTMCwtl PMCTtCM. imiC Oatwant Tip*: MMI MMI T IM-I JUT INI % PlWpUfi: H|M*M|| rilTIMi rCLCVISIOM MCCIVtll lUMIflan: IMF TV MCCIVCM; KLlVISIOM INTIMCMMCC mint mm pa nuu ClftM CMn: I IfTO; 004*00 JULT nn no mil CUCTOIC C0NMCT00S liriin: to UCM UI0C MUCKS; MUfK STSTINS; ti 00TN lOtOOOIM; SMIW CMT0CT ITIIM; COIMCO VIM KCTIOMl ILCCTOICM. CPMCTOMi PCI HUUMi VIM WtPPID MMCTIOMl PlIWH CDtWSCTSON SIOMAi ATflPOMMOM CltM UM: 01I00C HONS 0 1 8 3 3 0 Sat Itaaa lawipttaw mi o pci M.younMrMliPKN s m ifion s i iMea 4 9990 IBMUSf 194 MsvaueTin i49i onenrMTiM 1 (IN 4TTMMTIII 4999 IMWT1I S91M llllllf | I S9M4 Ml It 9 I4MM trlrt t1/9/t-9 Karan tim: 0.099 Frtnta: 9 law.; 9 s1 HONS 0 1 8 3 3 1 WISI/MAMWMKUM/t WMfV MWWr//MT9MI /)WV1MwMiIoNaIIN SWIM MN ^MMM SCI.mMMil WVWWtt IW//5W wmw Wicu in s rtmi i4 atr UNIV MriROl.MlfM MiriRM CT0 CHM/MllliM MK M1/OWTMI0/C4MMU/ M4 MflCll OATS wi f PCS JIM NBUQUHN MINI S| tlNvwxw . SCIlMCt Of tMg TOTAL CMVIOOMKNT . f0. Nl. SToShdu^/WIKIi/* **" P#U'<T 1,1 ,W* 400 H-M, 1070 I 7tOAO/S-*O09f HONS 0 1 8 3 3 2 to* its-- Psssrlpil-- 1 MUOURINITMVIIIMN a liftoff 9 ftffff* 4 N IlffMf * 4 MST--Ctl-- T 9 ftTTt--STIPN aiMffTIM ft IftlfftO Print 1/9/I" iMran ti--i o.toi Prints: HONS 0 1 8 3 3 3 MM SI* (ItCCTflWfC tlMftllS MI'N) VI MUM (MO) M VMM I fM (CLICTMMC IMRISTIIfS MS'NI TV HMUSN ASTM (MUCIN SOCICtt M TCSTINQ MB MTMIM.S) Mac CMfCttkAMCUl) V (MUSH *W (MBIICMI lOCICTV VM VISTINI MB MTCRIM.S) ISC (HCIUMOHI) TV fMCLISH IMMU - MBI (MPMIBM MFfMMI (MMCCTMt. ISCCTMCM.) ) wrm HONS 0 1 8 3 3 4 Feasibility Study of Chemioal Detoxification of Polychlorinated Biphenyl Capacitors Phase I Study Ktwordt: . Fotychlorinaito Bipnanyi* Capacitor* Dachlorlnatlon Waata Diipoaai 'AMfttTJyatti TtcnnoiogifajK, MountMVVMw.'California EPRI EWl CS-2477 ffOjact 1283-7 ^inai Raoon Juna 1982 ELECTRIC POWER RESEARCH INSTITUTE HONS 018248 Feasibility Study of Chemical Detoxification of Polychlorinated Biphenyl Capacitors Phase I Study CS-2477 Research Project 1263-7 Final Report. June 1982 Preoared By ACUREX WASTE TECHNOLOGIES. INC. 485 Clyde Avenue Mountain View. California 94042 Principal Investigators G. J Mnlle L. Weitzman Prepared lor Electric Power Research Institute 3412 HUIview Avenue Palo Alto. California 94304 EPRI Project Manager R. Komai Heat. Waste, and Water Management Program Coal Combustion Systems Division HONS 018299 ABSTRACT Chemical detoxification of polychlorinated biphenyl (PCB) using sodium metal reduction Is emerging as a significant new method of destroying PCB liquids. This report presents the results of a preliminary study on chemical detoxification as It applys to PCB's In capacitors. The results of the first phase of a two-phase study are presented to evaluate the possibility of chemical processing of PCB capacitors. The tasks are broken down within each phase as follows: Phase 1 e Literature search e Acquisition of EPA permits for PCB research e Evaluation of the legal and regulatory requirements of this process e Design specialized equipment for handling PCB capacitors In the laboratory e Design Phase II research program Phase II e Construct laboratory housings e Develop safe methods for opening PCB capacitors during processing e Develop method for safe disposal or decontamination of capacitor shell e Develop method for destruction of PCB's In capacitor core e Determine cost of this treatment and design a demonstration program The results of the first-phase program were very encouraging. Based on available Information, It appears possible to chemically destroy PCB's In capacitors. This report Identifies questions that must be answered by the Phase 11 (laboratory) program before the feasibility of such an operation can be determined. Finally, this report describes a research program that must be followed to answer the previously mentioned questions, and to develop the design data for a full-scale capacitor treatment system. Ill HONS 018250 EPRI PERSPECTIVE PROJECT DESCRIPTION Th electric utility Industry Is faced with the task of removing and disposing of polychlorinated biphenyl (PCS) capacitors. Removal can b achieved either by removing failed capacitors or by utilizing some form of accelerated phase-out. The only disposal options at this writing are storage by the utility or destruction at the sole incinerator certified for capacitors, the ENSCO facility in El Dorado, Arkansas. This project pursues chemical destruction of capacitor PC8$ to provide another option for the Industry's 2.8 million capacitors. This final report siaamarlzes the results of Phase l of a two-phase study (RP1263-7) to examine the feasibility of a chemical disposal option for PCB equipment. Pre viously published reports on PC8s (EPRI Final Reports FP-1207, Volumes 1 through 4) delineate the scope of the problem and of potential disposal options (Volisae 1), provide guidance for the development of spill plans (Volumes 2 and 3). and document EPRI participation In the sampling and analysis during the ENSCO Incinerator test burn (Volume 4). PROJECT OBJECTIVES The overall objectives of the study are to further develop existing technology for . treating dilute PCBs In mineral oil and to extend the technology to the treatment of high-concantratlon PCBs In capacitors. The first-phase objective, reported here, was to Investigate and determine the legal and regulatory requirements for the second-phase experimental work and the eventual coamercltl process. PROJECT RESULTS The proposed process for treatment of PCB capacitors Is based upon sodium chemistry, l.e., a reactive organo-sodlua compound dechlorlnates the PCBs. Phase I of this study Investigated the literature for Information on capacitor handling and treat ment of PCBs; Identified, applied for, and received the permits required to pursue PCB-destructton research; solicited guidelines on the degree of PCB destruction HONS 018251 required of the treatment process; and developed the test plan to be pursued In Phase II. Phase I results support the continuation of the project Into Phase II. The chemical treatment process will be deemed acceptable If no detectable PCB Is found in the chemically treated waste. The method of analysis to be used Is gas chromatography with an electron capture detector, and the EPA considers the limit of detection to be In the 1 to 2 ppm range. The primary approach of Phase II will be to test whether It Is possible to destroy the PCBs In the capacitor without first laachlng them out of the cellulose matrix. . This report Is Intended to provide a suanary of this planned chemical treatment option to uttllty personnel involved with PCB capacitor disposal. The report also provides a description and explanation of the federal requirements for alternatives to Incineration; the explanation may prove useful In the evaluation of other PCBdestruction technologies. Phase 11 Is already under way. The scheduled completion of the project Is the end of 1962. Ralph r. Komal, Project Manager Coal Combustion Systems Otvlslon HONS 018252 vl ACKNOWLEDGMENTS The author gratefully acknowledges the help provided him by Mr. Earl Story and members of his staff at the Cincinnati Gas and Electric Company. The Information they provided on the structure and methods or handling of capacitors proved Invaluable to the design of the equipment and procedures for the Phase I and II study. vll MOWS 018253 CONTENTS Section 1 INTRODUCTION.......................................................................................................... 1.1 Chemical PCS Destruction Method ............................................ 1.2 PCS Capacitor Structure and Handling ............................. 1.3 Advantages of Chemical Destruction .................................. 1.3.1 Exposure of New People to a Perceived Risk . 1.3.2 Verification of Destruction .................................. 1.3.3 Dispersion of Pollutants ............................................ 2 LEGAL ANO REGULATORY REQUIREMENTS .......................................................... 2.1 Requirements for Research .......................................................... 3 LITERATURE SEARCH................................................................................................. 3.1 Computer Literature Search ..................................................... 3.2 Other Literature Searches .......................................................... 4 CAPACITOR PROCESSING....................................................................................... 4.1 Piercing and Opening .................................................................... 4.2 Leaching and Rinsing .................................................................... 4.3 In Situ PCI Destruction .............................................................................. 5 PHASE II PROGRAM PLAN....................................................................................... 5.1 Laboratory Description............................................................... 5.2 Construction of Containment Housings ............................. 5.3 Capacitor Perforation and Shredding .................................. 5.4 Shell Decontamination.................................................................... ' 5.5 Coro Decontamination .................................................................... 5.5.1 Direct PCI Destruction ................................................ 5.5.2 Leach and Process Route ............................................ 5.6 Design Demonstration Program................................................. 6 CONCLUSIONS ............................................................................................................... APPENDIX A RESULTS OP COMPUTER LITERATURE SEARCH................... Page 1-1 1-3 1-4 1-7 1-8 1-g 1-9 2-1 2-4 3-1 3-1 3-2 4-1 4-1 4-2 4-5 5-1 5-1 5-2 5-6 5-7 5-8 5-9 5-9 5-10 5-1 A-l HONS 018254 SUMMARY The disposal of capacitors containing polychlorinated biphenyl (PCS) dielectric fluid Is a Major problem for the electric utility Industry. With the start of operation of the Energy System Corporation (ENSCO) Incinerator In El Dorado, Arkansas, the Environmental Protection Agency (EPA) ruled that sufficient capacity for PCB disposal was available and PCB capacitor landfilling Mould no longer be allowed. The utility Industry has been skeptical that only one facility can handle all of the waste capacitors produced, hence alternative technologies must be evaluated and developed. Recently chemical detoxification of PCB using sodium metal reduction has emerged as a significant method of treating liquid PCB. This approach has the advantage of mobility. It can be taken to the PCB's so that siting problem are eliminated and transport cost reduced. The process results In very l<w emissions, effluents and waste production. Furthermore, the costs of this treatment is usually less than Incineration. This report presents the results of a preliminary study showing that this type of treatment my be applicable to PCB capacitors as well. It presents the results of the first of a two-phase study to evaluate the feasibility of chemical processing of PCB capacitors. The tasks In each of the two phases are: Phase 1 1. Literature search 2. Acquisition of EPA permits for PCB research 3. Evaluation of legal and regulatory requirements of such a process 4. Design of specialized equipment for handling PCB capacitors In the laboratory 5. Based on tht results of 1 and 3 above design the Phase It research program HONS 018255 S-l Phase II 1. Construct laboratory housings for handling capacitors 2. Develop safe methods for opening PCS capacitors during processing 3. Develop method for safe disposal or decontamination of capacitor shell a. Oevelop method(s) for the destruction of the PCS's In the capacitor core ' S. Determine the cost