### Air Quality Monitoring Network Plan – July 2009

D-1 APPENDIX D



## SOUTH COAST AIR QUALITY MANGEMENT DISTRICT LEAD (Pb) MONITORING NETWORK PLAN

JULY 2009

Prepared by

Rene M. Bermudez Principal Air Quality Instrument Specialist

Philip M. Fine Atmospheric Measurements Manager

### Air Quality Monitoring Network Plan – July 2009

D-2 

## Introduction On November 12, 2008 the Environmental Protection A gency (EPA) issued final revisions to the National Ambient Air Quality Standards (NAAQS) for lead (Pb). EPA revised the level of the primary standard from 1.5 micrograms per cubic mete r (μg/m 3 

### ) to 0.15 μg/m 3 

### , measured as total suspended particulates (TSP), and revised the secon dary standard to be identical in all respects to the primary standard. EPA also promulgated new mon itoring requirements including new design requirements for the Pb NAAQS surveillance network. Monitoring is now required for all Pb sources (source oriented monitoring) that may contr ibute to violations of the Pb NAAQS and/or emit more than 1 ton/year of lead. Monitoring is a lso required in large urban areas for Pb as part of a non source-oriented surveillance network. Acc ording to 40 CFR Part 58 Appendix D, monitoring agencies are required to begin source-or iented monitoring by January 1 st 

### , 2010 and are required to identify Pb sources to be monitored and sampling locations in the annual network plan submitted by July 1 st 

### , 2009.



## Public Comments Pursuant to Federal regulations, this plan is to be made available for public inspection and comments for at least 30 days prior to submission t o U.S. EPA. Hard copies of this document were made available on June 1, 2009 at the South Co ast AQMD Public Information Desk in Diamond Bar, CA. The document was also posted to t he public South Coast AQMD website at www.aqmd.gov on June 1, 2009, with links under the South Coast AQMD home page titled “Current Programs, Events and Topics.” Links to th e document are also provided in the “Air Quality” area of the website. The draft document will also be made available to U.S. EPA during this period for review.



## Monitoring Objectives The primary objective for the Pb monitoring network is to provide data on the ambient Pb air concentrations in areas where there is the potentia l for violation of the NAAQS. Revisions to the primary and secondary NAAQS for Pb provide requisit e protection of public health and welfare respectively. Modifications made to the existing ne twork design requirements for the Pb surveillance monitoring network will help to achiev e better understanding of ambient Pb air concentrations near Pb emission sources and to prov ide better information on exposure to Pb in large urban areas.



## Methodology EPA has elected to continue use of current Pb-TSP F ederal Reference Method (FRM, 40 CFR part 50 Appendix G), sampler with no substantive ch anges. The current method is based on the use of a high volume TSP FRM to collect a particula te matter (PM) filter sample and the use of EPA-approved Pb analysis methods. Upon data submi ssion, monitoring agencies must now report the average pressure and temperature during the twenty four hour sample period, and report Pb concentrations using actual flow, rather than standard flow.



## Monitoring Requirements New network design requirements specify that monito ring agencies conduct ambient air Pb monitoring near sources that have the potential to cause Pb concentrations in ambient air in excess of the new NAAQS (0.15 μ g/m 3 

### , 3-month average). Agencies are required to have at a minimum, one source-oriented State and Local Air Mo nitoring Station (SLAMS) site located at

### Air Quality Monitoring Network Plan – July 2009

D-3 the maximum expected Pb concentration in ambient ai r resulting from each Pb source that emits 1.0 or more tons/year based on the latest EPA Natio nal Emissions Inventory (NEI) or other scientifically justifiable method or data. The mon itoring location is to be determined based on the modeled the point of maximum impact, taking int o consideration population exposure and logistical considerations. EPA requires at a minim um, one non source-oriented monitor in every Core Based Statistical Area (CBSA) with a populatio n of 500,000 people or more with 15% collocation for all monitors. These monitors are t o be placed in neighborhoods within urban areas impacted by re-entrained dust from roadways, closed industrial sources of Pb, or other fugitive dust sources of Pb. EPA is allowing monit oring agencies to stagger installation of newly required monitors over a two year period. Monitori ng agencies are required to install and operate the required source-oriented monitors by Ja nuary 1 2010. The non source monitors are required to be installed and operated by January 1 2011. The annual monitoring plan due July 1, 2009 must describe the planned monitoring that will begin by January 1, 2010 and the plan due July 1, 2010 must describe the planned monitoring t o take place January 1, 2011. The minimum sampling frequency for the monitoring network remai ns at the current 1-in-6 day sampling frequency.

Background South Coast AQMD currently collects TSP Pb measurem ents at 10 sites (with two sites collocated) as part of an ambient Pb network. This established network meets the EPA requirements for the non source-oriented monitoring network. The spatial distribution of these sites is shown in Figure 1.

