swansea ambient air monitoring station (sams) phase ii 4 … · 2019-10-30 · data logger (with...

Swansea Ambient Air Monitoring Station (SAMS)

Phase II 4th Quarter CY2018 Air Quality Data Report

Prepared for the Colorado Department of Transportation

and the City and County of Denver,

Department of Environmental Health

Montrose Project No. 043AS-122317

Report ID: 043AS-122317-Q4 2018

Test Dates: October 1-December 31 2018

January 31, 2018

City and County of Denver

Report ID: 043AS-122317-Phase II Q4 2018

Table of Contents

PROJECT OVERVIEW ............................................................................................................................... 1

Background ................................................................................................................................................. 1 Objectives .................................................................................................................................................... 1 Operational Staff and Contacts ................................................................................................................... 2 SAMS Site Description ................................................................................................................................ 3

Picture 1 – Location of SAMS in the Swansea Elementary School Parking Lot ..................................................... 3 Picture 2 – Interior of SAMS ................................................................................................................................... 3

SAMS Equipment ......................................................................................................................................... 4 Discussion of Results and Professional Judgment ...................................................................................... 4

POLLUTANT DATA COLLECTED .......................................................................................................... 6

Figure 1a – Monthly PM10 Data .................................................................................................................. 6 Figure 1b – Monthly PM10 Data .................................................................................................................. 7 Figure 1c – Monthly PM10 Data .................................................................................................................. 8 Figure 2a – Monthly PM2.5 Data ................................................................................................................. 9 Figure 2b – Monthly PM2.5 Data ............................................................................................................... 10 Figure 2c – Monthly PM2.5 Data ............................................................................................................... 11 Figure 3a – Monthly NO2 Data ................................................................................................................. 12 Figure 3b – Monthly NO2 Data ................................................................................................................. 13 Figure 3c – Monthly NO2 Data ................................................................................................................. 14 Figure 4a – Monthly CO Data .................................................................................................................. 15 Figure 4b – Monthly CO Data .................................................................................................................. 16 Figure 4c – Monthly CO Data ................................................................................................................... 17 Figure 5a – Monthly Black Carbon Data .................................................................................................. 18 Figure 5b – Monthly Black Carbon Data .................................................................................................. 19 Figure 5c – Monthly Black Carbon Data .................................................................................................. 20 Table 1a – Monthly Summary of VOC Data .............................................................................................. 21 Table 1b – Monthly Summary of VOC Data .............................................................................................. 22 Table 1c – Monthly Summary of VOC Data .............................................................................................. 23 Table 2 – Reporting and Quantification Limits for Selected VOC Compounds ........................................ 23

DATA QUALITY ASSURANCE/QUALITY CONTROL ....................................................................... 24

Quality Assurance/Quality Control ........................................................................................................... 24 NOX and CO Analyzers - Span Test ....................................................................................................................... 24 NOX and CO Analyzers - Precision Test ................................................................................................................ 25 PM2.5 / PM10 Analyzer ............................................................................................................................................ 26 Aethalometer .......................................................................................................................................................... 26 Wind Speed and Wind Direction ........................................................................................................................... 26 Gas Chromatograph ............................................................................................................................................... 27

SIGNATURE PAGE ................................................................................................................................... 33

APPENDIX

Quality Assurance Logs Calibration Certification Sheets Primary Flow Standard Certification Sheet


Report ID: 043AS-122317-Phase II Q4 2018 Page 1

Project Overview

Background

Colorado Department of Transportation (CDOT) and Denver Department of Public

Health and Environment (DDPHE) entered into an agreement1 to monitor air quality at

Swansea Elementary School in three phases. Phase I monitored air quality for one year

prior to startup of a CDOT construction project on Interstate 70 (I-70). Phase II will

monitor air quality for three (3) years during the I-70 expansion project; construction may

last more than three years. Phase III will monitor air quality for one year after I-70

construction and ground disturbance activities are completed.

The monitoring aspect of Phase I began on April 1, 2017. The monitoring project scope

of work, which is an attachment to the agreement, defined the first quarter of a year as

beginning on September 1. Therefore, monitoring began in the third quarter of the 2017

project year (Q3 PY2017). Beginning in June 2018 the quarter system changed to reflect

common calendar quarters to prevent confusion about what time period a report is

covering. This Q4 2018 report was created to present the data collected during Phase II.