of such a treatment and design a demonstration program The results of this first-phase program were very encouraging. They showed that there appears to be no theoretical reason why PCS's In capacitors cannot be destroyed by chemical means. A program was developed to obtain the cost of data needed In order to design and determine the cost of the process. The preliminary program Identified the following potential problems associated with the chemical processing of capacitors: e 6as buildup In capacitors could result In the release of PCS's upon opening for treatment. e Hmower mills are the standard method for breaking up capacitors prior to Incineration. They create a PCB-contamlnated dust problem which (s difficult to control In a chemical system. Alternative methods for opening the cases must be used. Wet grinding, and sheering will be the mein size reduction methods that will be looked at. In addition, the minimum amount of size reduction that Is needed for chemical processing will be determined. e Sased on theoretical studies It appears paper may Inhibit or slow down chemical destruction of PCS's. The Phase 11 research program will examine the degree of Inhibition and If it proves to be unacceptable evaluate several methods of separating the PCS from the solids. e The PCS-contemlnated casing must be disposed of. The Phase II program will evaluate several methods of decontaminating the casing Including a combined casing/core detoxification scheme and compere their efficiency and cost with simply filling the drained case with absorbent and disposing of It In a landfill. HONS 018256 S-2 This report describes > research program tdilch will obtain the needed data for the design of a full-scale capacitor treatment demonstration unit. The Phase II progrn, has the following elements: e Safe perforation of the capacitor shell and removal of the core e Decontamination of the shell e Decontamination of the PCB contaminated core and free PCB liquid. This can be accomplished by leaching PCB's from the core material using some form of solvent washing technique followed by chemical treatment of the PCB-contamlnated solid or possibly the In-sltu treatment of the mixed paper, metal and PCB's. HONS 018257 S-3 SECTION 1 INTRODUCTION The disposal of capacitors containing polychlorinated biphenyl (PCB) dielectric fluids Is a major problem for the electric utility Industry. Before March 1, 1981. the Environmental Protection Agency (EPA) had permitted their disposal In chmlcal vasta landfills. However, with the start of operation of the Energy Systems Corporation (ENSCO) Incinerator in El Dorado, Arkansas, EPA ruled that sufficient capacity for the disposal of these capacitors was available and landfilling would no longer be permitted. Subsequently that utility Industry has been skeptical that one facility has sufficient capacity to destroy all of Its PCB capacitors. Aside from the Rollins facility In Texas, It Is unlikely that additional Incineration capacity will become available In the foreseeable future, hence, alternative technologies must be evaluated and developed. In the past few months a technology utilising the tetrahydrofuran/naphthalene complex of sodium metal has emerged as a promising approach for the destruction of PCB liquids and PCS-contamlnated dielectric fluids. Several companies. Including Acurex Corporation, have applied for and received permits to chemically treat these liquid PCB materials. In addition, two companies have begun to accept PCB capacitors for processing. It Is, however, unclear from available Information whether these actually destroy the PCI or only extract It, leaving a PCI-free solid residue and concentrated PCB liquid, which must be disposed of by other means. Finally, a mmfcer of companies currently accept capacitors for storage under approved conditions. Some of these guarantee their destruction at some future date. As options like these become available to the electric utility Industry, It Is Important that the facts are presented mid evaluated to that each company can handle Its capacitors as efficiently as possible. This report presents the results of the first Phase of a two-Phase study to evaluate the feasibility of chemical processing of capacitors. The two Phases have the following objectives: MONS 018258 1-1 Phase 1 Perform limited literature search to ensure that the latest technology Is Included In this program Acquire the necessary EPA and other permits for laboratory-scale research on PCB's a Evaluate the legal and regulatory requirements necessary for this type of process e Determine the best design for containment housings to handle the PCI capacitors Phase II e Construct the PCI containment housing In the laboratory a Determine a safe method of perforating the capacitor shell to avoid worker and workplace contamination with PCI e Determine whether rinsing Is adequate for shell decontamination or If other decontamination procedures are needed a Evaluate several potential methods for destroying PCI's In the capacitor core, both free liquid and that absorbed by the core material a If these tasks are successful, determine the approximate cost of this trestmant, Including design mid coat of a demonstration program a Prepare final report This preliminary study Is Intended to establish: a If there is any Information available In the scientific literature which could be useful In evaluating the available PCI capacitor cleanup processes or for development of new ones. For reasons discussed later In this report, the emphasis Is placad on chemical destruction of PCI's. a Types of legal and regulatory requlraaents this process must comply with a Types of containment and handling equipment which will be required to properly protect workers and plant sites whan processing PCI-contalnIng capacitors In the field. This will Include specifications for their design. In addition, the results of this study have shown that further work, especially on chemical destruction would be useful to encourage the development of Improved processes for the destruction of PCI capacitors. This report also describes the work plan for such further work, and the types of permits this research requires. HONS 018259 1-2 Mfort presenting the results of this prelIninary study, it Is worthwhile to describe the basic chenlcal PCD destruction process In use today. 1.1 CHEMICAL PCS DESTRUCTION HETHOO The chenlcal method used to destroy PCB's Is well established and, theoretically, Simple. It Is well known that sodium can. In the presence of naphthalene and tetrdiydrofuran, dechlorlnate organic molecules such as PCB's. Work has been done In this area by several Investtgators since 1936, (J_, 2, and 2). The procedure works as follows: a Prepare a sodium reagent by mixing sodium metal with the proper amounts of naphthalene and tetrahydrofuran. This must be done under nitrogen, as air and water will react rapidly with sodium and deactivate the reagent. The reagent Is referred to as sodliaa naphthallde and Is represented In this report by the syaihol Na*. a The reagent Is added to the PCB-contamlnated material (or pure PCS) and the PCS destruction reaction Is permitted to occur. This Is a very critical step, as the dechlorination reaction Is highly exothermic. If cooling or dilution Is not provided, the reaction can become violent. t After the reaction has taken place, the excess sodium Is quenched with water, converting It to sodium hydroxide. PCI's are destroyed via a reaction of the sodium naphthallde radical anion (Na*) with the organic chlorine. The reaction proceeds In steps, one chlorine removed at a time. The products are sodium chloride and a complex mixture of nonchlorinated pplyphenyls, as well as the sodium hydroxide formed during the quenching of the excess sodium with water. The chemical reactions are Illustrated In simplified fora below: ClaHj(BP) 2Na---CljHs(BP)Na* NaCl Cl3Hj(BP)Na* HjO--~Cl3H7(BP) NaOH or 2 Cl3H6(BP)Na------ -C13HS(IP) - (BP)Cl3H6 2 Na* These reactions Illustrate what happens to a tetraehloroblphanyl. Identified here at CI^HgllP). The term (IP) refers to the biphenyl structure. As shown, the product Is either a trlchloroblphenyl or a dimer of two chloroblphenyls. The sodium will continue to remove chlorine from these compounds until the nonchlorlnated form Is reached. At this point, the PCI molecule ceases to exist from both a legal and technical point of view. With proper design of the system. It Is possible to achieve essentially complete destruction of the PCI, at least to the limit of measurement EPA considers this to be 2 ppm. 1-3 HONS 0X8260 The baste process described above suffers from a number of drawbacks. The most significant Is that naphthalene Is classified as a "priority pollutant* under the Clean Water Act. Furthermore. Its presence In any residue formed by the process could subject the residue to disposal limitations under the Resource Conservation and Recovery Act (RCRA). There are a number of chemicals available to replace naphthalene In this process. Since these variations are, however, considered proprietary, the subsequent discussion will focus on the use of naphthalene. There appear to be no theoretical reasons why such chemical treatments cannot be used to decontaminate PCB capacitors. There are, however, many problems encountered in the actual handling of these solids. These problems. If not properly dealt with, can cause PCB contamination over wide areas, and utilities are not necessarily absolved of liability upon turning the capacitors over to a second party for disposal. Therefore, It Is Important that these Issues and their solutions be clearly stated and understood. 1.2 PCB CAPACITOR STRUCTURE AND HANDLING Capacitors are relatively simple electrical devices. They are usuelly rectangular, completely sealed metal containers with two procelaln-lnsulated electrical connectors on the top. Ftgure 1-1 shows a bank of capacitors In a typical configuration. The Interior of such a capacitor contains layers of conductor foil, typically aluminum, separated by plastic film or paper, these are rolled Into a tight mats which occupies almost all of the capacitor's Interior. A schematic view Is shown In Figure 1-2. To Improve the dielectric characteristics, provide cooling, and exclude air, these capacitors are filled ixtder vacuum with pure PCB's. All solids Inside the capacitor are completely saturated with PCB. In order to destroy the PCB's, It Is necessary to open the capacitor. Physically, opening the capacitor does not present a great difficulty; however, the capacitors occasionally accumulate small amounts of gas Inside the core during normal use. This gas Is under a slight, (although unknown) pressure and can cause free PCB liquid to spatter or spray out of the capacitor idien It Is punctured er ruptured. Therefore, It Is necessary to pierce these capacitors In an enclosure to prevent contamination of workers and workplace. Incinerators cope with this problem by using a hawser mill to shred the whole capacitor prior to burning. This Is not possible whan using a chemical process, as there Is no flame to vent the hanaer mill dust. Equipment for piercing and opening the capacitors safely In the laboratory has been designed and Is described In Section A. The Phase It program will Include (among other Items) the design of a potential commercial-scale unit. l- MOWS 018261 Fljurt 1-1. Photograph of a Typical Powar Capacitor Bank 1-5 HONS 018262 i. Capacitor shell b. Porcelitn bushing c. Fill hole for dielectric fluid d. Cepecltor peck e. Electrodes f. Insulating file (paper or plastic) g. Muelnun foil Figure 1-2. Detail of a Typical Power Capacitor 1-6 HONS 016263 Power capacitors are sized by KVAR (Kilovolt-Ampere-Reactance) end kV (kilovolt). Thti study util deal exclusively