In 1990, U.S. EPA requested that the South Coast AQ MD collect ambient air particulate Pb samples near several large Pb handling (battery rec ycling) sources. Long-term source oriented monitoring began in 1991. Quemetco RSR in the City of Industry exceeded the previous federal ambient particulate Pb standard of 1.5 μ g/m 3 

### during the second quarter of 1991. Lead monitoring ended at Martin Brass Foundry Inc. in th e City of Torrance during 1993 when measurements were consistently below the ambient st andard. Sampling also ended at Quenell Enterprises Inc. in the City of Commerce in 2006 wh en the monitoring site was redeveloped. The facility is now owned by Exide Inc, and has rep orted emissions of 0.03007 tons/yr.

South Coast AQMD currently conducts source-oriented monitoring at three facilities. At Exide Inc. in the city of Vernon, Pb emissions are report ed as 1.998 tons/yr and sampling is currently conducted at two sites identified as “Rehrig” and “ ATSF”. The Rehrig location began sampling in November 2007 in response to a request from AQMD compliance staff. The Rehrig site began monitoring on a 1-in-6 day schedule, but samp ling frequency at Rehrig and ATSF was changed to either 1-in-2 or 1-in-3 day between Febr uary and May 2008, and the Rehrig site began daily sampling in May 2008. The monthly aver ages at Rehrig for December 2007 through April 2008 exceeded 1.5 μg/m 3 

### . The results of sampling near Exide are summarize d in Table 1. Monthly averages at Rehrig continue to exceed the n ew Pb NAAQS of 0.15 μg/m 3



### . At Quemetco in the City of Industry, monitoring emi ssions are reported as 0.321 tons/yr and sampling is currently conducted at one site identif ied as “Closet World”. This location monitors on a 1-in-6 day sampling schedule and no exceedance s of the previous 1.5 μg/m 3 

### Pb NAAQS have taken place since 1991. Monthly averages last exceeded the new standard of 0.15 μg/m 3 

### Pb

### Air Quality Monitoring Network Plan – July 2009

D-4 in 2005. In 2006, monthly averages ranged between 0.02 and 0.10 μg/m 3 

### . Sampling did not take place in 2007 and most of 2008 due to the loss of a ccess to our sampling location.

At Trojan Battery in Santa Fe Springs monitoring em issions are reported as 0.0145 tons/yr and sampling is conducted at one site identified as “UD DH”. The UDDH site operates on a 1-in-6 day sampling schedule and no exceedances of the 1.5 μg/m 3 

### Pb NAAQS have taken place since 2006. The highest monthly average since 2006 was 0 .23 μg/m 3 

### occurring in May 2007. Since September 2007, all monthly averages have been belo w the new Pb NAAQS of 0.15 μg/m 3



### .

Pb Sources and Emissions EPA National Emission Inventory data from 2005 repo rts that there are three sources of Pb in South Coast AQMD that emit more than 1.0 ton/year ( Table 2). In contrast, the most recent data from South Coast AQMD annual emissions reports (200 6-2007) shows only one source greater than 1.0 ton/year (Table 3). The Quenell Enterpris es facility in the City of Commerce, now owned by Exide has emissions of 0.03007 tons/year a nd Quemetco RSR has reported emissions of 0.321312 tons/yr. Based on these recent emissio ns reports, Exide is the only non-aviation source currently emitting over 1.0 ton/year. The n ew monitoring guidance also requires general aviation sources to be monitored if Pb emissions ex ceed 1.0 ton/yr. General aviation aircraft use leaded aviation fuel and have been identified as a source of Pb emissions. The EPA Technical Support Document, “Lead Emissions from the Use of L eaded Aviation Gasoline in the United States” reports Pb emissions estimates for the gene ral aviation Pb sources across the country. Of these sources, one is located within South Coast AQ MD boundaries; the top five airports above 1.0 tons/year are shown in Table 4. Estimates for airport emissions of Pb for Van Nuys Airport are given as 1.4 tons/year. Current plans are to f ind a suitable location on the grounds of Van Nuys Airport or adjacent property at which to monit or for Pb. The monitor will be sited as close as feasible to the blast fence where the majority o f piston-driven aircraft begin their take-off. Talks are underway with airport management and surr ounding businesses to secure a location, and monitoring is to begin before the end of 2009. The current and planned source-oriented Pb monitoring network site information is included in Table 5 and depicted in Figure 2. Even though Quemetco and Trojan Battery emit less than 1 .0 ton/year Pb, and recent data does not suggest potential exceedances of the new Pb standar d, AQMD will continue monitoring in the coming year to demonstrate compliance with the new Pb NAAQS at these sites.