Objectives

Montrose Air Quality Services, LLC (Montrose) was contracted by the City and County

of Denver to start up and operate the SAMS. The SAMS is located at the Swansea

Elementary School; between the faculty parking lot and the playground; South East

Corner; at 4650 Columbine Street, Denver, Colorado. This report represents Q4 2018.

The station monitored the following parameters during Q4 2018:

• C6 (6-Carbon) through C12 (12-Carbon) Volatile Organic Compounds (VOC)

• Black Carbon

• Carbon Monoxide (CO)

• Particulate Matter less than 10 Microns (PM10)

• Particulate Matter less than 2.5 Microns (PM2.5)

• Meteorological Measurements

• Nitrogen Oxides (NOx)

The monitoring is being performed to meet the requirements of the agreement between

CDOT and DDPHE. Additionally, the regulations and specifications set forth by the

Colorado Department of Public Health and Environment (CDPHE) and the United States

Environmental Protection Agency (USEPA), are being followed as applicable.

1 The agreement between CDOT and DDPHE became effective on August 12, 2016 and can be obtained

from CDOT by referencing routing number 17-HTD-ZH-00167.



Operational Staff and Contacts

The contact information for each of the principal parties is summarized in the table

below:

Tim Buntrock Michael Ogletree

Colorado Department of Transportation City and County of Denver

3543 East 46th Avenue 200 W 14th Ave

Denver, CO 80216 Denver, CO 80204

Phone: (720) 920-4692 Phone: (720) 865-2891

E-mail: [email protected] E-mail: [email protected]

Patrick Clark, PE, QSTI Dr. Larry Anderson

Montrose Air Quality Services, LLC University of Colorado Denver

990 W. 43rd Ave. 7120 Routt Street

Denver, CO 80211 Arvada, CO 80004

Phone: (303) 670-0530 Phone: (303) 664-0757

E-mail: [email protected] E-mail: [email protected]

Austin Heitmann

Montrose Air Quality Services, LLC

990 W. 43rd Ave.

Denver, CO 80211

Phone: (303) 670-0530

E-mail: [email protected]

mailto:[email protected]

mailto:[email protected]



SAMS Site Description

Region: Denver

AQS ID: 080310023

Latitude: 39.78101

Longitude: -104.95545

Picture 1 – Location of SAMS in the Swansea Elementary School Parking Lot

Picture 2 – Interior of SAMS



SAMS Equipment

The list of primary equipment used in this project is shown in the table below. Montrose

has supplied and installed the following:

• Glass lined sample probe

• Glass sampling manifold

• Sample blower, fittings, and tubing

• Instrument rack

• Cylinder mounts, calibration gases and regulators

• Security camera

Pollutant/Parameter

Sampling Period

Manufacturer

Model

Nitrogen Oxides

Minute Teledyne T200U

Carbon Monoxide

Minute Thermo Scientific 48i-TLE Trace Level CO

Dynamic Dilution Calibrator Periodic

Teledyne T700U

PM2.5 / PM10 Minute GRIMM

Technologies Inc.

180 EDM

Meteorological measurements

(temperature, pressure, relative

humidity)

Minute GRIMM

Technologies Inc.

180 EDM

Meteorological measurements

(wind speed and wind

direction)

Minute RM Young 05305V

C6 through C12 VOCs 30 Minutes Chromatotec Airmo C6-C12

(Model A27022)

Black Carbon

5 Minutes Magee Scientific Aethalometer

Data Logger

(with remote accessibility)

Multiple Agilaire 8872

Discussion of Results and Professional Judgment

The reported data is for Phase II Q4 CY2018 which is considered, October, November

and December.

The results of NO2, CO, PM2.5, PM10, black carbon and VOC monitoring data can be

found in Figures 1 through 5 and Table 1 on Pages 7 through 24. The Clean Air Act

requires EPA to set National Ambient Air Quality Standards (NAAQS) for pollutants

considered harmful to public health and the environment. The graphs shown indicate the

readings for each month relative the NAAQS Standard (if applicable). Electronic records

https://www.epa.gov/clean-air-act-overview



of all data and calibrations have been uploaded to the Dropbox data room maintained by

DDPHE.

No pollutant NAAQS was exceeded during Q4 PY2018. Additionally, there were no

exceptional events, weather or otherwise, during the sampling period. An exceptional

event is any unusual or naturally occurring event that can affect air quality but cannot not

be reasonably controlled using techniques that agencies may implement in order to attain

and maintain the NAAQS. All exceptional events are documented by CDPHE.