with power cap* cl tors ranging In size froei about 2S KVAR, 2,400V to about 4SO KVAR, 7,200V. Specifying these two factors specifies the capacitor. It should further be noted that the results froei this study should be applicable to most PCB capacitors. The size range was chosen largely because it represents the typical nix of capacitors employed by a utility. The PCB content of these capacitors Is a function of their size, manufacturer, and the year they were made. The Cincinnati Gas and Electric Company (CGtE) polled their capacitor suppliers to determine the amount of PCB's used. They examined capacitors ranging from 15 KVAR, and voltage applications of 2,400 to 7,200V. These capacitors were manufactured from 1950 to 197S and Included those manufactured by General Electric, Westlnghouse, and McGrow Edison. The results for a given application, and year of manufacture, the PCB content was relatively constant regardless of the manufacturer. In addition, there was a steady reduction In the PCB content of the capacitors over the years. This reduction appears to be on the order of a factor of two and Is noticeable throughout this time period - even before PCB's were of environmental concern. The PCS content ranged from a low of 0.5 gal (1.9t) to a high of 10.1 gal (38.21) PCB per capacitor. The majority of the units were found to contain a total of between about 2 and 4 gal (7.6 and 15.11) PCB. On the basis of these capacitors, the chemical detoxification breaks down Into the following steps: 1. Safe perforation of the capacitor shell and removal of the core 2. Decontamination of the shell 3. Decontamination of the PCB-contamlnated core arid free PCB liquid. This can be accomplished by leaching PCB's from the core material using tame form of solvent washing, followed by chemical treatment . of the PCS-centamlnated solid or possibly In situ treatment of the mixed paper, metal, and PCB's. 1.3 ADVANTAGES OF CHEMICAL DESTRUCTION A review of current literature on the subject shows there are many technologies capable of destroying PCB's (4). Some examples of these are: a Combustion technologies -- Liquid Injection Incinerators -- Rotary kiln Incinerators 1-7 MOMS 018264 -- High efficiency boilers (for 50 to 500 ppm PCB's) -- Cement kilns -- Fluidized bed Incinerator -- Molten salt incinerator -- Pyrolysis -- Ocean-based Incineration e Chemical technologies -- Chemical oxidation -- Chemical dechlorination e Emerging technologies -- Microwave plasma destruction In spite of these options, there Is a shortage of disposal capacity In the United States, This Is due to the fact that the restriction on PCS disposal facilities is not technical, but social. Simply put. It Is very difficult to site a facility handling PCB's. As a result, It Is essential that any technology employed overcome objections to Its emplacement. The objections raised to such facilities and the attributes that the technology must have to overcome these objections are described In the following paragraphs. 1.3.1 Exposure of New People to a Perceived Bisk ' This has been the most difficult problem to overcome. Basically, people perceive an Increased risk from PCB disposal facilities and object to their placement In their neighborhood. Even If the people are convinced that the facility will destroy PCB's completely, they object to "the danger of shipping PCB's through their neighborhood.* The problem bolls down to the statement "Haste disposal facilities are needed and a good Idea but not near where I live.* It might be added that people five more miles from a proposed facility have been known to abject because they feel It Is too close to them. Even when existing Industrial facilities (l.e., cement kilns, boilers, etc.) have been Involved, there has been tremendous local citizen and government opposition. A direct result of this opinion Is a concern for a decrease In the property values. After all, a perceived risk does make this property less deslreble. The ideal PCB destruction technology It one which Is capable of being moved or located at tha site where the PCI wastes are being stored. 1-8 HONS 018265 1.3.2 Verification of Destruction This problem Is best summarized by the stetement "We're sure you cm destroy PCB's during the test when all these scientists and engineers are running the process, but hew can we be sure you will destroy then during operation? We all know that breakdowns occur." In addition, there are the problem associated with hazardous products of combustion, materials such as chlorodlbenzofurans and chlorodloalns which form, or are suspected of forming, when PCB's are burned. Combustion Is largely an uncontrolled chemical process. As a result, almost any organic material can conceivably be formed. While such an extreme concern seem unwarranted. It must, nevertheless, be considered In the selection of a technology. The technology of choice should utilize well understood and controllable destruction methods. Furthermore, It should operate In a batch mode, making It possible to chemically analyze the outflows prior to release or discharge. 1.3.3 Dispersion of Pollutants Gaseous emissions are released from some sort of stack which Is often associated with heavy volumes of noxious smoke. This contributes to making people who live miles from the facility fearful of It. In order to overcome these concerns, the Ideal PCS destruction technology should have no gaseous emissions, and only small volumes of aqueous effluent. It Is recognized that no technology Is capable of managing all forms of PCB's and whlla satisfying successful Implementation criteria. However, as the following discussions will show, there are certain technologies which, for specific Important applications, come very close to meeting the Ideal criteria. Chemical treatment Is the only method currently available which can overcome the previously mentioned problems. As a liquid Phase system. It Is very compact and can be readily made mobile. In this way. It can be taken onsite. Instead of transporting PCB's to a new location. Furthermore, unlike combustion systems. It produces essentially no emissions or smoke and only small amounts of solid waste or aqueous discharges. Finally, the liquid Phase reaction Is readily controlled, and It Is possible to analyse each batch of material treated for PCS prior to discharge. In this way. It can be assured that the PCB's are destroyed mid none Inadvertantly discharged. HONS 018266 1-9 SECTION 2 LEGAL AND REGULATORY REQUIREMENTS TIM bulk of th pertinent PCB regulations thet apply to a facility for destroying PCI's In capacitors are given In the Federal Register of May 31, 197} (5). The background document (6) for these regulations Is also an Important source of Information on PCB handling and disposal methods. According to these regulations, the only presently acceptable method for disposal of PCB capacitors Is Incineration In i "Annex I" Incinerator. The name comes from the fact that the specifications for PCI Incinerators are given In "Annex I* of these regulations. The EPA Regional Afenlstrators are given the authority to a lion alternative methods of disposal If they are essentially equivalent In destruction, and not present a hazard to health aid the environment. Chemical destruction of PCI's Is being approved via this discretionary authority of the administrator of each of the ten EPA regions. To date, chemical treatment has only been approved for transformer oils containing up to 1.000 ppm PCB. As a result, the required degree of destruction and conditions Imposed on such permits trill have a direct Impact on the environmental requirements for a capacitor treatment system. Incinerators have bean shoun to result In PCB destruction In excess of 99.9999 percent. Therefore, to shorn similar destruction levels, the product oil from a met chemical process woul have to contain less than 1 ppm PCB at a 100 percent PCB Input. The sensitivity of the currently available analytical methods (gas chromatograph with an electron capture detector - 6C/EC) is 1 to 2 ppm. Since the Input PCB will not be pure. It Is Impossible to demonstrate PCB destruction "equivalent" to an Annex I Incinerator. The policy that EPA has adopted, however. Is that a PCB destruction process Is acceptable If the PCB concentration In the effluent streams Is "Unmeasurabla* using in acceptable 6C/EC technique. This Is an Impossible situation for solids such as capacitors, since the PCB concentration In a solid can be measured to a far greater sensitivity than that In traisformar oil. The method for measuring PCB In trmisformer oil Is simply to dlluta the oil with 10:1 hexane for viscosity reduction. This Is fo11owed.by a 2-1 HONS 018267 Cleanup using an adsorbent or acid wash to remove Impurities (If necessary) and injecting It Into the GC/EC. The GC/EC Is sensitive only to the total quaitlty of PCS Injected. The total volume of sample Injected Is fixed by constraints on the GC. As a result, there Is no way of Increasing the system's sensitivity beyond I to 2 ppm PCB. The PCB content of a solid Is found by first extracting the PCB with a Suitable solvent. The extraction Is normally carried out using a Soxhlet extractor, a device that contains a reservoir of solvent below a bed of PCB-contamlnated solid -- paper In this case. The low boiling solvent (methanol or hexane) Is boiled aid allowed to condense above the solid bed, dripping through the bed and leaching the PCS's. When solvent accumulates to a level above the contaminated solid, that quantity of solution Is drained back Into the solvent reservoir. Solvent continues to be recycled with PCB's accumulating In the reservoir. The extract containing the PCB's Is then analyzed using a GC/EC. Clearly the amount of PCB's In the Initial sample of paper Is a function of the sample size, as a result, PCB's In the parts per billion (10 ) or lower range can be detected. Because of the Ubiquitous nature of PCB's, It 1$ possible to Identify PCB's In "noo-PCB* materials In this manner. However, It Is Impossible to say that the solid stream Is literally "PCB-free." Criteria for what Is considered to be a "PCB-free" solid do not exist at present. Strong cues could be made, however, for the following to be considered PCB-free: e Solids containing less than 50 ppm PCB by weight e Solids containing less than 1 to 2 ppm PCB by weight t Solids are subjected to a leaching test with the extract containing less than 1 to 2 ppm PCB The Justification for the first criterion Is simply that the cutoff for PCI-contalnlnated material Is 50 ppm. Any material with lus than 50 ppm PCB may legally be disposed of In a sanitary (nonhazardous) waste landfill If It dots not have any other hazardous constituents or properties. Furthermore, PCB regulations allow a PCB-contamlnated transformer oil (over 50 ppm PCB) to be cleansed to below 50 ppm using an adsorption or absorption process and thereby made Into a non-PCB oil. EPA has subsequently Indicated (8) that this Is only applicable If PCB's are being physically removed from the oil. If PCB's are being destroyed, as with a chemical process, the final product must contain less than a detectable amount of PCB's, 1 to 2 ppm. If this argument Is used the residue paper and metal could. HONS 018268 2-2 most likely, not be reused but would have to be disposed of In a sanitary or chemical waste landfill. The justification for the second argument (that solids are considered to be PCB-free If they contain less than 1 to 2 ppm PC8) lies slaiply by analogy to PCB-contamlnated transformer oils. At 1 to 2 ppm PC8, there are restrictions on the oil. A process which brings the PCB concentration In an oil down to this level Is acceptable, hence a process which brings It down to the same level In a solid should also be