Rule 1420 Monitoring On September 11, 1992 South Coast AQMD adopted Rule 1420 in order to reduce emissions of lead from non-vehicular sources. The rule applies to all persons who own or operate facilities that use or process Pb containing materials such as primary or secondary Pb smelters, foundries, lead-acid battery manufacturers, or recyclers and l ead-oxide, brass and bronze producers. Requirements include a provision that all facilitie s that process more than 10 tons of lead per year must install, maintain, and operate ambient ai r quality monitoring equipment. Any facility that processes more than 2 tons per year, but less than or equal to 10 tons of Pb per year must determine ambient Pb concentrations by either monit oring or dispersion modeling. Air quality samples must be collected using approved equipment from a minimum of two sampling sites at or beyond the property line of the facility where m aximum ground level Pb concentrations are indicated by air dispersion modeling calculations. Samples are to be collected for 24 hours consecutively for 30 days, and thereafter every 6 th 

### day. Continuous recording of wind speed and

### Air Quality Monitoring Network Plan – July 2009

D-5 direction is required during sampling periods using approved equipment. Samples are submitted to an approved laboratory for analysis. Results ar e reported to South Coast AQMD each calendar quarter and any exceedances are reported w ithin 24 hours of the completed sample analysis.

Results of Rule 1420 sampling conducted by Exide sh ow two occasions between December 2007 and May 2009 when monthly averages were greater tha n 1.5 μg/m 3 

### (Table 1). During January 2009 the North (N) site recorded a monthly average of 1.55 μg/m 3 

### and in March 2009 the monthly average was 2.08 μg/m 3



### . Rule 1420 sampling conducted at Quemetco shows the highest monthly average value recorded between February 2007 and February 2009 was 0.76 μg /m 3 

### just inside the fence line. Monthly means of values taken on the property of Quemetco a re given in Table 6.

Since Rule 1420 monitors are operated by the facili ties and are often located on facility property within the fence line, data collected may not meet the definition of “ambient” and siting may not conform to relevant EPA siting criteria. Therefore they are not designated as SLAMS sites at this time. However these sites will provide data t o aid in the enforcement of regulations designed to meet the new Pb standard.

Source-oriented Monitor Siting Source-oriented micro-scale sites are to be located at the site of maximum ambient impact, taking into account population exposure and logisti cal considerations. In practice, this generally equates to monitoring at the fence line or beyond a t a site that is as close as feasible to point of highest modeled concentrations. Modeling was compl eted for each of source-oriented locations indicating the expected location of maximum impact for Pb. Dispersion modeling for each facility was performed using AERMOD (version 07026) to determine the monthly lead concentrations. The AERMOD default regulatory optio n was used and building downwash was included. AERMAP was used to determine the terrain base elevations for each receptor and source and a hill height scale value for each recep tor. AERSURFACE was used to determine the surface albedo and surface roughness. A Bowen ratio of 1.0 was used, instead of the AERSURFACE output value. This was done because the National Land Cover Data (NLCD) 92 dataset does not include the recent land developmen t projects that occurred within Southern California, which would result in a lower Bowen rat io. AERMET was used to develop the necessary meteorological data for each project usin g the meteorological data from the appropriate monitoring station and upper air soundi ng data collected at the Miramar Naval Air Station. A 100-meter by 100-meter receptor grid cen tered on the facility was used, as well as fenceline receptors placed using 25-meter intervals . All facility boundary, source parameters, and emission rates were obtained from the most recently submitted (Health Risk Assessment) HRA for each facility.

Using the U.S. EPA’s post processor, the maximum 3- month rolling average lead concentration was calculated. The results are plotted in Figures 3, 4 and 5.

### Air Quality Monitoring Network Plan – July 2009

D-6 Exide The most recent Health Risk Assessment (HRA) for Ex ide was prepared in June 2007 using the emission inventory for the 2005/2006 inventory year , which reports a total facility emission of 1.16 tons of lead per year from 18 on-site emission points. The meteorological data from the Lynnwood monitoring station was used. The maximum g round-level lead concentration is 0.88
μ g/m 3 

### and is shown in Figure 3 along with current monito ring locations.

South Coast AQMD will continue to monitor at the Re hrig and ATSF locations. The current sampling schedule for Rehrig and ATSF are daily, an d 1-in-3 respectively. These schedules may be changed over FY 2009-10 to 1-in-6 depending on c ompliance needs. South Coast AQMD may relocate the ATSF sampler in FY 2009-10 to a lo cation closer to the facility where higher concentrations are expected.

Quemetco The most recent HRA for Quemetco was prepared in Ja nuary 2009 based on source tests performed in November 2008. The HRA reports total facility emissions of 0.15 tons of lead per year from 10 on-site emission points. Although the facility includes an on-site meteorological station, the data collected at the station is not s ufficient to use in AERMET. Therefore, the meteorological data from the La Habra monitoring st ation was used. The maximum ground-level lead concentration is 0.03 μ g/m 3 

### . Using the post processor, the concentrations are rounded off to two decimal places. Therefore the maximum lead con centration is not identified at a particular point as there are five receptor locations with the same maximum concentration. Instead, the maximum lead concentration is represented by an are a bounded by the 0.03 μ g/m 3 

### isopleth in Figure 4.

South Coast AQMD will continue to monitor at the Cl oset World location downwind of Quemetco. The current sampling site is located wit hin the maximum modeled isopleth and cannot be located closer to the fence line due to t he proximity of a flood control channel. The Closet World location currently monitors on a 1-in- 6 day schedule.

