HomeMy WebLinkAbout10047_Atherton Mills_ IAR Risk-based Goals 20150113
1075 Big Shanty Road NW
Suite 100
Kennesaw, Georgia 30144
770-421-3400
amecfw.com
January 20, 2015
Ms. Carolyn Minnich, Brownfields Project Manager
North Carolina Department of Environment and Natural Resources
Division of Waste Management
Brownfields Program
1646 Mall Service Center
Raleigh, North Carolina 27600-1646
Subject: Indoor Air Monitoring – Risk-based Goals
Atherton Mill Property
2000 South Boulevard
Charlotte, Mecklenburg County, North Carolina
Brownfields Project Number: 10047-06-60
AMEC Project: 6228-12-0051
Dear Ms. Minnich:
AMEC Foster Wheeler Environment & Infrastructure, Inc. (AMEC) evaluated the constituents
detected in indoor air samples collected at the Atherton Mill Property, 2000 South Boulevard,
Charlotte, North Carolina. Six indoor air samples were collected in April 2013, July 2013, and
January 2014. One outdoor ambient air sample was collected during each of these three
sampling events. Ten indoor air samples were collected in June 2014 and seven indoor air
samples were collected in September 2014. During each of the June and September 2014
events, an upwind and downwind ambient air sample were also collected. As a first step,
detected concentrations from the 2013 and 2014 indoor air sampling events were compared to
the North Carolina Department of Environment and Natural Resources (NCDENR) Division of
Waste Management (DWM) Non-Residential Vapor Intrusion Screening Levels published in
June 2014 (NCDENR, 2014). Eleven volatile compounds were detected at maximum
concentrations that exceeded the DWM non-residential indoor air screening levels.
Exposure Assessment
The Atherton Mill Property is a commercial development housed partly in the former Parks-
Cramer Company manufacturing facility that was built in the 1919, and partly in a former
Charlotte Trolley Car Barn. One historic feature of the site is wooden brick floors, which have
been observed to off-gas naphthalene. Additional volatile compounds have been detected in air
samples that may be associated with current retail and office activities, and other sources such
as furnishings and building materials. To support air monitoring for the eleven volatile
Indoor Air Monitoring – Risk-based Goals
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constituents of potential concern (COPCs) that exceeded the DWM screening levels, target
monitoring goals were developed to be protective of retail sales workers and office workers. The
COPCs detected in the sampled tenant spaces differ with only one to three COPCs detected in
the majority of the spaces sampled. The retail sales and office employment classifications are
representative of current occupants at Atherton Mill. Office workers were assumed to be
employed 8 hours per day for 250 days per year for 25 years (USEPA, 2014a). Retail sales
workers were assumed to be employed 8 hours per day for 250 days per year for 4 years
(USEPA, 2014a; Bureau of Labor Statistics, 2014).
Toxicity Assessment
Toxicity values [Inhalation Reference Concentrations (RfCs) and Inhalation Unit Risks (IURs)]
used in this evaluation were obtained from the USEPA Integrated Risk Information System
(IRIS) and other USEPA-approved sources as listed in the May 2014 Vapor Intrusion Screening
Level calculator (USEPA, 2014b). The toxicity values used in this assessment are listed on
Tables 1 and 2. The RfC is used to estimate non-carcinogenic inhalation hazards. The RfC is an
estimate of the daily exposure to the human population (including sensitive subgroups such as
children and the elderly) that is likely to be without an appreciable risk of deleterious effects. The
IUR is characterized as an upper-bound estimate designed to be protective of the majority of the
human population.
Calculation of Risk-based Goals for Air Monitoring
Risk-based air monitoring goals were calculated for office workers and retail sales workers using
the equations presented in the Vapor Intrusion Screening Level calculator (USEPA, 2014b) and
the exposure assumptions listed above for each employment group. For the purpose of
calculating risk-based air monitoring goals, the target hazard index for non-carcinogens has
been based on one because cumulative target organ-specific systemic or non-carcinogenic
health risks are unlikely to exceed one. The target risk for carcinogens has been based on 10-5
for the indoor air pathways because cumulative risks would not exceed 10-4, an upper risk level
that is considered to be in the acceptable range under CERCLA. These target hazard and risk
goals are in agreement with current DWM guidance (NCDENR, 2014).
Air monitoring goals protective of office workers potentially exposed to the COPCs are presented
in Table 1. Air monitoring goals protective of retail sales workers potentially exposed to the
COPCs are presented in Table 2.
The values listed for chronic exposure to non-carcinogens are also protective of short-term
exposures. USEPA has identified fetal cardiac defects in TCE-exposed animals as the basis for
interim short-term action levels. The concerns focus on the presumption that the critical period
for human fetal cardiac development occurs within a three-week period within the first trimester
of pregnancy, although the specific timing and duration of TCE exposure associated with
Indoor Air Monitoring – Risk-based Goals
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potential developmental toxicity for humans is not known. A risk-based air monitoring level of
8.8 µg/m3 for TCE will be protective of both short-term and longer-term chronic exposure
durations.
AMEC appreciates this opportunity to provide our environmental consulting services. If you
have questions concerning this letter or this project, please contact us at 770-499-6849.
Sincerely,
AMEC Environment & Infrastructure, Inc.
Melissa Bystedt Laura M. Smith, RHSP
Project Scientist Associate Scientist
Enclosures:
Table 1
Table 2
References
Indoor Air Monitoring – Risk-based Goals
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REFERENCES
Bureau of Labor Statistics, 2014. Employee Tenure in 2014. News Release, September 18,
2014.