acceptable. The final criterion for a PCB-fre* solid (an extract containing less than 1 to 2 ppm PCB) Is based on the fact that the PCB-free solids would most likely be disposed of In a landfill. This type of test can be used to determine whether a waste Is or Is not huardous under the Resource Conservation and Recovery Act. By a logical extension, therefore. It should be reasonable to use the same test for PCB-contalnlng materials. The previously mentioned criteria are all possible "end points" for a capacitor detoxification process. Clearly, no one can predict what EPA's Interpretation of the regulations would be for a particular application, however. It appears, based on Informal discussions with EPA personnel that the second or third criterion will be the one most likely used. These two result In approximately the same level of PCB removal from the capacitor solids. An Important recent development Is the awarding of a temporary permit to process PCB capacitors by EPA Region VI to Environmental International, Inc. of Kansas City, Missouri. While process Information for the operation Is proprietary mid unavailable, the permit Indicates that the processing will "reduce the volume of PCB material which must be stored." The permit also specifies that a PCB-free material Is one whose PCB content Is less than 2 ppm (assumed by weight). At least one other company (BED, Inc. of Naukesha, Wisconsin) Is developing a scheme for removing PCB from capacitors using a leaching technlgue, and then storing the PCB until a destruction method Is available. It therefore appears that It can be assumed that a material Is PCB-free If It contains less than 1 to 2 ppm PCB. One further regulatory point should be discussed here. There are many companies who will accept capacitors for Indefinite storage at their facilities. Some merely store them, others offer to destroy them at some future date. Environmental International and, possibly, SEO offer to concentrate and store the PCB until It 2-3 HONS 018269 can be destroyed. It Is strongly recommended that legal counsel be consulted before using such servtces. According to EPA's Interpretations of the PCS laws and regulations, It does not appear to be possible to transfer liability for PCS to another party; hence the current owner rust be assured that the material. In whatever form. Is properly stored and disposed of. Liability Is eliminated, of course. If the PCS's are actually destroyed. 2.1 REQUIREMENTS FOR RESEARCH The PCS regulations require that all research conducted with PCS's must be approved by the Regional Office of EPA. Such approval Is obtained by submitting a request to the Regional Administrator explaining the type of research to be performed. The request should Include the following; e Description of the types of research to be performed e Description of the laboratory and Its facilities for proper handling of PCS's e A plot plan or photo of laboratory surroundings e Quantities of PCS's to be handled e Purpose of the research This Information has been submitted to EPA for our laboratory. EPA approval was recleved on Oecember 30, 1961. HONS 018270 2-4 SECTION 3 LITERATURE SEARCH As first sUp to performing this study, a literature search was undertaken to determine what type of data was available In current literature on the treatment of PCS capacitors. The search sought to uncover any work that had been done on the following: PCS destruction with sodium reagents and other chemical means e Leaching of PCS from paper using solvent e Solubility of PCS In organic solvents e Mass transfer of PCS In organic solvents 3.1 COMPUTER LITERATURE SEARCH As a first sup, a series of computer llUrature searches were performed. These searches were performed using the following key-words: a PCS's or polychlorlnaUd biphenyls a Leach or leaching a Diffusion a Destruction a Concentration a Attenuation a Adsorption The searches were conducted on various combinations of these key-words and generated approximately 130 'hits.* Of these, the vast majority of references dealt with PCS's In the ecosystem and their Uxlcology. Two reports (9 and JO) were discovered dilch dealt with PCS's from capacitor applications. The first (9) discussed sampling at a PCS capacitor filling operation and was not found to be of use to this project. The second (JO) was a 3-1 HONS 018271 report of PCB emissions from the capacltor shredding operation at the ENSCO Incineration facility at El Dorado, Arkansas. This report showed that PCI emissions around the banner mill used to shred the capacitor could be a potential workplace health hazard. Therefore, they supported the contention that timer mills are an unacceptable method of opening capacitors In a nonincinerator application because of the PCS-contamlnated dust problem. This will be discussed In greater detail In the following sections. 3.2 OTHER LITERATURE SEARCHES Acurex files and standard references were also searched for any applicable information. This im covered only one reference that pertains to the handling of PCI capacitors Specifically, and many references dealing with the general leaching of substances from a solid matrix. The reference dealing with the handling of PCB capacitors was a public release from SED, Inc. of Haukesha, Wisconsin. SED claims to be developing methods for separating PCI from other materials, such as natural gas pipeline condensate, transformer oils, fuels, and capacitors. While the details of the processes used are proprietary, they do seem to be combinations of standard chemical refining processes, such as distillation, adsorption, and leaching. The process described by SED for the treatment of capacitors Is a shredding of the capacitor followed by a Soxhlet extraction of the residue using methanol. The PCB can be readily separated from the methanol, which Is reclaimed In a separate subsystem. SED claims to be able to produce a "PCS-free" paper and metal (the degree of cleanliness Is not specified) product suitable for reclaiming or recycling, as well as pure PCI liquid which they will store pending destruction at tome future date. No cost data was given for this treatment. It should be pointed out that Soxhlet extraction Is a common laboratory and Industrial technique for leaching material froa an Inert solid matrix. It Is described In section 2 mid will be discussed further In Section 4.2. An area of the literature search which proved fruitful was Identification of methods which predict leeching bed behavior (Vl_). Since leaching Is one of the oldest unit operations of chemical engineering, reliable equations exist that can be used to predict this type of systems behavior, unfortunately. Information could not be found on distribution coefficients for PCI's between paper and a solvent such as methanol or hexane. As a result, these calculations can only be used for 3-2 HONS 018272 taping calculations. Additional data Is noodod to use them for design purposes. ThtS will be discussed further In Sections 5.4.2 end 5.5. HONS 0X8273 3-3 SECTION 4 CAPACITOR PROCESSING One* tht C4P4Cltor housing has betn breached, there ere too possible Methods which cm be used for PCB destruction. The first, conservative, approach (s separation of the PCB using a solvent extraction or leaching schene followed by a sodium naphthallde treatment of the PCB-contualnated solvent. The second approach, which has not been described In the literature, Is treating of the PCB-contamlnated core Deterta! as a slurry. The core material consists largely of paper or plastic film end eliNtnum with possible small mounts of other metals, all contaminated with PCB. The metals will not affect the PCB destruction process; however, the effect of tht paper Is unclear. Laboratory experience Indicates that paper appears to be relatively inert to sodium; however, one may Infer from chemical structure of cellulose, the principal constituent of paper, that at least some chemical reactions should occur. This question Is discussed In greater detail In Sections 4.4 wd S.6. Needless to say, significant cost reductions would result should PCB destruction prove possible without separating the PCB's from the other core material. It my evan prove possible to destroy the PCB's In the capacitor directly, thereby eliminating the need for cracking, shredding, and rlnstng of the casing. The following sections will discuss the fundamentals and Informtlon gaps associated with: a Piercing and opening of casing 'e Leaching and rinsing of cuing and core materials a Destruction of PCB liquid e Possibility of treating total capacitor without first leaching out PCB's 4.1 PIERCING ANO OPENING As discussed previously, a fraction of the capacitors which need to be disposed of contain a sawll amount of gu under pressure. Mien the capacitors are pierced, this gu could ruult In a PCB spray that could contaminate workers and processing equipment, and ruult In PCB releuu to the eiwlronmant. The haanmr mill at a 4-1 MONS 01827N capacitor Incineration facility was found to be a source of PCS dust (10). It should be noted that the dust from a hammer mill associated with an Incinerator or other combustion equipment Is normslly suppressed by maintaining a negative pressure and venting the discharge to the furnace as combustion air. This is clearly not possible when operating a chemical process, since no combustion air is used. If a hammer mill Is used to shred the capacitors prior to treatment. It Is necessary to vent It to an air pollution control device that can capture PCB-contamlnated dust. Fabric filters, while very effective for dust suppression, do not work well when the dust Is oily, as In this case. The PCB would coat the bags and clog them. Scrubbers could be designed to remove the dust, but their use would result In a PCB-contamlnated liquid stream which would need to be treated. Electrostatic precipitators might be effective, but there Is little Information on their efficiency In removing such a very high resistivity dust. There does not appear to be a satisfactory dust suppression system available for a hamaer mill processing PCB capacitors. Phase II of this research program will compensate for this by attempting to either eliminate the shredding of the capacitors altogether or reduce It by determining the minimum amount of shredding the capacitors would require. Should capacitors shredding prove to be required (at whatever level) It will be necessary to examine the various methods available. Various designs will need to be evaluated to determine idilch are likely to be the most practical for this application. Alternatives to hamaer mills are available. A promising option Is a wet milling system (under oil Instead of water) that would utilise grinding rather than Impaction. The material produced Is of a lest uniform particle site than that from a hamaer mill, but this type of grinder would produce far less dust. Another option (s a shearing mechanism that merely cuts the capacitor open and dumps the core out In several large pieces. The Phase II program will evaluate these options and recommend a shredding system that meets the needs of a chemical PCB destruction operation. 