Trojan Battery Modeling for Trojan Battery was based on the emissi ons reported for the 2006/2007 inventory year, which reports a total facility emission of 0. 04 tons of lead per year from one on-site emission point. The meteorological data from the Ly nnwood monitoring station was used. Since no stack parameters were available, the default par ameters for SCC 31306505, obtained from the US EPA, were used. The maximum ground-level lead c oncentration is 0.04 μ g/m 3 

### . Using the post processor, the concentrations are rounded off to two decimal places. Therefore the maximum lead concentration is not identified at a p articular point as there are two receptor locations with the same maximum concentration. Inst ead, the maximum lead concentration is represented by an area bounded by the 0.03 μ g/m 3 

### isopleth in Figure 5.

South Coast AQMD currently monitors for Pb adjacent to Trojan Battery at a site designated as UDDH. The sampling location is as close to the hig hest modeled concentration area as possible given logistical siting constraints. Sampling will continue to confirm that Pb levels continue to remain below the new Pb NAAQS of 0.15 μ g/m 3 

### . Since emissions from this facility are much

### Air Quality Monitoring Network Plan – July 2009

D-7 lower than 1.0 ton/year, and two years of data show no exceedances, this site may be discontinued in FY2009-10.

Pb Non Source Monitors

Non source-oriented monitors are located in urban a reas to gather information on general population Pb exposure. One non source-oriented mo nitor is required in each CBSA with a population > 500,000 as determined by the most rece nt census data. South Coast AQMD currently operates a non source-oriented monitoring network of 10 locations with three collocated sites detailed in Table 7 and depicted i n Figure 1. South Coast AQMD’s current Pb monitoring network exceeds the minimum required mon itoring as part of the final revision to the NAAQS for Pb. Any redesign of this network will be addressed in the 2010 Annual Network Plan.

### Air Quality Monitoring Network Plan – July 2009

D-8 TABLE 1 Exide Monthly Average Pb Concentrations

Month ATSF 1 

### Rehrig 1 

### ATSF 2 

### SE 2 

### SW 2 

### NW 2 

### NE 2 

### N 2

December, 2007 0.16 1.97 0.25 0.33 0.90 January, 2008 0.17 2.88 0.20 0.42 1.14 February, 2008 0.23 2.50 0.23 0.35 0.97 March, 2008 0.25 2.09 0.33 0.17 0.28 April, 2008 0.18 2.28 0.24 0.17 0.19 May, 2008 0.13 0.90 0.22 0.16 0.18 0.77 June, 2008 0.11 0.60 0.16 0.10 0.18 0.57 July, 2008 0.14 0.61 0.19 0.14 0.31 August, 2008 0.20 0.80 0.25 0.32 0.27 September, 2008 0.17 0.95 0.24 0.18 0.34 October, 2008 0.17 0.74 0.23 0.16 0.36 November, 2008 0.13 0.70 0.24 0.19 0.28 December, 2008 0.06 0.94 0.10 0.35 0.25 January, 2009 0.07 0.35 0.11 0.34 0.32 1.15 1.55 February, 2009 0.08 0.32 0.10 0.10 0.15 1.08 1.21 March, 2009 0.08 0.59 0.12 0.07 0.17 1.07 2.08 April, 2009 0.09 0.54 0.09 0.07 0.15 0.83 1.31 May, 2009 0.05 0.16 0.12 0.12 0.23 0.75 0.86

1 South Coast AQMD Monitor
2 Rule 1420 Monitor All values in μg/m 3



### TABLE 2

2005 U.S. EPA National Emission Inventory Data

NEI SITE ID NEI Facility Name Category 2005 NEI v 2 Emissions (tons/yr) City

NEI21201 QUEMETCO INC Lead Compounds 1.935600987 CI TY OF INDUSTRY

NEI21202 QUENELL

ENTERPRISES INC Lead Compounds 1.9334615 COMMERCE

NEI2CA124838 EXIDE

CORPORATION Lead Compounds 1.62809 VERNON

NEI20307 BP WEST COAST

PRODUCTS LLC CARSON Lead Compounds 0.78605 CARSON

NEI22117 JOHNSON CONTROLS

BATTERY GROUP Lead Compounds 0.4499375 FULLERTON

### Air Quality Monitoring Network Plan – July 2009

D-9 TABLE 3 South Coast AQMD Lead Inventory 2006-07

Facility Id Facility Name Category Emissions (lb/yr) Emissions

(tons/yr) City

124838 EXIDE

TECHNOLOGIES Lead

Compounds 3996.75 1.998375 Vernon

8547 Quemetco, Inc. An

RSR Corporation Lead

Compounds 642.6247 0.321312 City of Industry

800436 Tesoro

Corporation Lead

Compounds 309.5451 0.154773 Wilmington

800089 Exxon Mobil Oil

Corporation Lead

Compounds 182.8288 0.091414 Torrance

11192 Hi-Shear Corp Lead Compounds 170.2574 0.085129 Torrance



### TABLE 4 Airport Specific Estimates of Pb Emissions 1

FIPS 2 Airport State County Airport Name Tons/yr
06037 VNY CA Los Angeles Van Nuys 1.4