The aethalometer, GRIMM, and all meteorological equipment was calibrated weekly with

no unusual results or maintenance issues this quarter.

The Chromatotec Gas Chromatograph (GC) for C6 through C12 was calibrated daily by

running a permeation benzene tube and zero air checks with no unusual results this

quarter while the GC was in operation.

The CO and NOX analyzers were calibrated daily by diluting an EPA Protocol 1

calibration. On 10/14/18 the CO analyzer failed the daily calibration due to the internal

background of the instrument reaching its maximum allowed value and needing to be

reset. The CO data was considered invalid, and not included in this report, until the issue

was resolved on 10/24/18. On 11/11/18 the NO2 calibrations on the NOx analyzer began

drifting out of calibration, invalidating the data during the time the issue persisted. The

issue was attempted to be corrected multiple times in the field with manual calibrations

but the daily drift became too large to adjust for. The manufacturer was contacted on

11/28/18 to determine how to resolve the issue. Since the instrument is still under

warranty the manufacturer supplied replacement parts for the instrument that arrived

during Q1 2019.



Pollutant Data Collected

Figure 1a – Monthly PM10 Data

The graph below is shown for October and is the plot of the 24 hour averages. The

orange line represents the 150 micrograms per cubic meter (ug/m3) 24 hour ambient PM10

NAAQS.



Figure 1b – Monthly PM10 Data

The graph below is shown for November and is the plot of the 24 hour averages. The

orange line represents the 150 ug/m3 24 hour ambient PM10 NAAQS.



Figure 1c – Monthly PM10 Data

The graph below is shown for December and is the plot of the 24 hour averages. The

orange line represents the 150 ug/m3 24 hour ambient PM10 NAAQS.



Figure 2a – Monthly PM2.5 Data

The graph below is shown for October and is a plot of the 24 hour averages. The orange

line represents the 35 ug/m3 24 hour ambient PM2.5 NAAQS and the yellow line

represents the 12 ug/m3 one (1) year mean ambient PM2.5 NAAQS. Please note that the

24 hour average values cannot be directly compared to the annual mean NAAQS.



Figure 2b – Monthly PM2.5 Data

The graph below is shown for November and is a plot of the 24 hour averages. The

orange line represents the 35 ug/m3 24 hour ambient PM2.5 NAAQS and the yellow line





Figure 2c – Monthly PM2.5 Data

The graph below is shown for December and is a plot of the 24 hour averages. The

orange line represents the 35 ug/m3 24 hour ambient PM2.5 NAAQS and the yellow line





Figure 3a – Monthly NO2 Data

The graph below is shown for October is a plot of the one (1) hour averages. The orange

line represents the 100 parts per billion (ppb) one (1) hour ambient NO2 NAAQS and the

yellow line represents the 53 ppb one (1) year mean ambient NO2 NAAQS. Please note

that the one (1) hour average values cannot be directly compared to the annual mean

NAAQS.



Figure 3b – Monthly NO2 Data

The graph below is shown for November is a plot of the one (1) hour averages. The

orange line represents the 100 ppb one (1) hour ambient NO2 NAAQS and the yellow line

represents the 53 ppb one (1) year mean ambient NO2 NAAQS. Please note that the one

(1) hour average values cannot be directly compared to the annual mean NAAQS. No

valid NO2 data was collected from 11/11/18 through the end of the month for the reasons

described on page 5.



Figure 3c – Monthly NO2 Data

The graph below is shown for December is a plot of the one (1) hour averages. The

orange line represents the 100 ppb one (1) hour ambient NO2 NAAQS and the yellow line

represents the 53 ppb one (1) year mean ambient NO2 NAAQS. Please note that the one

(1) hour average values cannot be directly compared to the annual mean NAAQS. No

valid NO2 data was collected during December 2018 for the reasons described on page 5.



Figure 4a – Monthly CO Data

The graph below is shown for October and is a plot of the one (1) hour averages. The

orange line represents the nine (9) ppm eight (8) hour ambient CO NAAQS and the

yellow line represents the 35 ppm one (1) hour ambient CO NAAQS. No valid CO data

was collected from 10/14/18 through 10/24/18 for the reasons described on page 5.