4.2 LEACHING ANO RINSING There are two activities that fall under this heading. First, unless the capacitor Is treated In one piece or shredded thole. It Is necessary to' decontaminate the 4-2 018275 empty cue prior to d 1 sposa1 . Methods of achieving decontamination need to be evaluated. Second, the core material. If It cannot be treated as a mass with the sodium reagent, needs to be leached with solvent to remove PCB's. The decontamination of the case Involves more than simple rinsing with solvent. To Illustrate, Napier {12) conducted an Informal experiment in which he filled a steel pipe with PCSs and let It sit for a time. He then drained and rinsed It In the manner required to decontaminate PCB transformers, and refilled the pipe with non-PCB dielectric fluid. This was allowed to sit for 90 days. The dielectric fluid tested for PCB, and showed significant PCB contamination. This does not mean that It Is Impossible to decontaminate the empty capacitor shell. However, the procedure may require a great deal of time and/or solvent and may be Impractical. A useful tool for aiding the cleaning of the case Is ultrasonic cleaning. The limiting factor In rinsing of the case Is the diffusion rate of the PCB molecule from the walls Into the bulk solvent. Ultrasonic cleaning Is a well established tool for aiding this type of diffusion, and can substantially reduce solvent usage. Its efficiency will be explored In the research progrma. An alternative method of decontaminating the shell may be to simply rinse It with sodium reagent, since It does not appear to contain any component idiich would Inhibit the PCB destruction reaction. This area needs further Investigation. Finally, It nay be desirable to treat the empty shell In the same manner as a drained PCB-transformer shell. That Is, after removal of the core, the shell Is triple-rinsed with solvent, filled with a non-PCB solid, absorbent, and then landfilled. This approach, while probably not the preferred option, must be considered u an alternative should the Phase II studies show that rinsing to cleanllnesss Is too costly. Separating KBs from the paper and metal In the capacitor core Is a far more difficult problem than decontamination of the metal shell. The PCB*s are tightly bound to the highly ebsorbent core material. There seems to be little question that It can be removed through a leaching operation, possibly using some form of reboiling extraction system. The question Is whether the energy or solvent requirements and time needed to achieve the necessary level of separation can m*e such a process practical. HONS 018236 4-3 There ere several ways of performing this type of leaching. The simplest, of course, Is to simply mis a volume of PCB-saturated core material with a volume of suitable solvent, such as hexane or other organics. The PCB will. In time distribute Itself between the paper and solvent, then the mass can be filtered to separate a partially cleaned solid from the PCB-contamlnated solvent. The process can be repeated with new solvent to further reduce the PCB content of the solid mass. Clearly, the number of leaching steps which will be required to achieve a given final PCB concentration Is a function of many factors. The most Important art: a Volume of solvent for each leaching stage e PCB concentration in the original solid material a Distribution coefficient of PCB's between the solid and liquid phases a Time permitted for each leaching step To understand the Importance of each of these factors It Is possible to perform a scoping calculation. Assume that a mass of solid (say 1m3) containing 10 percent PCB by volume Is mixed with an equal volume (lm3) of a solvent such as hexane. This material Is than allowed to ttand, possibly with some stirring until equilibrium Is reached, and Is then filtered. Even though the partition coefficient Is not known, it Is still possible to estimate the degree of cleaning which would result by assuring that the composition of the liquid remaining absorbed In the solid mass Is the same as that of the filtrate. In this case, one wash would result In approximately a tenfold reduction In the PCB concentration of the solid. Ideally than, about six washings would be required to achieve a PCB concentration of less than 1 ppm. If the quantity of solvent Is doubled, the same effect would be obtained with about five washings. Similarly, If the solid contained 20 percent PCB (Instead of 10) a 1 ppm product requires only about seven washings. Clearly, these are not significant factors. In fact. It can be shown that the only significant factor Is whether the leaching liquid can be Intlmetely contacted with the PCB-contamlnated solid In a practical way. If such contact can be achieved, a final solid product containing lest than 1 to 2 ppm PCB Is readily achievable. There are several methods of further reducing the quantity of solvent required. The most common method would be the use of a countercurrent extraction process whereby the contaminated solvent fran one batch Is used to leach the material In 4-4 HONS 018227 mother, higher PCB concentration batch. This Is shown schematically In Figure 4*1. Another method for reducing the quantity of solvent required Is by re-refining It. A simple method of doing this Is analogous to the percolator method of making coffee. The PCS-laden solid material Is placed In a bed above a reboller filled with the solvent. The solvent 1$ boiled and vapor is allowed to condense above the bed. The condensed solvent percolates through the solid and carries the PCB's Into the reboller. Since PCB's have a high boiling point, they will tend to remain In the rebollder while the solvent, hexane for example, will continue boiling up through the bed. At the conclusion, the solvent can be readily reclaimed by a simple distillation, leaving behind pure PCBs. Because of the very low PCB concentration that must be achieved In the solid, each batch will have to be processed with two to three "percolations." There appear to be several methods readily available for removing PCBs from the capacitor cores. The question Is not one of "Is It possible." but rather of practicality and cost for the alternatives available. 4.3 IN SITU PCB DESTRUCTION There appears to be no scientific reason to prevent the opening and shredding of PCB capacitors, followed by leaching out of the PCB's using a solvent such as hexane. The PCB's can then be chemically destroyed. The more processing a decontamination scheme requires, however, the greater the cost. Clearly, It Is worthwhile to attempt to eliminate the leaching step by direct treatment of PCI-contaminated solid matertal with the sodium reegent. The process to be explored can be: a Pierce the capacitor to relieve any pressure which may have built up a Open case and remove core material a Shred core material and mix with a diluent such as hexane a Treat the slurry with a sodium reagent to destroy the PCB's This approach can work If the core does not contain any material that will Inhibit the PCB destruction reaction. The sodium reagent Is a very strong reducing agent, end will readily reduce water, releasing hydrogen. It will also react with alcohols, acids, and many other organic compounds containing an -OH structure. The core material, does not contain water, hence this will be of little concern. The metallic components will not affect the reaction. The Insultatlng materials 4-5 HONS 018278 ClMn solvent Non-PCs solid Solvent + PCS PCS contam. solid HONS 0 1 8 2 7 9 Figure 4-1 Scheeietic of Countercurrent leeching Operation Inside the capacitors are either polypropylene or paper. Polypropylene Is also Inert; however, paper nay react with the sodium and possibly inhibit the PCI destruction. Paper Is principally cellulose, a polymeric material of the following general composition. CM,OH { H_ _ _ OH CM,OH j MOM The sodium could. In theory, attack the -OH groups on the molecule rather than the PCS. While this Is a concern. It does not preclude the treatment of the slurry. The sodium. In attacking both the cellulose and PCB's participates In two competing reactions. The PCB attack has been found to be very rapid. One would expect the cellulose attack, since It Is a heterogeneous reaction, to occur far more slowly. In fact, a quick test with dry paper and sodium (under nitrogen) revealed no noticeable attack. This test Is far from conclusive but It Is very encouraging. We have, In addition, successfully filtered a sample of reagent through filter paper and little or chemical reaction was observed. As a result, all the available data Indicates that It will be possible to destroy tht PCI's In the capacitor without having to leach It out of the solid matrix. Should the paper prove to Inhibit the PCS destruction, It would still be possible to combine a leaching with a PCI destruction system and achieve significant overall reductions 'In the cost of PCI capacitor decontamination. HONS 018280 A-7 SECTION 5 PHASE II PROGRAM PLAN All of the work completed to date his shown that tha chemical treatment of PCI capacitors appears possible. Tha program now moves Into Its second phase, verification and determination of treatment cost. This will Involve construction of specialized laboratory facilities to open and handle PCS capacitors, as well as performance of a research program to do the following: a Construct the PCB containment housing In the laboratory a Determine a safe method of perforating the capacitor shell to avoid PCB contamination of worker and workplace a Determine whether rinsing Is adequate for shell decontamination or If other decontamination procedures are needed a Evaluate several potential methods for destroying PCB's In capacitor cores, both free liquid and that absorbed by the material of the core a If these tasks are successful, determine the approximate cost of such a treatment and design and cost of a demonstration program a Prepare the final report 5.1 LABORATORY DESCRIPTION The technical program will not Involve the purchase or construction of large pieces of processing equipment. An 'Isolated1' laboratory to handle contaminated materials will be necessary, and ft -Is currently under construction In Cincinnati, Ohio at no cost to EPRI. The construction of this laboratory Is continually being reviewed by our in-house safety engineer who will assure compliance with Occupational Safety and Health Administration (OSHA) and Department of Health requirements. Because of the nature of the capacitors. It will be necessary to install special equipment within the laboratory to pierce and open the capacitors. As discussed earlier, these capacitors nay have accumulated internal pressure, therefore the containment housing must be constructed to handle the sudden discharge of PCB materials should one of the capacitors be under pressure. There are no openings In 5-1 MONs 018281 capacitors, so (t Is Impossible to determine whether any given unit Is wider pressure prior to perforation. These enclosures will be built as part of Phase II. They are described In Section 5.2. These special enclosures are the only pieces of equipment beyond routine laboratory ware which will have to be purchased or built for this program. The purchase of chemicals will Include sodium metal, naphthalene, tetrahydrofurmi, and other solvents necessary for core PCS extraction tests. The laboratory Itself Is (shown In Figure 5-1) a sealed room with a seamless polyethylene liner floor that can contains PCS sptll and be readily cleaned. The liner is laid In such a manner as to form a dike completely around the PCI haidllng area. The walls and celling are coated with a special, Impermeable paint that can be readily washed down. The areas where PCB materials will be sorted and handled are further shrouded with polyethylene sheeting. This arrangement makes decontamination In the event of a PCB spill or spray very easy. This laboratory design has been submitted to EPA and approval for research Is expected by January 1, 1902. . 