08005 APA CO Arapahoe Centennial 1.2

04013 DVT AZ Maricopa Phoenix Deer Valley 1.1

12117 SFB FL Seminole Orlando Sanford 1.0

12127 DAB FL Volusia Daytona Beach International 1.0

1 Source: Lead Emissions from the Use of Leaded Avia tion Gasoline in the United States, EPA420-R-08-020 (2008)
2 Federal Information Processing Standards Code



### TABLE 5 South Coast AQMD Source-Oriented Monitoring Facilities

Source Address Facility ID South Coast Inventory ton/yr Start Date Schedule

Exide Technologies 2700 S Indiana St. Vernon, CA 90058 124838 1.998375 4/91 1-in-6

Quemetco RSR 720 S 7th Ave. City of Industry, CA 91746 8547 0.321312 1991 1-in-6

Trojan Battery 9440 Ann St. Santa Fe Springs, CA 90670 21872 0.042768 11/92 1-in-6

Van Nuys Airport 1 16461 Sherman Way. Van Nuys CA, 91406 12127 2 1.4 Planned 2009 1-in-6

1 Data Source: Lead Emissions from the Use of Leade d Aviation Gasoline in the United States; EPA420-R- 08-020 October 2008
2 Federal Information Processing Standards Code (FIP S)

### Air Quality Monitoring Network Plan – July 2009

D-10 TABLE 6 Quemetco Monthly Lead Concentrations for the Period Sept 2007 to Feb 2009

Statistics Monitor #1 Monitor #2 Monitor #4 Monitor #5

Minimum (μg/m 3 ) 0.14 0.14 0.07 0.07
Mean (μg/m 3 ) 0.28 0.22 0.13 0.40 Maximum (μg/m 3 ) 0.51 0.33 0.20 0.76
Number of monthly means 16 16 16 16
Standard deviation (μg/m 3 ) 0.13 0.05 0.04 0.19
95% confidence interval (μg/m 3 ) 0.22-0.34 0.18-0.25 0.11-0.15 0.31-0.49



### TABLE 7 Non-Source Lead Monitoring Locations

Location Site Code ARB No. AQS No. Start Date Schedule Compton 2 COMP 70112 060371302 11/08 1-in-6 LAX Hastings LAXH 70111 060375005 4/04 1-in-6 Long Beach 3 (North) LGBH 70072 060374002 10/62 1-in-6 Los Angeles 3 (Main) CELA 70087 060371103 9/79 1-in-6 Lynwood 1 LYNN 70084 060371301 10/73 1-in-6 Pico Rivera #2 PICO 70185 060371602 9/05 1-in-6 Riverside 3 RIVM 33146 060651003 10/72 1-in-6 Rubidoux RIVR 33144 060658001 9/72 1-in-6 San Bernardino SNBO 36203 060719004 5/86 1-in-6 South Long Beach SLGB 70110 060374004 6/03 1-in-6 Upland UPLA 36175 060711004 3/73 1-in-6

1 Site Closed on 10/30/08
2 Replaced Lynwood AMS on 11/05/08
3 Collocated sitesAir Quality Monitoring Network Plan – July 2009D-11UplandSan BernardinoLos AngelesPico RiveraRubidouxLAX/HastingsRiversideLynwood1Compton2Long BeachLong Beach SouthJune 2009 Review1Site closed on 10/30/082Site replaced Lynwood 11/05/08Air Quality Monitoring Network Plan – July 2009D-12+ Van Nuys Airport+ Quemetco+ EXIDETrojan Batteries +(EXIDE)June 2009 Review

### Air Quality Monitoring Network Plan – July 2009

D-13 Figure 3 Exide Maximum Modeled Pb Locations

### Air Quality Monitoring Network Plan – July 2009

D-14 Figure 4 Quemetco Maximum Modeled Pb Locations

### Air Quality Monitoring Network Plan – July 2009

D-15 Figure 5 Trojan Battery Maximum Modeled Pb Location

## Copyrighted page/s removed. Copyrighted ma terial is not available in Regulations.gov since it may not be reproduced without consent of the copyright holder.

Contact the EPA Docket Center’s P ublic Reading Room to view or receive a copy of this document.