Figure 4b – Monthly CO Data

The graph below is shown for November and is a plot of the one (1) hour averages. The


yellow line represents the 35 ppm one (1) hour ambient CO NAAQS.



Figure 4c – Monthly CO Data

The graph below is shown for December and is a plot of the one (1) hour averages. The


yellow line represents the 35 ppm one (1) hour ambient CO NAAQS.



Figure 5a – Monthly Black Carbon Data

The graph below is shown for October and plots the 24 hour averages. Black Carbon

does not have a NAAQS.



Figure 5b – Monthly Black Carbon Data

The graph below is shown for November and plots the 24 hour averages. Black Carbon




Figure 5c – Monthly Black Carbon Data

The graph below is shown for December and plots the 24 hour averages. Black Carbon




The results of the selected VOC compounds are shown in the table below. Electronic

records of all VOC compounds have been uploaded to the Dropbox data room maintained

by DDPHE. When calculating the average, the following rules were applied:

• If an individual result was above the reporting limit (RL), the result was used in

calculating the average

• If an individual result was below the RL or not detected, one half the RL was used

in calculating the average.

Table 1a – Monthly Summary of VOC Data

The table below is shown for October and averages 30 minute runs. None of the

compounds reported have a NAAQS.

Compound

Average

Result for

October

(ppb)

Total

Number

of Data

Points

Number

Above

QL2

Number

Between

RL and

QL

Number

Below RL

N-Hexane 0.407 1428 893 309 226

N-Heptane 0.129 1428 298 225 905

N-Octane 0.0919 1428 136 189 1103

Benzene 0.193 1428 431 305 692

Toluene 0.640 1428 912 274 242

Ethylbenzene 0.102 1428 134 275 1019

m,p-Xylene 0.298 1428 398 392 638

o-Xylene 0.132 1428 68 131 1229

2 Quantification Limit (QL)



Table 1b – Monthly Summary of VOC Data

The table below is shown for November and averages 30 minute runs. None of the


Compound

Average

Result for

November

(ppb)

Total

Number

of Data

Points

Number

Above

QL3

Number

Between

RL and

QL

Number

Below RL

N-Hexane 0.449 1382 871 281 230

N-Heptane 0.157 1382 345 269 768

N-Octane 0.101 1382 154 222 1006

Benzene 0.250 1382 529 332 521

Toluene 0.721 1382 956 187 239

Ethylbenzene 0.122 1382 155 299 928

m,p-Xylene 0.368 1382 441 397 544

o-Xylene 0.147 1382 79 147 1156




Table 1c – Monthly Summary of VOC Data

The table below is shown for December and averages 30 minute runs. None of the


Compound

Average

Result for

December

(ppb)

Total

Number

of Data

Points

Number

Above

QL4

Number

Between

RL and

QL

Number

Below RL

N-Hexane 0.517 1398 1008 269 121

N-Heptane 0.177 1398 347 304 747

N-Octane 0.140 1398 185 251 962

Benzene 0.287 1398 639 324 435

Toluene 0.803 1398 1021 157 220

Ethylbenzene 0.131 1398 191 341 866

m,p-Xylene 0.413 1398 534 392 472

o-Xylene 0.156 1398 109 163 1126

Table 2 – Reporting and Quantification Limits for Selected VOC Compounds

The RLs and QLs for the selected compounds is shown in the table below:

Compound

Reporting

Limit

(ppb)

Quantification

Limit (ppb)

N-Hexane 0.1 0.2

N-Heptane 0.1 0.2

N-Octane 0.1 0.2

Benzene 0.1 0.2

Toluene 0.1 0.2

Ethylbenzene 0.1 0.25

m,p-Xylene 0.15 0.35

o-Xylene 0.2 0.35




Data Quality Assurance/Quality Control

Quality Assurance/Quality Control

Quality assurance is a general term for the procedures used to ensure that a particular

measurement meets the quality requirements for its intended use. Quality control of

continuous analyzers consists of precision and span checks or flow verifications. Quality

objectives were assessed via laboratory and site system audits.

All work being done on this project follows the operating procedures described in the

“Swansea Air Monitoring Station Quality Assurance Project Plan” (QAPP) dated 7/1/17.

The QAPP can be provided by Michael Ogletree upon request. Mr. Ogletree’s contact

information can be found in the “Operational Staff and Contacts” section of this report.