5.2 CONSTRUCTION OF CONTAINMENT HOUSINGS These housings are necessary to contain any possible PCB discharges when the capacitors are pierced and handled. The first requirement Is a housing which can be used to pierce the capacitor and contain any resulting spray (see Figure 5-2). The housing Is made out of an open-leaf 5S-gal drug, modified so that a sharpened l/4-1n. (0.6-cm) steel rod passes through a packed gland in the head. The rod Is placed on top of the capacitor and rapped with a hammer, piercing the ease. Any PC* spray released will be contained In the drug. All materials of construction are compatible with solvents used, as well as with the sodium reagent. As a result, this system will be easy to decontaminate at the conclusion of the research. The capacitor will be opened In a second enclosure. This enclosure Is made of dear plastic. It Is approximately 4 ft x 4 ft x 2 ft (1.2m x 1.2m x 0.6m). One of the 4 ft x 4 ft walls (1.2m x 1.2m) Is pierced with flexible gloves creating a totally sealed "glove-box" effect. All processing of the capacitors solids will take place Inside this glove-box (see Figure 5-3). HONS 018282 5-2 lib to contain possible spill FI jure 5-1. Test Laboratory 5-3 HONS 018283 1/4" (6. 35m) High carbon steel rod -9/32" 01a (7.1w0 1/4' 01a (6.35ua) Tapped for set screw rrasri!6* (1S2n) 9/32" (7.1ms) Bore HONS 0 1 8 2 8 4 Detail of Lance IV 55 Gallon dna (208 liter) Weld to druahead 9/32" (7. lax) Bore Detail of Packing Figure 5-2. Capacitor Piercing Systea S8?BT0 SNOW Figure 5-3. Glove Box for HenOI<ng Cepecitors In order to properly process the PCB material, several different types of h>d tools end laboratory equipment will become contaminated with PCB. These are restricted to small items such as a saw or a llqulfler (blender) to open the capacitor and shred the core material. Because these tools and laboratory equipment will be contaminated with PCB's, it Is expected that they will have to be discarded or decontaminated at the end of the experimental program. Acurex will be responsible for the safe and leqal disposal of contaminated equipment. 5.3 CAPACITOR PERFORATION AND SHREOOING The goal of this program Is a safe, reliable means of opening and shredding (if necessary) capacitors so that they can be readily subjected to chemical treatneit. This program will be coordinated with the two decontamination programs to determine the most efficient combination of shredding and treating. The current method of shredding of capacitors Is by passing the whole capacitor through a hammer mill. This, while convenient, is not necessarily the best approach. Hamer mills work best on materials of approximately the same friability. Capacitors are a mixture of metal (from the shell), paper, or plastic film and foil. The hard metal can be separated from the soft core material without a large amount of processing. In doing so, much of the dust produced by the hammer aril! Is eliminated. The objective will be to keep the case as Intact as possible and remove the cores. The following possible approaches to this will be Investigated. e Pierce the capacitor to relieve pressure, then cut off the top and use a shredding wheel to remove the core; alternately, cut the capacitor Into several pieces e drill several holes along the top of the capacitor and Insert high-speed chopping blades (much like blender blades on a shaft) Into the core to liquify It Clearly, these are very general approaches and represent only the first step In an Iteration to arrive at the optimum shredding techniques. The physical properties of the capacitors' component parts will be examined and compared to the specifications for a variety of commercially available shredding or site reduction equipment. This will set the specifications for designing full-scale equipment. In addition, the results of the laboratory shredding program will be evaluated to determine whether a custom-designed size reduction system is likely to be more appropriate for this application. 5-6 HONS 016266 Th* results of this size reduction research Mill be Integrated with that of the leaching and PCB destruction test for the design of the full-scale demonstration plant. 5.4 SHILL DECONTAMINATION Once the core has been removed from the capacitor, it (s necessary to prepare the shell for disposal, preferably In a nornal (nonchemlcal waste) landfill or by reclamation. Three known methods can be used: a Triple-rinse the shell with a non-PCB solvent, fill with absorbent and discard In a secure landfill. Then treat the liquid with sodium naphthallde to destroy the PCB's. Primary solvents for consideration are THF, hexane, and kerosene. The use of ultrasound as an aid to decontamination will be explored. a If there are no materials associated with the shell to Inhibit the PCB destruction reaction, decontamination may be possible by simply treating the shell with sodium naphthallde reagent. a Subject the shell to an extraction to reduce Its PCB concentration to below the EPA limit of detection, 2 ppm PCB. The shell material can then be reclaimed or disposed of In a regular sanitary landfill. The Phase 11 program will evaluate these options. The shell will be cut Into 6-In. x 2-In. (lS.2-cm x 10.2-an) tabs and each of these tabs will be subjected to a rinsing procedure using various amounts of different solvents, with and without ultrasonic cleaning. The quantity of solvent used for each tab will be computed on the basis of solvent (ml) per square centimeter of surface to be cleaned. In this way. It will be possible to relate the results of these tested tabs back to the whole capacitor case. This approach Is necessary so as to minimize the mnfeer of capacitors which must be handled. This approach will also eliminate capacitor to capacitor variations which could make results difficult to Interpret. To determine whether triple rlnstng the capacitor shell Is an effective decontamination method the tabs will be triple-rinsed with an appropriate volume of each solvent under consideration. Each rlnsate will be analyzed for PCB's. The rinsed shell material will be subjected to a Soxhlet extraction (as described In Section 2) to determine the amount of PCB residue remaining. The second approach, decontamination with direct treatment of sodium reagent will be Investigated by placing the tab Into an appropriate volume of sodium reagent. HONS 01628* 5-7 These tests will be conducted using successively lower mounts of reagent to determine the minimum reagent needed to reduce the PCS concentration to below 2 ppm by weight. The final set of tests are similar to the previously mentioned tests to be performed In the triple rinsing tests. These, however, will be performed using different types of solvents until the PCB concentration In the solvent Is less than 2 ppm -- the EPA limit of detectability. These tests, along with ancillary PCB solubility tests, will be used to design a leaching system for the full-scale demonstration. 5.5 CORE DECONTAMINATION The Phase II research program Is Intended to achieve an optimum capacitor treatment system design. Ideally, the program will Identify a scheme whereby PCB's will be destroyed without the leaching process. The first step will be to test that approach by performing a series of tests to establish whether treatment without leaching out PCB's Is possible. These tests will consist of the following: e Remove a sample of PCB-contamlnated core material and shred finely In a blender e Treat this material with the sodium reagent and detemlne levels of PCB destruction achieved, reagent usages and times Involved The tests will be performed at various levels of reagent addition. It Is expected that the results of one test will lead to the design of other experiments. As a control, the free liquid removed from the capacitor will also be subjected to sodium treatment. This series of tests will also evaluate whether the diluents used affect PCB destruction. Among the diluents that will be Investigated are hexane, kerosene, and tetrahydrofuran. The results of this set of tests will determine whether direct sodium reagant treatment or preleaching will be used for the rest of this program. If the previously mentioned tests are successful, the leaching tests will be minimized and the majority of the effort will focus on optimizing destruction conditions for PCB's In a heterogeneous medium. If It proves Impossible to achieve good PCB HONS 018280 5-0 destruction In the heterogeneous medium, then the effort will focus on developing an optimal PCS leaching/destruction cycle. The two alternative programs are described In Sections 5.5.1 and 5.5.2. 5.5.1 Direct PCS Destruction This research scheme will be followed If the preliminary tests show that It Is possible to destroy PCB's without first separating from the core material. The program steps are: A. Perform a series of experiments, starting at a high reagent concentration, to determine the minimum amount of reagent needed to treat a finely chopped sample of the core material. These will be done at successively low reagent addition so as to develop a relationship between reagent concentration and reaction completion. B. At the minimum reagent addition rate, perform a series of experiments to establish the minimum grinding the capacitor core material will require for treatment. C. Determine what methods exist for achieving the desired degree of capacitor core site reduction while still In the case. Therefore, the case and core material can be decontaminated In one step. D. Perform a limited number of leaching tests on the core material to determine mass transfer rates and other leaching parameters to permit the design of leaching systems. In addition, a dual-system leaching followed by PCB treatment will be evaluated. 5.5.2 Leach and Process Route This research approach will be used If the results of step A, on the previous page, show that PCB cannot be destroyed when mixed with the core material. . Perform a series of experiments designed to determine the mass transfer and equlllbrliae parameters for the leaching of PCB from the capacitors. This will be done using three different solvents. f. At the optimum solvent usage, determine the minimum amount of grinding that the capacitor material will require. S. Determine whether It is possible to grind the capacitor core sufficiently while it Is still In the case. This will make It possible to decontaminate the core and case In one step. H. Compare the effects solvent types used on the subsequent PCB destruction reaction. HONS 018289 5-9 5.6 DESIGN DEMONSTRATION PROGRAM If the laboratory tests Indicate that capacitors can be safety and satisfactorily destroyed using the described chemical approach, the results uill be condensed and Incorporated into a proposal program for coitmercial scale demonstration of the technology. A cost estimate and schedule will be included. 5-10 MONS 018290 SECTION 6 CONCLUSIONS This preliminary study has shown that there are no physical or chemical reasons why PCI capacitors cannot be decontaminated by chemical means. The question is strictly a matter of "practicality.'' Chemical detoalfication methods are currently revolutionizing the area of PCI transformer oil treatment, largely because of their atoll 1ty (they can be used onsite, hence no siting problems) and they are more cost-effective than Incineration. Chemical detoxification of capacitors appears to offer the same advantage. At present there Is Insufficient Information available to properly design, build, and operate practical PCI capacitor detoxification systems. The Phase II research program described In this report will research, develop, and design the full-scale capacitor opening processing equipment necessary for this system. It will also provide the Information needed to select an optimum decontamination scheme for the case and to destroy PCI's, rather than to merely extract then from the solids and store It. The research plan developed Is flexible. It strives to achieve a breakthrough, the direct chemical destructlen of PCI's In capacitors. It also has provisions, using existing technology, for achieving success should unexpected problems prevent such direct PCI destruction. Therefore, there is a maximum probdalllty for the successful development of a usable chemical detoxification system for PCI capacitors. HOWS 018291 6-1 REFERENCES 1. Scott, N. 0., J. F. Walker and V. F. Hansley, J. American Chemical Society 58. 