NCDENR, 2014. Division of Waste Management (DWM) Vapor Intrusion Screening levels
Guidance Document, North Carolina Department of Environment and Natural
Resources, April 2014. Tables updated in June 2014.
USEPA, 2014a. Human Health Evaluation Manual, Supplemental Guidance: Update of
Standard Default Exposure Factors, OSWER Directive 9200.1-120, February 2014.
USEPA, 2014b. Vapor Intrusion Screening Level Calculator. U.S Environmental Protection
Agency, May 2014.
Parameter Inhalation InhalationRfC Unit Risk (IUR)(mg/m3) (µg/m3)-1 Benzene 3.0E-02 7.8E-06 IRIS 98 130Chloroform 9.8E-02 2.3E-05 ATSDR/IRIS 33 4301,4-Dichlorobenzene 8.0E-01 1.1E-05 IRIS/CalEPA 70 3,5001,2-Dichloroethane 7.0E-03 2.6E-05 PPRTV/IRIS 29 31Ethyl Acetate 7.0E-02 NA PPRTV NA 310Ethylbenzene 1.0E+00 2.5E-06 IRIS/CalEPA 310 4,400N-Hexane 7.0E-01 NA IRIS NA 3,100Naphthalene 3.0E-03 3.4E-05 IRIS/CalEPA 23 13Tetrachloroethene 4.0E-02 2.6E-07 IRIS 2900 180Trichloroethene 2.0E-03 4.1E-06 IRIS 190 8.81,2,4-Trimethylbenzene 7.0E-03 NA PPRTV NA 31m3 = cubic metersPrepared/Date: LMS 1/16/15mg = milligramChecked/Date: MKB 1/19/15RfC = Reference Concentrationµg = microgramsNA = Not AvailableCalEPA - California Environmental Protection AgencyIRIS - Integrated Risk Information SystemPPRTV - Provisional Peer-Reviewed Toxicity ValueATSDR - Agency for Toxic Substances and Disease Registry(a) Target Indoor Air Conc. (Carcinogens) = (TCR * ATc)/ (ET * EF * ED * IUR)(b) Target Indoor Air Conc. (Non-Carcinogens) = (RfC * THI * ATnc * 1000)/ (ET * EF * ED)CA = Constituent Concentration in Air (estimated) See above(µg/m3)ATnc = Averaging Time (Noncarcinogen, hours) 35,040ET = Exposure Time (hours per day) 8 (hours/day)ATc = Averaging Time (Carcinogenic, hours)613,200EF = Exposure Frequency (days per year) 250 (days/year) TCR = Target Cancer Risk1.00E-05ED = Exposure Duration (years)4 (years) THI = Target Hazard Index 1Note: Median tenure for retail workers ranges from 2.8 years to 3.3 years for January 2004 through January 2014 (Employee Tenure in 2014, Bureau for Labor Statistics, September 2014. . Exposure duration rounded upward to 4 years.Target Indoor Air Conc. for Carcinogens(ug/m3) (a)Target Indoor Air Conc for Non-Carcinogens(ug/m3) (b)Table 1: Calculation of Preliminary Risk Goals for Indoor Air Concentrations - Retail WorkerAtherton Mill PropertyCharlotte, North CarolinaAMEC Project: 6228-12-0051Toxicity ValuesSource
Parameter Inhalation InhalationRfC Unit Risk(mg/m3) (µg/m3)-1 Benzene 3.0E-02 7.8E-06 IRIS 16 130Chloroform 9.8E-02 2.3E-05 ATSDR/IRIS 5.3 4301,4-Dichlorobenzene 8.0E-01 1.1E-05 IRIS/CalEPA 11 3,5001, 2-Dichloroethane 7.0E-03 2.6E-05 PPRTV/IRIS 4.7 31Ethyl Acetate 7.0E-02 NA PPRTV NA 310Ethylbenzene 1.0E+00 2.5E-06 IRIS/CalEPA 49 4,400N-Hexane 7.0E-01 NA IRIS NA 3,100Naphthalene 3.0E-03 3.4E-05 IRIS/CalEPA 3.6 13Tetrachloroethene 4.0E-02 2.6E-07 IRIS 470 180Trichloroethene 2.0E-03 4.1E-06 IRIS 30 8.81,2,4-Trimethylbenzene 7.0E-03 NA PPRTV NA 31m3 = cubic metersPrepared/Date: LMS 1/16/15mg = milligramChecked/Date: MKB 1/19/15RfC = Reference Concentrationµg = microgramsNA = Not AvailableCalEPA - California Environmental Protection AgencyIRIS - Integrated Risk Information SystemPPRTV - Provisional Peer-Reviewed Toxicity ValueATSDR - Agency for Toxic Substances and Disease Registry(a) Target Indoor Air Conc. (Carcinogens) = (TCR * ATc)/ (ET * EF * ED * IUR)(b) Target Indoor Air Conc. (Non-Carcinogens) = (RfC * THI * ATnc * 1000)/ (ET * EF * ED)CA = Constituent Concentration in Air (estimated) See above(µg/m3)ATnc = Averaging Time (Noncarcinogen, hours) 219,000ET = Exposure Time (hours per day) 8 (hours/day)ATc = Averaging Time (Carcinogenic, hours)613,200EF = Exposure Frequency (days per year) 250 (days/year) TCR = Target Cancer Risk1.00E-05ED = Exposure Duration (years)25 (years) THI = Target Hazard Index 1Toxicity ValuesSourceTarget Indoor Air Conc for CarcinogensTarget Indoor Air Conc for Non-CarcinogensTable 2: Calculation of Preliminary Risk Goals for Indoor Air Concentrations - Office WorkerAtherton Mill PropertyCharlotte, North CarolinaAMEC Project: 6228-12-0051