SUPPLEMENTAL MATERIAL Table S- 1. Detection limits (DL) of 63 volatile organic compounds that were tested in this study. DL Compound DL CAS No. Compound CAS No. µg/m3 Propylene 115-07-1 DL Compound CAS No. µg /m3 8 2-Butanone (MEK) µg /m3 78-93-3 10 Dibromochloromethane 124-48-1 40 cis-1,2Freon-12 75-71-8 20 Dichloroethylene 156-59-2 20 Methyl Isobutyl Ketone 108-10-1 80 Chloromethane 74-87-3 20 n-Hexane 110-54-3 20 Methyl Butyl Ketone 591-78-6 80 Freon-14 75-73-0 30 Ethyl Acetate 141-78-6 20 1,2-Dibromoethane 106-93-4 40 Vinyl Chloride 75-01-4 10 Chloroform 67-66-3 20 Tetrachloroethylene 127-18-4 30 1,3-Butadiene 106-99-0 10 Tetrahydrofuran 109-99-9 20 Chlorobenzene 108-90-7 20 Bromomethane 74-83-9 20 1,2-Dichloroethane 107-06-2 20 Ethylbenzene 100-41-4 20 Chloroethane 75-00-3 10 1,1,1-Trichloroethane 71-55-6 30 Bromoform 75-25-2 50 108-38Vinyl Bromide 593-60-2 20 Cyclohexane 110-82-7 20 m/p-xylene 3/106-42-3 40 Freon-11 75-69-4 30 Carbon Tetrachloride 56-23-5 30 Styrene 100-42-5 20 Isopropyl alcohol 67-63-0 20 Benzene 71-43-2 20 o-xylene 95-47-6 20 Acetone 67-64-1 10 1,4-Dioxane 123-91-1 70 1,1,2,2-Tetrachloroethane 79-34-5 30 2,2,41,1-Dichloroethene 75-35-4 20 Trimethylpentane 540-84-1 20 4-Ethyltoluene 622-96-8 20 Methylene Chloride 75-09-2 20 n-Heptane 142-82-5 20 1,3,5-Trimethylbenzene 108-67-8 20 Freon-113 76-13-1 40 1,2-Dichloropropane 78-87-5 20 1,2,4-Trimethylbenzene 95-63-6 20 Allyl Chloride 107-05-1 20 Trichloroethylene 79-01-6 30 1,3-Dichlorobenzene 541-73-1 30 75-27-4 30 Benzyl Chloride 100-44-7 30 10061-01-5 20 1,4-Dichlorobenzene 106-46-7 30 95-50-1 30 Bromodichlorometha Carbon Disulfide 75-15-0 Trans-1,2Dichloroethene 20 ne cis-1,3- 156-60-5 Methyl Tert-Butyl 20 Dichloropropene trans-1,3- 20 Ether 1634-04-4 20 Dichloropropene 10061-02-6 1,2-Dichlorobenzene 1,1-Dichloroethene 75-35-4 20 1,1,2-Trichloroethane 79-00-5 30 1,2,4-Trichlorobenzene 120-82-1 40 Vinyl acetate 108-05-4 20 Toluene 108-88-3 20 Hexachloro-1,3-Butadiene 87-68-3 50 Table S- 2. Temperature and RH outdoors and in sampling apartments from 2004 to 2006 Indoors Outdoors Rainy day Year and dates N Mean Min Max Standard deviation N Mean Temperature (oC) 10/12/2004-10/13/2004 17 23.3 22.3 24.1 0.5 3 15.4 None 10/24/2005-10/27/2005 17 22.6 20.9 24.6 1.0 3 8.7 10/24, 25, 26 11/14/2006-11/16/2006 17 23.7 22.5 24.7 0.6 2 15.8 11/14, 16 10/12/2004-10/13/2004 17 43.6 37.2 52.3 4.5 3 63.6 None 10/24/2005-10/27/2005 17 35.9 27.3 46.3 4.2 3 78.9 10/24, 25, 26 11/14/2006-11/16/2006 17 56.4 44.3 67.5 5.7 2 83.0 11/14, 16 Relative humidity (%) Table S- 3. CO2 and CO levels in the apartments. Year and date N Median Minimum Maximum CO2 (ppm) 10/28/2003 17 436 405 895 10/13/2004 17 536 441 733 10/25/2005 17 485 423 587 11/14/2006 17 554 468 689 10/24/2007 17 561 456 750 10/28/2003 17 0.9 0.4 1.5 10/13/2004 17 1.5 1.1 2.2 