2442-2444 (1936). -------------------- ----- 2. Smith, G. and G. L. Bubbar, The Use of Sodium Naohthalenlde to Chemically Destroy PCB by Oechlorinatlon, ibid. 3. Brown, J. F., M. E. Lynch, J. C. Carnahan, and J. Singleton, Chemical Oeatructlon of PCB In Transformer Oil. Ibid. 4. Weltiman, L., Treatment and destruction of PCB and PCB Contmlnated Material. Paper presented to the division of Environmental Chemistry, American Chemical Society, New fork, N. Y., August 1981. 5. Federal Register, "Polychlorinated Biphenyls (PC8s) Manufacturing Processing, distribution In Commerce and Use Prohibitions," Vol. 44, No. 106, May 31, 1979, 6. Environmental Protection Agency, Office of Toxic Substances, "Support Oocument/Voluntary EIS and PCB Manufacturing, Processing, Distribution In Comnerce, and Use Ban Regulation: Economic Impact Analysis," April 1979. 7. Electric Power Research Institute, disposal of Polychlorinated Biphenyls (PCB's) and PCB-Contamlnated Materials, FP1207, Volume 1 October 1979. 8. Kuntz, G., W. Gunther, US EPA, Washington, D.C., Personal Coamunlcatlons. 9. Halle, C. L. and E. Baled), Methods for Determining the Total PCB Emissions from Incineration and capacitor - and transformer - FTT11no Plants. fcPA-B0tl-4-77-iH8. November IMI. * 10. Nodes, C. E., M. 0. Jackson and R. G. Lewis. Monitoring for PCB Emissions from an Electrolytic Capacitor disposal Project. rW-WO/4-78-OK, Hay 1978. ----------------- ------------- -- 11. Perry, Chilton and Kirkpatrick. Perry's Chemical Enolneers' Handbook. Fourth Edition, McGraw Hill, 19617^ ------------------------ 12. Napier, J. M., Personal Comunlcatlons (1980). HONS 018292 6-2 APPENDIX A RESULTS OF COMPUTER LITERATURE SEARCH HONS 018293 NlfOUIIWTIKllMifWN M UOf? 9 tun t*M iirwif nM SiSSra!*" ' >timmm inonirm l M M0O Prim 11/1/1-M t--rM Tim: 0. KM Prints: m 9mm.: u HONS 0 1 0 2 9 4 FMf-asmi NTH frtaM! K Ml Mil a# AMljrtlMl tnllty eaMrvI far PwtMIN KilMM OaweiMdB In Nmmm and ftwlmutal lplM 0UfaytM Call.. IMIW, M. Mt. af CMMlalpy.KiMlrfnwiUI ipenry, limrai Irlanfl* rark. mc. (otMMOOD *MtS ,h*rTi; STS**, PM* 4MN|rHIMIbi MM* CMtrait; (M'-N>MT .See iIm n Tl. n*M Til.. MUIVI21 InirMHn: NatiellM. Owill amlyila, *Ouoltty control . HMmiala, tapll"C, n Mini Kayapiiy. Hrfar^na aaalyatlm, Tli layar ahraaainrai|, laparallan, Urtna. Niiaiaa, CartaMin, latraetlm, cencantration<Cooposition). Iitrastlana. fhaapnarwa arpanla aaapMMa Identifiers: Nipi parfai nance I iill Oraamgrphy. tolycMartwM aiphanyla, WTIWUM mi-ionn mis iricaa: rc im/m aoi MUellnf Ma Kaavallaatllty af NlMHIarirataa Ifhinrli (Ntal In Sells Mart* Carotins Stala Unu. at lalaijlt'OfMca of Mat or Sesoercn and lactMiogy, MesMnpton. OC. loss300000) MlTHOM: Strok. Marry do*n Mastars* Miosis 40TIA3 fid: M, SSC, AS*. MO isso map frojoct: aMM-mHaC Manltar: OwdTB'I3S-NG(*) Mllllll Basertptarc: *Soli analyaia. fiaaasay, San proportion. Chiorino arpanle eoaaainaa, Sands. Actlvotod carbon. Absorption. Fast Ic Idas, Clays. Those*. Leaching. Ftanta(potony). laatopic labeling. Slaps. (wile aoaitity. SaltMlllty. Moisture content. Sail prsosurs. Moods. Motor pal lotion Idantlliars: Folychlorlnated bipfwnyi*. Aroctor i}|i, *aotn of pal latent*. Orpanic aotlor. MTISOIOWT. MTISOIOMPI f IMI'UWTI NTIS Frtcao: PC AOS FMI-3037M mis Frlcaa: SC AOB/Hf AO I lOWw Mf OolyaMlarlnatad Biphenyl* py natural PMytoptarfcton Aeaamiagea: Flaw and 1 Moratory Detamtnett*n a# tac-rci Part lato*M*tar Indao af Sorption State Unw. af Mow fork at Stony Break. Marina Sciences Baaaarsh Canter. HMt tonal Ocaanic one Ateoopnoric Adalnlstratlan. MocAwllla. UD. pmos of Sac Pet. ( OI4S9MM) AOTMOP: Blpps. 0. C-; Fewer*. C. 0.; Maw land. a. O'Cannora, M. B. dr; Morstor. C. f. MN4II fid: Bf. BA. BC. MO, 410. 7C. BAM OBITS eltao Ip 99Manlier: NBAA-tttATStt .Fa. In Cnrlraneantal Fallwtian (Sorts* A), v piOl~ltO ltap.. Frcpsrod In aaaparatlon with Tanaa I and a Untv.. Canape Stettan. Paaartptara: Phytoplankton. L*np Island land. CMcriia argents aaapdwnda. Catuariaa. Orewth. Farticlaa. CansantretlefMCemMltten), Piatoaa. Baprinto leant l flare: *Polychiarln*t*d aipnonyla. Malar pollution affoatatFlantal. Piaaccuswlatian. saa prant prapraa. SAalatonaaa aaotatua. Fartlaulalaa. WlSCBBBl Cnvlronaantpl Aaaaosnant af Fhyaleal/Oionleal tracts BpI a tad ta Mia Oradplnp and Plapaaal af Spall free tits Frepaaas Treitfi Taps Craaalnp af tne Anaeastla River fcaiaglcal Analyata. Inc.. Sparks. Ml.Masntnpton Metropolitan Area Transit Authority. OC. (073419000) AUTMOB: Flno. frank M.; Vast. JonethenC.; Saul, Stephen w ; Mead. Saran . Oats rapt, (final) Hay BO-fsa Bl 04Tessa fid: I3P. BBC. BOO. BM 0BAIBI30 Mar Bt ItSp Bapt Ms: CA-FPS-OIK Ipanaarad in part My dasninpton Motropelitan Araa Transit Authority. OC. Oaacriptara: *00110 waste diapaaat. Mater pollution. Aaaaa--ants. Anaeastla Plvor, CancantratiaMCoapoaitianl. fnittliN. Ollordan. OPT. Iran. IMrary(alal). Sadlaanta. Sitae. Oopuldttana. laMlaa(Oata). Faiaaia water. Praietd water. SaopMnp iMntifiars: Oredpe apa 11. *Sai id waatas. *water pollution Adplinp. Falycnierinotad aipnonyla. miswuia. NfISMmaia HONS 0 1 8 2 9 5 PMI'IIM? Mil Pp|n; PC MT/W Ml tHtMMM llniv.HWImr. Wtar wren Cwtp.*(n*lrwMMl Office. Hni). OMcapa* li. Irwt UMt lbtlnal Pntm (OMMtIM) AtmtM: An*>an. A. p.; DaMiay. f(al rapt. D)4n Mm4 ru: ia. mc. mi. Mr CO IMp rant: tfA-a-OODM2 niter: p. V.; Strand. J. d ouum tf. Paoorlptara: *4Jr pollution, HM mmtpan Poetictdee. aatar pollution. Partlalaa. Vranmort prapirtlae, taaaaltlw. SaapHnt. Conoenroton<Oaapaetton). Vaporisation. vtliniu- at tan, flua<Peta) ItanJlflam; Palyoftlartnotad Uptanyla. vAtr-wetcr interfaces , Arcelor im, Araclar I3S4. XAO-I resin. Araclar I3d0. Maarlcal solution. MltiPMU. MUStPACtA PNI'ltflfO MVIS Prlaaa: PC AM/IP Ml (nhattai at PCD Destruction Ifflalaney m art InMiatrial aaaaraD Trianplc Inat.. daaaarcn Trtartgia Para. MC.Industrial (nvtronacntal Daaaarea la.. teasereft TMotcI# Para, MC. IMMMOOO) AUTMOP: Calllita. P. f.; Hunt, 0. P. final rapt. Pup-tap M D4MMM fid: ISP. DPI*. A POAIdttA Apr PI ftp* Contract: (ri-M-<n-]i4 Marti tar: tPA-SOO/3-dtOMO Paaeriptara: *Air palItitiart. Autltlnt. dollars. Chlorine arpartic coaaaunda. Mat paaaa. forreroutes evsluation. Industrial uaataa. Somltnp, atchipari Identifiers: Polychlorinated biphenyls. Say cttylPtcntpan), MVISCPAPPD ital end tr Daaaurpaa tnpinsortnp.Municipal Cnvlronacntat Paaaaccn tap.. Cinairmati. ON. Iamvaran) AtmoP: Paaar. ualtar 4. P: Piraaiart. MaaaouC final rapt. Apr VA-Mar so 844HM n: tap. aao acAiativ Apr at map Srant: (PA-*-dOM* Manttar: (n-Mt/MI M7 Oaacrlptara: Patar traataant. 'Activated cardan. Cerpon tatracniarica. tanaana. Cniorlna nrpanlr conpoundo. ACaorptlon . PnM acid. PataPla voter. draphe(Cherts). Laboratory aaipr"i. Parfaraanea evaluation laantifiora: Vaaie a*atancaa. Polycnierinated diphenyie. Otaiarla, Panaano/CIcniaro. Organic aattar. Ctnana/cicMara. MriUfADBO IMHI29M MVIS frlcaa: PC AI4/MF AO I PulOat Inaa far the Disposal of pcps (NlyMItrliatM Ipnanylal and PCD Itana Py Thorpe) Destruction II*. Inc.. aaderda Poacn. CA.industrial fnTTrnrwarvm search Lap., daaaarcft Trianpla Para. mc. (oOdTAAOOO) MMHM: lelur--n, 0. I.; Sc Into, t. t.; aaast*. P. s.j toluoyoa. . O. ; dahnson. a. d. final rapt. Oct V0*Apr AO AAdWI fid: ISP. dit. MC. MA. 43f rap ai stop CPAItlt? Contract: IPk-M-Oa-3174 PenI tor: IPA-AOO/3-dl -032 Oaacrlptara: Pastlcldsa, Incinaratora. *00100111100. Mfulitiaw, *( to waato dtapoaai. Caapuation product a. Indtratrlal uaatoo. Ooalpn criteria. Parroraac* evaluation, laopl inf, Air pollution control aIdnsofPnAtlfOlaaroa: Polycrlornatod Alpwnyl, *tlquid uaatoo HONS 0 1 8 2 9 6 PMt'taftfT MVIS frlcaa: PC AIT/NP AOI Iffodtlusnasi Caralaapanla PMMWIT mil IPWM: PC *09/** Ml Paotllttea twNXlm of 9*01 Cfftelenoy IHNr --timrllw MOMnHIMPWr:l: IIIMM.--IT-OI-It>IOllTU4 O,MlaCiHlalWn,fCi M(a1rl1m1 Imntlflvn: *HpW<ny1/rclilm*, #*lydilrintM blftanrU. iKlMrattM, MoOiPlni plants. NTIMM0I9 PMM1M4Y MTIS IrlOMi PC M/V MM MClaasltirkioNmOaNpoevv,alMuailtaionnoM. CpamtItfmam. isOO-at-TSO. Nellto tea ri ONONaM.t(TanWNalat)a)Ilntnst,hfiaurnOl aaansOatiTaewclftnltaofatltyAaanaataMtaanacaito.irCaninecti.nnati. aOtttOO1 bfyp* p amat ni; oa. at. iiu, in. no. ooa niiiim OyTIenseendlaaevutetiarasrotlptptnryyitma.a).rleCsnHS:tryaulptlraIvasMrenuitsoayrvs...eaCtryloasIaenn.aucaeCatprnsMtaatnretaolrapittnenataeu.rwaiCaarSClr#ppata.alnanpnnadicaats1rIed1.nostOaSa. pnaue)feeeu. stntryTcalaiiewsl.aomesnfHsoapaaidetiscaloltuPnnrnaee*... nIId3aeaNnlt-ntNi.fi-e)ra.si:Pr esteyaatepntistantreptn.aataNuPaislotaatpnacneaanp.yetare. tNaOaatcnactttayetrttneenpeep.etNewTsrUaeaMfe.WtyImacan$d (0311 *20*0) oSfiOsnToaWtaOlaOrt:atpvte,Mrst*a.y:DTteots-.Seraatpa; al0.a0oMoaartrgirmr,iovi.d(.; zteike. a. i. ONcatnI0t0er; fIP4Sp-SOO/T-OO-ITl OefapIinaaaneweadalapcudlrwyrstsnpptiOrtstlieaeae,nsr.lPattsawe: .arCts*IetdNensiastr.asaaC,snfstsritaneiectwlt.eeintcpl(atC*ernfilrecyaapccppryeoeacwdteutetcltrcatstepsnaM.l|an.yentdantrso.aSc,naatrcatceopno*tlntianarspr.ni.naplaoyOfsltalteussrtpct.lieaotMrrnnsiaicc,.s I.dPeenltyicfineiresr:insCteodaloifpirneednypiesw. anrwpiclapnstoso,dair pollution detect ton soat'ittaoa nvi trim: sc aoc/np aot PeCvOaluOaetisoldnuNay LOesvaelslsl OirnetpMlnupaan aaipese Tissue; a statistical MTeaCss.ateafnrSewftli*ratnaTanarelnaetnsa.pl lePr1o0te4In0c0sti0ot0.n.00t0p)onScye.saMarMchiirpiTari,taDnCp.leOfflcPoarak.f NGSFUSuTiOeNltOOlvOMr:.a;pLvwt.te1Ca1IsOt.a:nSSaoT.a.eSrStleTpa.n.Sa;nTVaC..rSleHssenC. S4NISltIe1H9 ell 0.; Plserctite. NCMeoownn0tirt0oarc:t; |IP0C9*Pp-MS-OM/-U0-IT-MS4<*0lf DCInaesnsececratiIpncttIorOartsslas: .nICCPnastassprtllaneaaldltsieasrnp.la. nOlTceascslpalcnaop. laaCuonhyse.sa.lcaHeealasaarennesae.lyIosnOt*aaonoaylayspins,.. Identifiers: Polycfilorlnatad Plpnanyls. Paaticlda residues. Menltarlnp. lasts ewoelance*. Oace. NflSfPSOVS HONS 0 1 8 2 9 7 POSI-laiaai NT 10 Prteee: PC SOT/NT SOI Plata IMf ta ONtein Traaa llaanl Nm talanaaa at a Ceel'Ptrud Wlllty tailor Tannoaaaa Valley swtnarity. cnattanaapa. OW. af tnarpy Paeanstret tana and feehnelepy. Indwatrtal CnviramsHtel HONS 0 1 8 2 9 8 PC IM/ lot Inc.. flttPurpi. Cincinnati, m. ( a. Alan rf.i raja Intarla rapt. M4M PM: . MC* 4AAIA1II ip at MP Cantraet: IM-tt'OI-ITM *ntter: IN'tOO/t-lt-OP Oaaoriptara: MPtarapp aatarlain. iOtelywia. laaityOipi/pHaa>, Separation. crystallisation. AreaIpl tatlawCCwaalatry . ConoantrstianlCcapscitionl. Tacnnal- ap. Aleebele. lltpattc hyOricarbana. oiaiillatian. Centrifugal tan, Catalyota. laaifn aritarla. Araaatic ptlypciK MyPwaitaM, AMdelatee. Phaaala. Aalnee. Araaatic eaaaww, Maiapaa arpanla cawounpa. Paattcieae. evaporation. Filtration. Fleeowtat ten. Ian cinnanglnp. APaerptien. Satvant attraction, Pacarana a ntlfla a: LlaaM ueeteo. Paly^ilarinataP at tan. ntiscaaoao Olelegicai fetphanyla, tneiatrlal riptara: Pater pollution. ra*a Alvar. Sanplinf. napiana. Itpapl. Oilarina orpanic aaapaunaa. line. blcaal . leePtPeiel). Csrecwlratiwnlfapaoltionl. Carbon. Mtiragan. Saaaaapt vartatiana. tafea aicnipcn. Saciaanta feanttrtera. *aatar *lity acta, reiycnierinetep lipapia. PMMtltM PfIS Irlcaa: rc M/P AOI KvaVaatlcn at SucpeeteO Cnvlrenaantel Ocntanlnatlan a# Pa NartaP. NWilpn Araa fiavlranncntal Aratactian Ipney, Chicago. It. ONIMOtl) UNMI Ftp: 190. !, 0. in CAAtatOS Sap 0 7Tp Aapt Na: IPA-COA/4-CO'OO* aaplon V. < Pacer Iptara: Aqulfore. fbalctty. *Weter pal tut ten, Scapllng, Water supply. rataaia voter. resticipee. Araanic. CaPaiun. taapaaui). Cdlertne arpanla ceapeunao. Atpnonyi. Satis. Iiaowocftology). Pleeciay. pcaina organic coapounea. Cancantrat lerMCevpool t ton), atenigan leant If iara: PelybroelneteP btpanyla, Aipbony I /erase. PelycfiterineteP llptanyla, tpnenyl/cbtere. NeatocMMicntgan). NTIStAACIA PNMttTN MTIS Frtcaa: FC AOA/MF AOI Aslant Mater Aattty Criteria Far AalycFilarlnataP Plpdanylo tnvlronaantal Pratact ton Agency. Waaninptan. OC. Cr t tar la anp Stanparaa oiv. (Olinnil) 0114409 HM FIP: . 