To ensure the collection of high quality data, the following Quality Assurance/Quality

Control procedures were implemented:

NOX and CO Analyzers - Span Test

A span test was conducted every other day. The NOX span test started at 21:46 and lasted

for approximately 50 minutes. The CO span test started at 22:46 and lasted for

approximately 20 minutes.

A CO span test was conducted by first analyzing a span gas of CO which was introduced

to the sampling manifold at the back of the analyzer. After a stable reading was reached

and recorded, a zero gas was introduced to the sampling manifold at the back of the

analyzer. The CO gas was generated by diluting an EPA Protocol 1 calibration gas using

the Teledyne Dynamic Dilution Calibrator.

An NO/NO2 span test was conducted by first analyzing a zero gas that was introduced to

the sampling manifold at the back of the analyzer. After a stable reading was reached and

recorded, a span gas of NO was introduced to the sampling manifold at the back of the

analyzer. The NO gas was also generated by diluting an EPA Protocol 1 calibration gas

using the Teledyne Dynamic Dilution Calibrator. After a stable reading was reached and

recorded, a span gas of NO2 was generated by diluting an EPA Protocol 1 calibration gas

and combing the diluted gas with a known quantity of ozone (O3) using the Teledyne

Dynamic Dilution Calibrator. After a stable reading was reached and recorded, a zero gas

was introduced to the sampling manifold at the back of the analyzer.

Each calibration gas was certified according to EPA Protocol 1 procedures. The

generated gases were approximately, five (5) ppm of CO, 400 ppb of NO and 300 ppb of

NO2. In all cases the measured responses were then compared to the generated gas value

to determine the analyzer drift. The EPA requirement for span is 10 percent. The span

check results are summarized in the table below:



Parameter Span Count Span Passed Span Percentage

Nitrogen Oxide 46 46 100

Nitrogen Dioxide 46 15 32.6

Carbon Monoxide 46 43 93.5

NOX and CO Analyzers - Precision Test

A precision test was conducted every other day. The NOX precision test started at 21:46

and lasted for approximately 50 minutes. The CO precision test started at 22:46 and

lasted for approximately 20 minutes.

A CO precision test was conducted by first analyzing a precision gas of CO which was

introduced to the sampling manifold at the back of the analyzer. After a stable reading

was reached and recorded, a zero gas was introduced to the sampling manifold at the back

of the analyzer. The CO gas was generated by diluting an EPA Protocol 1 calibration gas

using the Teledyne Dynamic Dilution Calibrator.

An NO/NO2 precision test was conducted by first analyzing a zero gas that was

introduced to the sampling manifold at the back of the analyzer. After a stable reading

was reached and recorded, a precision gas of NO was introduced to the sampling

manifold at the back of the analyzer. The NO gas was also generated by diluting an EPA

Protocol 1 calibration gas using the Teledyne Dynamic Dilution Calibrator. After a stable

reading was reached and recorded, a precision gas of NO2 was generated by diluting an

EPA Protocol 1 calibration gas and combining the diluted gas with a known quantity of

ozone (O3) using the Teledyne Dynamic Dilution Calibrator. After a stable reading was

reached and recorded, a zero gas was introduced to the sampling manifold at the back of

the analyzer.

Each calibration gas was certified according to EPA Protocol 1 procedures. The

generated gases were approximately, 1.5 ppm of CO, 100 ppb of NO and 70 ppb of NO2.

In all cases the measured responses were then compared to the generated gas value to

determine the analyzer drift. The EPA requirement for span is 10 percent. The span

check results are summarized in the table below:

Parameter Precision

Count

Precision

Passed

Precision

Percentage

Nitrogen Oxide 46 46 100

Nitrogen Dioxide 46 13 28.3

Carbon Monoxide 46 32 69.6



PM2.5 / PM10 Analyzer

A zero check was conducted on the GRIMM analyzer every two (2) weeks. The zero

check was conducted by placing a particulate filter inline and observing the response of

the analyzer. If anything other than a zero reading was observed, corrective action was

taken. Additionally, a flow check was conducted on the analyzer by using a NIST

traceable standard to measure the flow rate through the GRIMM. The NIST standard was

a MesaLabs DCL-MH DryCal flowmeter. The calibration certification can be found in

the Appendix of this report. The flow test was considered acceptable if the flow rate was

between 1.15 and 1.25 liters per minute (lpm). On a weekly basis the met station ambient

temperature, relative humidity, and pressure was checked by comparing the measured

values to that of a reference standard. The results were considered acceptable if the

temperature, relative humidity, and pressure was within 2oC, 5%, and 10 mmHg,

respectively. A summary of the weekly and biweekly checks is summarized below.