Requests for copies may be made as follows:

In person/writing: Environmental Protection Agency, Docket Center 1301 Constitution Ave NW, 2822T, Room 3334 Washington, DC. 20004

Telephone: 202-566-1744

Fax: 202-566- 9744

Email: docket-customerservice@epa.govAir Quality Monitoring Network Plan – July 2009D-17

### Air Quality Monitoring Network Plan – July 2009

D-18 

# Site Survey Report

Siting Information

Site Name: Exide Date: 6/30/2009 State Code: NA AIRS Number: NA

Latitude:  Longitude: 	



 Elevation (m): 55 Address: 2700 S Indiana St. Vernon, CA 90058 Senior AQIS: Albert Dietrich Site Technician: TBD Site Phone: N/A

Operating Agency: South Coast AQMD


## General Siting Conditions

Station Temperature Traffic Topography Predominant Wind Direction: SW Controlled: No Description: Residential Sit e: Level Arc Air Flow (Deg): 360

Recorded: No Distance: 30 m Region: Level Probe Last Cleaned Date: N/A

Count (Veh/Day): QA Manual Manifold Clean: N/A

Meteorology Non-vehicular Local Sources Approved: Yes Cleaning Schedule: N/A

Located With Instruments: No Description: Trai n Agency: South Coast AQMD Autocalibrator Type: N/A

Distance: 5 m Urbanization: Suburban Site Survey Complete: Yes

Direction: surrounding Ground Cover: Asphalt / Gravel Logbook Up To Date: Yes



## Action Items

Comments

### Air Quality Monitoring Network Plan – July 2009

D-19 

# Detailed Site Information

Site Name Exide AQS ID (AIRS #) N/A GIS coordinates Latitude:  Longitude: 

 Location Train yard Address 2700 S Indiana St. Vernon, CA 90058 County Los Angeles Dist. to road 30 m Traffic count Groundcover Asphalt/Gravel PEP audit? N/A NPAP audit? N/A Flow audit? N/A Representative Area 31100-Los Angeles-Long Beach-Sa nta Ana Pollutant TSP- A Rehrig TSP- B Rehrig TSP- C Rehrig TSP- ATSF Monitor obj REPRESENTATIVE CONCENTRATION REPRESENTATIVE CONCENTRATION REPRESENTATIVE CONCENTRATION REPRESENTATIVE CONCENTRATION Spatial scale Microscale Microscale Microscale Micr oscale Sampling method GMW TSP GMW TSP GMW TSP GMW TSP Serial # NA NA NA NA Property # 1563 1553 1581 1545 Last Calibration Date 4/2/09 4/24/09 6/11/09 6/ 11/09 Analysis method Weighed by SCAQMD lab Weighed by SCAQMD lab Weighed by SCAQMD lab Weighed by SCAQMD lab Start date 4/1991 4/1991 4/1991 4/1991 Operation schedule 1:6 1:6 1:6 1:6 Sampling season All Year All Year All Year All Year Probe height 2.6 2.6 2.6 2.6 Distance from supporting structure N/A N/A N/A N/A

Distance from obstructions on roof N/A N/A N/A N/A

Distance from obstructions not on roof N/A N/A N/A N/A

Distance from trees N/A N/A N/A N/A Distance to furnace or incinerator flue N/A N/A N/A N/A

Distance between collocated monitors N/A N/A N/A N/A

Unrestricted airflow Yes Yes Yes Yes Probe material N/A N/A N/A N/A Residence time N/A N/A N/A N/A Will there be changes within the next 18 months? No No No No

Is it suitable for comparison against the annual PM2.5? N/A N/A N/A N/A

### Air Quality Monitoring Network Plan – July 2009

D-20 Frequency of flow rate verification for manual PM samplers audit N/A N/A N/A N/A

Frequency of flow rate verification for automated PM analyzers audit N/A N/A N/A N/A

Frequency of onepoint QC check (gaseous) N/A N/A N/A N/A

Last Annual Performance Evaluation (gaseous) N/A N/A N/A N/A

Last two semi-annual flow rate audits for PM monitors N/A N/A N/A N/A

### Air Quality Monitoring Network Plan – July 2009

D-21 

## Exide - Rehrig Site Photos

Looking North Looking East from the probe.

Looking South from the probe. Looking West from the probe

### Air Quality Monitoring Network Plan – July 2009

D-22 

## Exide - ATSF Site Photos (Cont.)

Looking at the probe to the West. Looking from the probe to the East.

Looking from the probe to the South. Looking from the probe to the North.

## Copyrighted page/s removed. Copyrighted ma terial is not available in Regulations.gov since it may not be reproduced without consent of the copyright holder.

Contact the EPA Docket Center’s P ublic Reading Room to view or receive a copy of this document.

