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PR0535342
EnvironmentalHealth
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4700 - Waste Tire Program
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PR0535342
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PR0535342
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Entry Properties
Last modified
7/29/2020 5:32:38 PM
Creation date
7/22/2020 8:36:59 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4700 - Waste Tire Program
RECORD_ID
PR0535342
PE
4740
FACILITY_ID
FA0020390
FACILITY_NAME
RENEWED RESOURCES CORP
STREET_NUMBER
29425
Direction
S
STREET_NAME
MACARTHUR
STREET_TYPE
RD
City
TRACY
Zip
95376
APN
25312026
CURRENT_STATUS
02
SITE_LOCATION
29425 S MACARTHUR RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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SJGOV\gmartinez
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EHD - Public
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AUG-17-19'98 08:71 FPLN P-JBL I C HEALTH SERO?CES TO 9'1e:DJ1-�3 H. <br /> ' AUG-1- <br /> -19re 09:21 FF.Ut'1 JA :ittjH"3!L 4'lL:t4 _i 7 7Y0.}J4GJ <br /> LEA Advisory #46 <br /> November 6, I997 <br /> Pale 3 of 8 <br /> fragMentation will be rapidly convened into secondary products. Several aromatic and cvChe <br /> compounds by means of the Diels-Aldrr reaction are also produced. ix <br /> 11 1185 been Shawn that open burning. regardless of feed stock or fuel, results in greater mutagenic <br /> emission factors than does controlled combustion provided by incinerators,boilers,cement lcilrrs, or <br /> other combustion devices. Chunk tires produce higher burn rates and marc potent organic emissions <br /> than do shredded tires.. The mutagenic emission factor for tete open burning of tires was 3-4 orders of <br /> magnitude greater than that for the combustion of ail,coal. or wood in a utility boiler. x <br /> Airborne Emissions <br /> All tire fires may vary and the exact emisrivns=dcwrcentratriom ca=iTwt be predicted. There are many <br /> factors that influence the ernissions produced while the fire is Darning. Some of these Factors include the <br /> amount of fuel. fire temperature,nietervlogia conditions,topography of the area.etc. to most cases <br /> airborne emissions focmd will include volatile organics,semivelatile organics(including polycyclic <br /> arcrnatic hydrocarbons(PAH)), carbon monoxide,attd p+trticulate matter,which includes metals. <br /> In 1983,the National Institute of Oavpational Safety and Health (NIOSH)evaluated a fimcontaining <br /> appmximately 5 ntillion tires. This fire,called the Rhinehart Tire Fire.covered a 4-acre site and created <br /> a black Flume of smoke approximately 3,000 feetiTigh aad 30-50 miles long. The NIOSH evaluation <br /> showed no acute hazard for employees performing containment end cleanup operations. Airborne <br /> mr.�i(nring of:fie ptnme indicated the prescsice of rar6va rnvnosido(SO-100 pgm), PAH(58-6502 <br /> ngiin3), metals(all below 2 ug/m3 except lead,zinc,and iron),total organic compounds(0.73-0.8I <br /> rnVm3 ), and nitrosamine(below laboratory detection limits). (See report for mare specific emission <br /> Lula iuforrnativn.) The potential for excessive inhalarion expostue to PAHs and carbon monoxide and <br /> dermal absorption of heavy acetals,primarily zinc and kad,were reported as exposure concerns. <br /> Voistiic organic sniissiwls wcra dete1.icd Jul ill*01c 16-mre Pancc-re Tire Fire,which tT med 3-5 million <br /> tires within a steep-sided box canyon. $cnzene concentrations did not exceed OS KA aril NIOSH <br /> allowable exposure levels when sampled on two different days at a location 50 feet dowrtwind of the fire. <br /> ;Measured benzene ltrveis ranged from .43-.50 mg/10. Airborne emission sampling also detected,not <br /> significantly, FAHs,metals,and sem. volatile organics(see report far mote specific emission data <br /> infannation). These concentrations did not exceed regulatory allowable exrAlsalre Ir'VIS Sampling <br /> points were 50 feet downwind,50 feet upwind and west and east of The visual smoke pltuae.xl <br /> Subsequent industrial hygiene monitoring of Hoard personnel many wvcks after the fire had bean <br /> ertanguishtd indicated no omploycc 4ycrclposvrc. $sn1P1in91v-suks ii dicatcd no detectable <br /> hydrocarbons or heavy metals dust(7-inc,cadmium,C}frvmium,and lean)_ Vic breathing zone sampits <br /> were taken during site supervision and the soil sampling process. Air monitoring results of employees <br /> performing remediation activities,specifically scraping barn residues from the canyon walls onto the <br /> floor, showed the presence of nuisance particulate(.31-i 1 mg/M3 ),zinc(<0.002-1 I tngfm3 ),and FAHs <br /> below their detection limits(See report for more specific errii«ion data information). xtt <br /> [It a controlled burn chamber simulating open burning of scrag tires,a fl.5. EPA report estimated <br /> emissions of sentivolatile organics ranged from 10 to 50 SU of tire material burned. It is likely that <br /> emissions tnoasumd during Ibis study characterize an actual fare,but the sirnilarity of actual gaseous <br /> concentrations and estimated emi5ssions may not be reprewtativ[. The predominant ernis'sion products <br /> ideirtifed.vere rnonoarornatic and polyaromatic hydrocarbons. The plresencc of bcnzo(a)pYlcsrC in <br /> particulate inxtracts is notable because of the compoutrd's carcinogenicity. High emissions of other <br /> coinpotinds, particularly benzene, with concentrations often exceeding I ppin, may pose a significant <br />
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