Test Count Passed Percentage

Zero Check 5 5 100%

Flow Check 5 5 100%

Temperature Check 7 7 100%

Pressure Check 7 7 100%

Aethalometer

On a monthly basis the aethalometer cyclone was cleaned and inspected. A flow check

was conducted using a NIST traceable standard to measure the flow rate through the

aethalometer. The NIST standard was a MesaLabs DCL-MH DryCal flowmeter. The

calibration certification can be found in the Appendix of this report. The flow test was

considered acceptable if the flow rate was within seven (7) percent of the measured value.

Additionally, a leak check was conducted by capping the sample probe and observing the

measured flow through the instrument. The leak check was considered valid if the

measured flow rate was less than 2.5 liters per minute (lpm). A summary of the monthly

checks and is summarized below:


Flow Check 3 3 100%

Leak Check 3 3 100%

Wind Speed and Wind Direction

The wind speed is calibrated via an anemometer drive that provides a convenient and

accurate way to rotate the anemometer shaft at a known rate. The known rate that the

drive rotates can then be compared to the wind speed reading on the data logger.



The wind direction is calibrated with a vane angle bench stand. The monitor is placed on

the stand which has a base with markings of 0 to 360 degrees. The tail of the monitor is

stabilized so that as the monitor is rotated the wind direction readings are stable on the

data logger.


Wind Speed Check 3 3 100%

Wind Direction Check 3 3 100%

Gas Chromatograph

The GC was calibrated prior to installation using a gas standard containing a known

concentration of the Photochemical Assessment Monitoring Station (PAMS) list of

compounds. A copy of the calibration certification can be found in the Appendix of this

report. Two (2) additional concentrations were prepared and analyzed by diluting the

cylinder gases using zero air and a Thermo Model 146i Multi-Gas Calibrator.

A PAMS 5-point calibration of the GC was conducted on December 6, 2018. All

collected raw data was then post-processed to provide valid data in this report to. The

calibration also identifies 35 compounds (or pairs of compounds that coelute). An

example of the calibration for one of these compounds, benzene, is shown in the

following figure. This calibration spans the concentration range from about 1 to 17 ppb.

Similar calibrations were done for the other PAMS compounds identified by the GC.



Due to the lack of availability of a PAMS calibration mixture the PAMS calibration had

to be delayed until 12-6-18. Since the instrument was shut down and moved since the

previous calibrations, it was decided to wait until a new PAMS calibration could be

performed to process this data set. The new PAMS gas mixture provided sufficient

justification to change response factors for some of the compounds identified, including

benzene and toluene. The Base Sensitivity used in these analyses was selected to balance

results from both the PAMS calibrations, and the daily PERM calibration checks. The

regression results from this PAMS calibration are similar to previous results with the

measured benzene being about 89% of the PAMS calibration. The measured benzene

from the daily PERM measurements are about 120% of those expected from the

calculated benzene in the permeation samples.

The detection limit for the GC technique was determined from data collected during

repeated measurements of a low concentration PAMS standard mixture. The detection

limit is three (3) times the standard deviation of low concentration measurements for the

individual compounds. Because some peaks are close together, there is a greater

uncertainty for partially overlapping peaks and small retention time shifts. We have

chosen to use a reporting limit, as the smallest concentration where we have confidence

that the compound is present. The smallest reporting limit has been set at 0.1 ppb and is

greater than or equal to three times the standard deviation for each of the compounds.



Compounds present at concentrations equal to the detection limit (or reporting limit, in

this case) are believed to be present, but concentrations near this limit are highly

uncertain. Data to be used quantitatively should exceed the quantitation limit. This

limit is used to identify when the concentration that was measured for the compound is

known with a reasonable degree of confidence. The quantitation limit is normally

defined as 10 times the standard deviation of low concentration measurements for

individual compounds. Concentrations below the quantitation limit and above the

reporting limit really indicates that the compound was present, but the concentration is

too uncertain to be of value.