Requests for copies may be made as follows:

In person/writing: Environmental Protection Agency, Docket Center 1301 Constitution Ave NW, 2822T, Room 3334 Washington, DC. 20004

Telephone: 202-566-1744

Fax: 202-566- 9744

Email: docket-customerservice@epa.govAir Quality Monitoring Network Plan – July 2009D- 24

### Air Quality Monitoring Network Plan – July 2009

D- 25 

# Site Survey Report

Siting Information

Site Name: Quemetco Date: 6/30/2009 State Code: NA AIRS Number: NA

Latitude: 
 Longitude:  Elevation (m): 89 Address: 720 S 7th Ave. City of Industry, CA 91746 Senior AQIS: Albert Dietrich Site Technician: TBD Site Phone: N/A

Operating Agency: South Coast AQMD


## General Siting Conditions

Station Temperature Traffic Topography Predominant Wind Direction: SW Controlled: No Description: Suburban Site: Level Arc Air Flow (Deg): 360

Recorded: No Distance: 20 Region: Level P robe Last Cleaned Date: N/A

Count (Veh/Day): 20,000 QA Manual Manifold Clean: N/A

Meteorology Non-vehicular Local Sources Approved: Yes Cleaning Schedule: N/A

Located With Instruments: No Description: None Agency: South Coast AQMD Autocalibrator Type: N/A

Distance: N/A Urbanization: Suburban Site Survey Complete: Yes

Direction: N/A Ground Cover: Asphalt Logbook Up To Date: Yes



## Action Items

Comments

### Air Quality Monitoring Network Plan – July 2009

D- 26 

# Detailed Site Information

Site Name Quemetco AQS ID (AIRS #) N/A GIS coordinates Latitude: 
 Longitude:  Location Parking lot Address 720 S 7th Ave. City of Industry, CA 91746 County Los Angeles Dist. to road 10 Traffic count 20,000 Groundcover Asphalt PEP audit? N/A NPAP audit? N/A Flow audit? N/A Representative Area 31100-Los Angeles-Long Beach-Sa nta Ana Pollutant TSP Monitor obj REPRESENTATIVE CONCENTRATION Spatial scale Microscale Sampling method GMW TSP Serial # NA Property # 1577 Last Calibration Date 4/3/09 Analysis method Weighed by SCAQMD lab Start date 1991 Operation schedule 1:6 Sampling season All Year Probe height 2.6 Distance from supporting structure N/A

Distance from obstructions on roof N/A

Distance from obstructions not on roof N/A

Distance from trees N/A Distance to furnace or incinerator flue N/A

Distance between collocated monitors N/A

Unrestricted airflow Yes Probe material N/A Residence time N/A Will there be changes within the next 18 months? No

Is it suitable for comparison against the annual PM2.5? N/A

### Air Quality Monitoring Network Plan – July 2009

D- 27 Frequency of flow rate verification for manual PM samplers audit N/A

Frequency of flow rate verification for automated PM analyzers audit N/A

Frequency of onepoint QC check (gaseous) N/A

Last Annual Performance Evaluation (gaseous) N/A

Last two semi-annual flow rate audits for PM monitors N/A

### Air Quality Monitoring Network Plan – July 2009

D- 28 

## Quemetco – Closet World Site Photos

Looking North from the probe Looking East from the probe.

Looking South toward the probe. Looking West from the probe

## Copyrighted page/s removed. Copyrighted ma terial is not available in Regulations.gov since it may not be reproduced without consent of the copyright holder.

Contact the EPA Docket Center’s P ublic Reading Room to view or receive a copy of this document.

Requests for copies may be made as follows:

In person/writing: Environmental Protection Agency, Docket Center 1301 Constitution Ave NW, 2822T, Room 3334 Washington, DC. 20004

Telephone: 202-566-1744

Fax: 202-566- 9744

Email: docket-customerservice@epa.govAir Quality Monitoring Network Plan – July 2009D- 30

### Air Quality Monitoring Network Plan – July 2009

D- 31 

# Site Survey Report

Siting Information

Site Name: Trojan Battery Date: 6/30/2009 Stat e Code: NA AIRS Number: NA

Latitude: 33° 55’ 17” Longitude: 117° 34’ 20” Elevation (m): 197 Address: 9440 Ann St. Santa Fe Springs, CA 90670 Senior AQIS: Albert Dietrich Site Technician: TBD Site Phone: N/A

Operating Agency: South Coast AQMD


## General Siting Conditions

Station Temperature Traffic Topography Predominant Wind Direction: SW

Controlled: No Description: Suburban Site: Level Arc Air Flow (Deg): 360

Recorded: No Distance: 10 Region: Level P robe Last Cleaned Date: N/A

Count (Veh/Day): 5,000 QA Manual Manifold Clean: N/A

Meteorology Non-vehicular Local Sources Approved: Yes Cleaning Schedule: N/A

Located With Instruments: No Description: None Agency: South Coast AQMD Autocalibrator Type: N/A