10/25/2005 17 0.9 0.2 1.8 11/14/2006 17 1.4 1.0 2.8 10/24/2007 17 1.2 0.7 1.6 CO (ppm) Table S- 4. Median PM10 and PM2.5 concentrations. Outdoors Indoors (µg/m3) (µg/m3) Year N Min 25th 50th 75th percentil percentil percentil e e e Max N Median PM10 2003 20 <1 <1 <1 <1 2 3 8 2004 17 <1 1 3 6 10 3 17 2005 18 <1 <1 <1 1 22 4 5 2006 17 <1 1 3 16 34 1 23 2007 17 <1 1 2 4 28 - - All years 89 <1 <1 1 3 34 11 8 PM2.5 2004 17 <1 <1 <1 1 3 3 3 2005 18 <1 <1 <1 <1 1 4 1 2006 17 <1 <1 1 6 15 1 6 2007 17 <1 <1 <1 <1 7 - - All 69 years <1 <1 <1 1 15 8 1 Table S- 5. TVOC concentrations including and excluding acetone, isopropyl alcohol and ethyl acetate (µg/m3). Location N Min1 In the apartments 85 <10 (< 10)2 130 (20) 350 (216) 2340 (2330) Hallway 15 40 (<10) 90 (30) 396 (314) 500 (500) Supply air 33 20 (<10) 130 (30) 412 (216) 26000 (960) Outdoor air 9 < 10 (<10) 70 (20) 494 (376) 1550 (1520) Median 90th percentile 1. Data in parentheses exclude acetone, isopropyl alcohol and ethyl acetate. 2. 10 indicate that all VOCs were below reporting detection limit. Max Table S- 6. Concentrations of detected VOCs and possible sources (µg/m3). N of Compounds 1 1 N Median th 1 90 percentile Chro Cancer nic -based REL exposur 2 e conc.3 1 Maximum detected1 Sources [1] Household and consumer products (i.e., cleaning agents, insecticides, Acetone 85 (33/9) 83 (31/8) 60 (50/30) 150 (120/50) 700 (210/70) NA4 NA cosmetic products); building products (i.e., paints, adhesives, particleboard) Household and consumer products Isopropyl alcohol 85 (33/9) 47 (13/3) 20 (<20/<20) 60 (60/70) 760 (210/110) 7000 NA (i.e., cleaning agents); building products (i.e., coatings, particleboard) Household and consumer products (i.e., shoe polish, hair spray, incense); Toluene 85 (33/9) 38 (19/4) <20 (20/<20) 80 (140/<20) 180 (220/1390) 300 NA cooking; building products (i.e., paint, adhesives, carpets, particleboard); electronic devices (i.e., printers, computers); gasoline emissions from outdoors m/p-Xylene 85 (33/9) 7 (3/0) <40 (<40/<40) <40 (40/<40) 280 (250/<40) 700 NA Household and consumer products (i.e., cleaning agents, shoe polish, incense); cooking; building products o-Xylene 85 (33/9) 6 (2/0) <20 (<20/<20) <20 (<20/<20) 100 (120/<20) 700 NA (i.e. table printers); gasoline emissions from outdoors Household and consumer products Carbon disulfide 85 (33/9) 5 (2/0) <20 (<20/<20) <20 (<20/<20) 160 (150/<20) 800 NA (i.e., insecticides) Building products (i.e., paints, n-Hexane 85 (33/9) 5 (4/1) <20 (<20/<20) <20 (<20/<20) 70 (40/130) 7000 NA adhesives) 1,2,4- Building products (i.e., paints); 85 (33/9) 5 (3/0) <20 (<20/<20) <20 (<20/<20) 40 (190/<20) NA NA Trimethylbenzene gasoline emissions from outdoors Building products (i.e., coatings, Methyl ethyl ketone 85 (33/9) 3 (3/0) <10 (<10/<10) <10 (<10/<10) 70 (20/<10) NA NA