The GC technique used in this work uses a sorbent tube to collect C6 through C12

hydrocarbons, then thermally desorbs these compounds onto the GC column for

separation. The larger compounds are not completely desorbed under the conditions used

in this analysis, so that can place additional limitations on the quantitative determination

of the concentrations of some of these compounds, since some of the compound collected

during one time period will not be desorbed until the following sample is analyzed. This

carryover of sample to a subsequent period was estimated by looking at data for a zero

sample following a PAMS calibration sample. This data allows one to estimate the

percent carryover of compounds to a subsequent period. The data for both undecane and

dodecane suggests that the carryover is more than 50% so concentrations will not be

reported for these compounds. The following table shows the reporting limits,

quantitation limits and estimated percent carryover for each of the compounds identified

in this work.



Reportable Compounds

Reporting Quantitation Approximate

# Name Limit Limit % carryover ppbv ppbv

1 2,2-Dimethylbutane 0.1 0.2 <5%

2 n-Hexane 0.1 0.2 <5%

3 Methylcyclopentane & 2,4-

dimethylpentane5

0.1 0.25 <5%

4 Benzene 0.1 0.2 <5%

5 Cyclohexane 0.25 0.75 <5%

6 2-Methylhexane & 2,3-dimethylpentane 0.2 0.5 <5%

7 3-Methylhexane 0.1 0.2 <5%

8 2,2,4-Trimethylpentane 0.1 0.2 <5%

9 n-Heptane 0.1 0.2 <5%

10 Methylcyclohexane 0.1 0.2 <5%

11 2,3,4-Trimethylpentane 0.1 0.2 <5%

12 Toluene 0.1 0.2 <5%

13 2-Methylheptane 0.1 0.2 <5%

14 3-Methylheptane 0.1 0.2 <5%

15 n-Octane 0.1 0.2 5%

16 Ethylbenzene 0.1 0.25 10%

17 m & p-Xylene 0.15 0.35 10%

18 Styrene 0.2 0.5 15%

19 o-Xylene 0.2 0.35 10%

20 n-Nonane 0.1 0.2 10%

21 Isopropylbenzene 0.1 0.2 10%

22 a-Pinene 0.2 0.4 nd

23 n-Propylbenzene 0.15 0.35 15%

24 m-Ethyltoluene 0.3 1 15%

25 p-Ethyltoluene 0.2 0.65 15%

26 1,3,5-Trimethylbenzene 0.2 0.5 15%

27 o-Ethyltoluene 0.2 0.5 15%

28 1,2,4-trimethybenzene 0.25 0.75 20%

29 n-Decane 0.3 0.85 20%

30 1,2,3-Trimethylbenzene 0.3 0.85 20%

31 m-Diethylbenzene 0.3 0.9 20%

32 p-Diethylbenzene 0.4 1.3 25%

33 n-Undecane

45%

34 n-Dodecane

45%

5 Due to Methylcyclopentane & 2,4-dimethylpentane co-eluting the concentrations of the

individual compounds became unavailable, therefore the compound concentrations must

be reported as a sum of both compounds



To verify the stability of the GC, a span check was normally done at a 25-hour interval.

The span check used a benzene permeation tube that emits benzene at a rate of 101

nanograms per minute, and was diluted to generate a gas concentration of approximately

35 ppb. The span check was followed by a zero check to minimize carryover of the high

benzene concentration of benzene from the span check to the next ambient sample and to

verify the desorption efficiency and check for contamination of the GC.

If the results of the span check varied by more than ±15% from the average response that

has been observed previously for more than two (2) consecutive days, a system retention

time and response test was scheduled as soon as possible. Appropriate remedial action

was taken if a problem was observed. A control chart showing the results of the span

check for Q4 2018 is shown below.

For the zero checks, the benzene carryover from a preceding calibration or span check

should be less than 1% of the concentration of the benzene in the span gas. If this zero

check limit was exceeded on more than two (2) consecutive days, a system retention time

and response test was scheduled as soon as possible. Appropriate remedial action was

taken if a problem was observed. A control chart showing the results of the zero check

for Q4 2018 is shown as follows.



The zero and span checks are summarized below:


Span Check 88 88 100%

Zero Check 88 88 100%



Signature Page

Prepared and reviewed by:

Patrick Clark, PE


Austin Heitmann


Additionally reviewed by:

Michael Ogletree


Appendix

Quality Assurance Logs

Calibration Certification Sheets

Primary Flow Standard Certification Sheet

swansea ambient air monitoring station (sams) phase ii 4 … · 2019-10-30 · data logger (with...

Documents