Distance: N/A Urbanization: Suburban Site Survey Complete: Yes

Direction: N/A Ground Cover: Asphalt Logbook Up To Date: Yes



## Action Items

Comments

### Air Quality Monitoring Network Plan – July 2009

D- 32 

# Detailed Site Information

Site Name Trojan Battery AQS ID (AIRS #) N/A GIS coordinates Latitude: 34° 01’ 34” Longitude: 11 7° 58’54” Location Parking lot Address 9440 Ann St. Santa Fe Springs, CA 90670 County Los Angeles Dist. to road 10 Traffic count 5,000 Groundcover Asphalt PEP audit? N/A NPAP audit? N/A Flow audit? N/A Representative Area 31100-Los Angeles-Long Beach-Sa nta Ana Pollutant TSP Monitor obj REPRESENTATIVE CONCENTRATION Spatial scale Microscale Sampling method GMW TSP Serial # NA Property # 4903 Last Calibration Date 12/30/08 Analysis method Weighed by SCAQMD lab Start date 11/26/92 Operation schedule 1:6 Sampling season All Year Probe height 2.6 Distance from supporting structure N/A

Distance from obstructions on roof N/A

Distance from obstructions not on roof N/A

Distance from trees N/A Distance to furnace or incinerator flue N/A

Distance between collocated monitors N/A

Unrestricted airflow Yes Probe material N/A Residence time N/A Will there be changes within the next 18 months? No

Is it suitable for comparison against the annual PM2.5? N/A

### Air Quality Monitoring Network Plan – July 2009

D- 33 Frequency of flow rate verification for manual PM samplers audit N/A

Frequency of flow rate verification for automated PM analyzers audit N/A

Frequency of onepoint QC check (gaseous) N/A

Last Annual Performance Evaluation (gaseous) N/A

Last two semi-annual flow rate audits for PM monitors N/A

### Air Quality Monitoring Network Plan – July 2009

D- 34 

## Trojan Battery - UDDH Site Photos

Looking North from the probe Looking East from the probe.

Looking South toward the probe. Looking West from the probe

## Copyrighted page/s removed. Copyrighted ma terial is not available in Regulations.gov since it may not be reproduced without consent of the copyright holder.

Contact the EPA Docket Center’s P ublic Reading Room to view or receive a copy of this document.

Requests for copies may be made as follows:

In person/writing: Environmental Protection Agency, Docket Center 1301 Constitution Ave NW, 2822T, Room 3334 Washington, DC. 20004

Telephone: 202-566-1744

Fax: 202-566- 9744

Email: docket-customerservice@epa.govAir Quality Monitoring Network Plan – July 2009D- 36

### Air Quality Monitoring Network Plan – July 2009

D- 37 

# Site Survey Report

Siting Information

Site Name: Van Nuys A.P. Date: 6/30/2009 State Code: NA AIRS Number: NA

Latitude: 

 Longitude: 	



 Elevation (m): 236 m Address: 16461 Sherman Way. Van Nuys CA, 91406 Senior AQIS: Albert Dietrich Site Technician: TBD Site Phone: N/A

Operating Agency: South Coast AQMD


## General Siting Conditions

Station Temperature Traffic Topography Predominant Wind Direction:

Controlled: No Description: TBD Site: Leve l Arc Air Flow (Deg): 360

Recorded: No Distance: TBD Region: Level Probe Last Cleaned Date: N/A

Count (Veh/Day): QA Manual Manifold Clean: N/A

Meteorology Non-vehicular Local Sources Approved: Yes Cleaning Schedule: N/A

Located With Instruments: No Description: Airp lane Agency: South Coast AQMD Autocalibrator Typ e: N/A

Distance: TBD Urbanization: Suburban Site Survey Complete: Yes

Direction: TBD Ground Cover: Asphalt / Gravel Logbook Up To Date:



## Action Items

Comments

### Air Quality Monitoring Network Plan – July 2009

D- 38 

# Detailed Site Information

Site Name Van Nuys Airport AQS ID (AIRS #) N/A GIS coordinates Latitude: 

 Longitude: 

 Location Airport Address 16461 Sherman Way. Van Nuys CA, 91406 County Los Angeles Dist. to road TBD Traffic count TBD Groundcover Asphalt PEP audit? N/A NPAP audit? N/A Flow audit? N/A Representative Area 31100-Los Angeles-Long Beach-Sa nta Ana Pollutant TSP Monitor obj REPRESENTATIVE CONCENTRATION Spatial scale Microscale Sampling method GMW TSP Serial # TBD Property # TBD Last Calibration Date TBD Analysis method Weighed by SCAQMD lab Start date TBD Operation schedule 1:6 Sampling season All Year Probe height 2.6 Distance from supporting structure N/A

Distance from obstructions on roof N/A

Distance from obstructions not on roof N/A

Distance from trees N/A Distance to furnace or incinerator flue N/A

Distance between collocated monitors N/A

Unrestricted airflow Yes Probe material N/A Residence time N/A Will there be changes within the next 18 months? No

Is it suitable for comparison against the annual PM2.5? N/A

### Air Quality Monitoring Network Plan – July 2009

D- 39 Frequency of flow rate verification for manual PM samplers audit N/A

Frequency of flow rate verification for automated PM analyzers audit N/A

Frequency of onepoint QC check (gaseous) N/A

Last Annual Performance Evaluation (gaseous) N/A

Last two semi-annual flow rate audits for PM monitors N/A