4F. PA. STY*. f7U. M8, AAO. 470 AAAI Oct CO 9O0p* Aapt MS: CPA*440/1*AO'OM Occcrtptcrc: Watar quality, Tealeelegy. Oilarina orpanic ca^aunpe. lovtc tolerance*. laboratory antnala. Criteria. Taalaity, water pollution, Aquatic aioloqy. Marine biology. Freed aster blalopy, ConeentretlonfCoapoottIon). fapeouro. Carctnapana. Fubtic twalth. Aiaa. Food, taper(aantal cata. PlantalAotany). Peat tetaaa leant If Iara: Taala cutoetanooe. Watar pollution effectelieaaano). water gailutlan offacialAntaela). water pollution offactbiriantal. Cnvlronnontaf beeltfi. Moat in rtafca. Maaiaua paralaatbta aapaaura. rnaraacaAinaitca. Clean water Act. Palycnior InataC blphanylc. Ctpnanol/pared loro. MIISfFAPwr OMirttutlsM ef Pali aatacy CHgaadi Of a Developing loo Untv.. Heueton. ti. Oepl. of Otology.MOeiieipei fnvlranaisntal ran La*.. Cincinnati. ON. (OINTTOII) f.AUTIND: Vtenor, to. final root. Sop 73-Doc M MIDI fid: SH. IN. 4Dd. Ill flUIIKH ttanlter: lycniertne< nTiscraoao Oklorlne organic ` Insecticides. UtroM. reat-IOBSBI AOt mas frlaae: <0rdar oa ftoDl-tOSAis. DC AtO/Mf Organoafilarlna Naldae in flahaa free the Martkuaat Atlantic Oman and Nil of Milos National Marino Manor los farvice. Seattle. MA, Nor invest and Alaeaa Manor lea Comer. (0S4MMM>> AUTMOB: Stout. Virginia f. mm fid: ia. Ado. 470. mo obalotos mIIm- MBAA-MMMOaca-a 1 Incloaad in funary Svllettn. v7S nt pGVSD I*00. Dsaariptora: cniaranymacardena. *710000. *ater pollution. Blpnanyl. Cniorino organic ooapounda. Otaifln. Deeiduea. 00T. CanaontrationtCoapaoitlanl. tiaaaaay. Morin Atlantic Ocean. Has loo Dill. Oaprinta Idantiriora: *000110100 roaiduoa. raiycnierinotod biphenyia. 0G0e0o5l7o1g0ic0a11l Survey. Indianapolis. IN. ntsr Oesoureas Olv. AUlMOC: OaOO. Linda L.; Asters, Cher las A. 7final rapt. toer*Aug t 6 4 7MMN) f Id: AH. Al. ACO. AG. GSAIOOTS toy CO 74p apt no: usos/aao/Mii-ao/om: uvas/vei-aojs fraparod In coeporailon vttn Soil Conservation Meaningten. OC. Service. Oeacriptera: *Coal oining. *dina voters. Sulfatas. Cypress Creek Vstersnod. veter pollution. Conductivity, Nutrianta. cniarenydrocarOena, Iron. Celctua oulfatas. Msgnesiuo. Mnganasa. DOT. ilpneny! coopeunds. Standards. Concantratian(Canpoaltion). Indians Identifiers: dins acid drainage, felychlormated btpnenyis. iIpkeny l/cniorol. Warrick county!Indiana). MTISOIGSVO. NTISA6SCS 0 21PM - MSI NT IS most rc AOA/af AOI Utanatlm of Meter-Soluble folyeniortnotad Biphenyia toy Cart* Matorlala IlllnolA Stole Seologtcal Survey. Urtoana.Municipal (nvlronaantal Bssoorcn lab.. Cincinnati. ON. (0I3SAA000) AurKW: Griffin, A. A.; Chian. K. S. K. final rapt. 0347504 fid: IM. Ad GOAIA034 av OO ion Grant: (ri l-MMMl O'-O Monitor: fPA*GOO/9'AO-OA7 frepared In caaearatIon vttn Ooergla Inat. er lech.. School af Civil engineering. Atlanta. OsierIptora: Hazardous vastOS. Biphenyl. Atedoterloretion. Adsorption. Chlerina organic ceapdunds. Oagradai Ion, dicrearganlsea. Saiutoiilty, Mobility, Volatility, Pollution, Sol la. Dacha, flanis(Dotany). Malar leant 1 Mara: NtISAMAoao foiycnioriiwted bipnanyia. arecier 1343. HONS 0 1 8 2 9 9 NMIltMt Nf IS frlcaa: K AO/f AOI Mater DaaMty Aaaaacaant of tea cypraee Marrtak ttotal, indite Creak tfatarmad. HONS 0 1 8 3 0 0 JM9I9 NTH Prl<asa: PC MT/V mi Mlal rat* mi IM Prtarlty MMatU l--M mm iHMRlCil iMlfPMa, RMall M *mrmmr. Mm., Spring# laid. Vi.|iwiri n ui friwtlt .............. MIW, ac. OfM mi HUT Pimwttm m ttwar*. (MMTiooo) Mma: Callahan, Miami A.; Sim*, atcfwal w. 5 --r-- a.; aay. Ira P.s Poulor. OmlM 9. Mna rapt. it*c4 pi#: iaa. aaa* auiaoti papal. Contrast: IM'M-OI-Mtl Monitor: (N.4C/4-l**On Ipgnaorpp in part ay Pram CPC-PP-01'--07. Pr*gsrad in aaapauftlpn aim W fnlarnatlanal. Pan!a Para. ca. iaa alaa --tar pollution, Tr ntrat lan<Caapaal t , Mstals. In PaatlelM. Catarina arpanla cmaam ittPtara: *Path af pollutants. Pslychlorinotsd pipnsnyls. WIS Prteaa: pc AOA/np Ml aaaaalap pp Paly--ilortnotad Ctpaanyl Py ^ptl* Caarpla Inat. a* loch., Atlanta. Cnwlrsnaonta) laiwrtti Cantor.C#f lea af Malar Paaaaren ana Tochnolsgy. --ahtnptan. OC. (OMM3MT) * Yaahnlcal aoaptaiian rapt. Oct 77-ds* CO aw Plat it. p. iTY. aao oasipoaa dan pp ftp apt Na: COC*OI*PO Caniraot; OI'i4*M*oni*nti Prafaet: OWOV-A-orj*A Monitor: MM'f|'(l) Praparac in aaaparatian aim caarpla uniw.. Imartaant tlailan. atnana. Call. Caustic Plalapy. CancsntrstlotlCmiinidw). Chlarlno organic p--owane. Cwlturoa(Olalapy). fooa --sins. tadnmnts. --tor palluttan. Baalllwo. larvoa Idontlf loro: Palychlorlnatoa hlphonylg. Otsaecwulst Ian Depuration. Wotsr pollution offaca<Anlmls). Miiioipwar ' roao-aiertc mu rrtcaa: pc mm/m 101 ! ItitrlMlci Ml turfmm Matmm mi Itmimtw, 9 NtytftiwlnttMi OlpOanyls Mim In Indiana UMw. at Cl --tar Paaaaren ana Tw Oapt. of Coalogy.*offlea of Washington. DC. (0*0--4020) AUTNM: Caatain. Mar* l. Maatsr'o maola 0IP04L9 Pla: 70. CPA. 000 May 7t P3p Contract: DI*I4-)4 000I*71M Prajaet: 0WOf-C-7S*I<71S4> Monitor: 0W0t-C-7Ml(IW|( || PPAIPOlg Mlptar*: *--tar analysts. Chlartna organic caapaunda. win pollution. cnaaical anolyala. Saapiaa. aa enroaatopraphy. Calwant attraction. Surfaca watar. CsncsntrattsnICa--Itton). Bunoff. sttaa. Indiana. Thaaao I Pant If lor: OolychlorInotsd Plphonyla. Plooaington( Indiana) *P*tti af pollutants. --tar pollution dotact ion, misoiOMPT K/C-1902 mil Prlcss: PC 003/-- AOI iiWMiim of Palychtartnatad Pip--nyts at tho OMCOP Cnwlranaantal Prataatian Oah Pldpo Caaaoua Olffusion Plant. TM.Oaportoont of Inoray Washington. OC. (4090000) AUTMM: Long. L. W. CIP9309 fd: 190. CP 7a Apr CO Pp Contract: W-740C-fNC-2C CCAIP0IC Paacrtptora: iraaatlcs. *Orgsnlc chlarlno iinnwii Cost MpO. Papulations. Wasia tgintm * laontlflors: (000/009000. C004/400000. fPOa/OCOCOI. NFISOC OTU Prtcaa: CC MAP Ml Vtacanatn tiniv.-Nii<m*aa.toti< APatntatratian, tocfcvltla. i Offlea at $# Cr* i (Mil MM at Chlttfi. IWUMMI Pinor HP (Ml., Sm lAtMta. II.*lkAlclp*l liwlrMMat limrin U.. Cincinnati. CM. IOIMIM00) MfHM: JMlti, MvMs Riatl, IwM Utol rtpi. Cat H-tn ao miimi rtii in. tic* car inr* imimi _Sca *Im ranart Patcc Mar M. MM IIMM. Iptcra: *tolM waato plapecal, MuarPoua catarlala. "M. SMpIlM. PelIwtian contra), Kncapaulattan, wirtflcKPi pnillH, IwpAM cmiti n. Cnlarlna `a aaepawnca. laaMltpr, PaatielPaa. fvaparatian. alee. Tearcal PapraPcttan IMntlflart: *SPHP ant conoponont. PtpManyla. UM pel Iwtian, NUSIMMI tolycniarinatad MIHM: Crayloo. toMort M.; toicii. totln I. OCOI4 FIP: t. PC. PCD. PIT. PT1. CIP7P lip CAAtaOIR topi to: Vlt-M-II TOI Monitor: NOAA>POOPICOT .Pto. in Taatcalopy irP AjpiiaP moroooolopy.' po pMi-ata Oaacrlptara: Tract. Moa'clty. Motor pollution. Iqh CMIorlno orpantc caapawnPa. APaarptlan. topoouro. lootopic Itol lip. Poprinta T liM*ai<aiolapy), itemilit ion. Pmi tafeoa Itontlf lora: too Pront propran. FolycniorInotoa Ptatonwla. PIpMonyl/cMIaro, Salnlliwt nocycwli. NTIWONMOA MtO*1MIH MTIS Men: PC AOP/MF AO I Cvolcatlan of Prataaala lor PoatlalPoa to PCS'a In Paw Caatocatar ^ MM*MTIM aril Prloaa; PC AOC/MP Ml tlttla (ArtMwr O.). Inc.. CatortPpe. Ml. Municipal CnviranMantal toaaarch la>.. Cincinnati. 0M. (otaaaaooo) MiTara fralMtiaa anP Taamicot Aaatatanaa Oapart TA m*M, MUM *Uta Capartcant M Mal. Plara PaMlic --r~~ir. Billing, Mataa '' Matlanal ll. far Occupattanat tefaty aMHaalM. Ciwimati. CM. toalth Maaarp anC Taanlcal Aaaiatanea Prancfi. ( OIMMOIt) mill PIP: M. CT. ITU. PTT. to. AM PCAIPOIS Pact to: MOaM*fM/TA*Tp*W .Saw alaa rapart patap An TP. MM*llMM.. MITMM: Carapay. Alaprla final rapt. Jun*0ct Ta OCAIlf ftp: TO. CCO. CCA npv ic itap Contract: (II M*0I*M|7 Monitor: CPA/COO/l-Tf'iaP mini, mi lip t. CPAICOII Ooocrlptors: ppatlclpaa. Motor anatyata. tooapa troatcont. maclcal analyafa. toapiInp. tolvant attraction. too rtirniiipct,. Naso cwronotopropny. Soporat Ion. Concontrotlo* MCoopooitloo). cnlarlna orpanic coopomdo onorlptara: MMfraawa catarlala. inpwatrial aaciclna. tMpaawra. Taaialty. Critarla. Inapaatlan. ttatorai. PaaaaanPatlcna. Inpwatrial Myplana. Cancantration<Caapooitia* Ml. Snap! inp* Caniaclnanto. Chtarina trpanff caapawnPa IMantlflora: MTtUbAOCP tolycMIorlnotOd bipMonvls, FrocoPuroo IPMtlf tara: Taolc auoataneaa. MapiMwwl aafaty c toaltM, Air aaapl lap. till inpstMantonal. tolyeMar intn PtpManyla* IfflMMpl HONS 0 1 8 3 0 1 MM-IIIMI V|t Prtoaa. PC Ml IXMi anP toatrlPwliaM p CcvclPplMP IJM Tract m-TairatoUrtolpf! HONS 0 1 8 3 0 2 8i*ll 8M/VIT NTIf PrtoH: PC M/V AOI lN(a qf Up--It (Vpp-- Mm) IM -- m -- t-- Tat--ad mmm (*<--! pro--I--'I liwir--ifl limrw lap.-Oulwtft. m. C--740001 mtm*: Mm. O. 1-: --tf. |. o.s Carlmm. I. v. --I art tala nmci FM: AT. AT. AC. ITT. IN. 172 CMIlttl t Apr 71 Ip apt M: (M/o/^7l/lN --Mv; M . la *i. a# Ua 7a--riae Maooarcn --art af cm*. i7 p--t-iooa irra. iiwifi in franco._ vN Oescrfptrs: *f ta--a. --Hanna, TmImI--, floasaaya. f *--rlaental Mta. larva#. Caneentretion<Cda--slttenl. --tea. Fe--lea, --t --Hut tan ITtlllart: *fq*ic --taneaa, Poly--Ir looted lipawyli. Oleeeeuau latlan, --tr -- Mutton effectelAnlaela), MIUNM PP'tM AQ3/0ST MIS Prior: PC AfO/NF Ml PelyaMrt--lap Up----la; --lait --tr quality CrltTta (iwtraamitl Protecttan afancy. Vaahlngtai, OC. Criteria and TIT-- 7110 ItP: II. W, M. ITT*. |7U. --8*. 1*71 -- Monitor: If MO. 470 MI Doorfpioro: *Watar --al ity, taalcolagy. (Maiw trpfilt coapauna. Peatieldaa. Taaic toiarancaa. taaoratory anioala. Crttria. Taa laity. Motor pol lutton, Aquatic aiaiopy. Marina Olalapy. Troon aatT aiaiopy. Concantrot lowIC--n 11 Ion). Capaaura. Carcinopo--. PwPilc hoalth. fiaa, loot, i--rioantal aato. Planta40atany) 1--ntlftre: *1#aic a--atancoa. **aar pa Mot ion affects!--Mona). Matr pollution affacta<Antaats>. tfatar --nation aTT--ts(Pianta). Inutra--ante! Maaitn. M--itti rtaaa. Maalaua paralaaiaia eapeeure. P--aaaainatica. Claan vatar Act. NTISIPAOMP PI*9-- T4I/I9T MTIf Prior: PC AI3/MT --I Selected --It --tlity --oar-- r fan-- --a-- --taro. it7i --tr for; Hipmimi n iaaii --iita. fiaaali-- --loan. Minor Cl< |teat --alyooa laa-- -- tT --vatapaant aaotan. ta. Awatln.**--olapleal Survey. MIT--M: Scnulsa. --an A.; Oupwy. Alton <1-: Anraaal r--t. --t TO-Sop Tl Tl--tMf n: I--. -- CBAIT--O Aup 71 tip a--t --: TM/l'iTi ManMr: 11 Prepared Oy --al--leal Survey. Oaatan. VA. NcP--raon, (aa --scrlptra: Surface win, --tr --Hut Ian. *Teaa. --tala . (ana. Aloe--aical ay--n Oaaana. Oxypn, OiimIvm --aaa. Past tel--a. 01--any la. Cnlrlno orpanic eoape--. CancentratlanlCoapealtian). r--naia. turPidlty. faeiealOata) leantitiara: Paiycniri--too at--onyis. *atr puoitty --to. NllSStPS PI-2-- 070/OST NT1S PrtCOO; PC A--fm AOI Tram Orpanlo Analyala: A Maw Tr--Mr in Analytical ChanI atry --tie--t --ram or Standards, ttasftlngton. OC. 1240 001 AU7M00: Hartt. --rry S.j Chaalr. Sta--N. Tt--l r--. TIA0ST4 TIP: 70. AM. 01. --A*. M. MM, S70. --V GAAlTAtA A-- 70 TA-- A--t --: --S/SP-ftt Monitor: IA Procootfinpa of tho -- tortols --aoaren Syapooluw (tth) Hold at Oalthor--rg. llrylond on April 10-13. 1*70. library of Conproaa catalop card no. Tt-OOOOC1. --aorlptra; *--00010 caapounda. Trace eleaents. *chaalcal analyala. --!tnpa. liactrac--alatry. Sa--ilnp. Mutrtants. (caayataa, Oru--. Taatctty. ftoaaoay. food additives. Gas chranalapr --i . --aa a--ctroacapy. Otaloplcal iracta. Moraonaa. Invlronwaotat surveya. Aaa analyala. Ualr analyala. Aramtie --lycyallc Oydrocaraona. CarponyTatas, Sail analyala . CMto--taanoc, Peat ic Idaa. Pantanaa. Concantrot lonicoa--ei~ tlanl. Araaala. t tatuaalflolopyl Idantlflrs: Air -- Motion datact ion. --tr --Mutton detection. liquid --rratogra--y. Staid of the art. Polycnirinalad Olpnonyls. Vltaain i. Mlpfi prforaonco liquid CUTS-- tapr--y. Wapana. Nf ISC--S