particleboard) Ethyl acetate Household and consumer products 85 (33/9) 3 (1/0) <20 (<20/<20) <20 (<20/<20) 60 (20/<20) NA NA (i.e., cleaning agents, insecticides, cosmetic products); building products (i.e., coatings, adhesives) Household and consumer products Methylene chloride 85 (33/9) 2 (1/0) <20 (<20/<20) <20 (<20/<20) 20 (20/<20) 400 10 (i.e., hair spray, incense) Cooking; building products (i.e., paints, adhesives, carpets); electronic Ethylbenzene 85 (33/9) 2 (2/0) <20 (<20/<20) <20 (<20/<20) 50 (50/<20) 2000 4 devices (i.e., printers); gasoline emissions from outdoors Household and consumer products (i.e., incense); building products (i.e., Styrene 85 (33/9) 2 (1/0) <20 (<20/<20) <20 (<20/<20) 2200 (30/<20) 900 NA adhesives, carpets); electronic devices (i.e., printers) Household and consumer products (i.e, n-Heptane 85 (33/9) 1 (0/0) <20 (<20/<20) <20 (<20/<20) 30(<20/<20) NA NA insecticides, cosmetic products); building products (i.e., paints) Methyl tert-butyl Fuel additive to improve combustion 85 (33/9) Ether 0 (2/0) <20 (<20/<20) <20 (<20/<20) <20 (40/<20) 8000 300 in vehicle motors Building products (i.e., paints, Cyclohexane 85 (33/9) 1 (0/0) <20 (<20/<20) <20 (<20/<20) 100 (<20/<20) NA NA adhesives) Household and consumer products Trichloroethylene 85 (33/9) 1 (0/0) <30 (<30/<30) <30 (<30/<30) 210 (<30/<30) 600 5 (i.e., drycleaned clothes, spot removers, fabric/ leather cleaners) Building products (i.e., paints, carpets, 4-Ethyltoluene 85 (33/9) 0 (1/0) <20 (<20/<20) <20 (<20/<20) <20 (30/<20) NA NA particleboard) Building products (i.e., paints, Propylene 85 (33/9) 0 (1/0) <8 (<8/<8) <8 (<8/<8) <8 (12/<8) 3000 NA adhesives, carpets) Methyl isobutyl 85 (33/9) 1 (0/0) <80 (<80/<80) <80 (<80/<80) 150 (<80/<80) NA NA Building products (i.e., adhesives) ketone Household and consumer products Tetrachloroethylene 85 (33/9) 1 (0/0) <30 (<30/<30) <30 (<30/<30) 100 (<30/<30) 35 1.69 (i.e., dry cleaned clothes, spot removers, fabric/ leather cleaners) 1. Levels detected in indoor air followed in parentheses by levels detected in the supply air/outdoor air. 2. Chronic RELs were from the California Office of Environmental Health Hazard Assessment (OEHHA).[2] 3. Cancer-based exposure concentrations were calculated using available cancer unit risk estimates (UREs). The risk corresponded to a lifetime incremental risk of one in 105 assuming 70 years of continous exposure.[3] 4. NA: Not available. Table S- 7. Toluene concentrations in indoor air in other studies (µg/m3). Number Studies of Median Mean 90th % References samples This building, 2003 17 70 76.5 170 This study This building, 2004-2007 68 < 20 < 20 110 This study NYC TEACH (winter) 36 Suburban and rural NJ 100 13 60.8 RIOPA-NJ 182 9.7 13 MA 100 7.6 42.5 [4] 17.7 [5] [6] [7] Table S- 8. Formaldehyde concentrations in sampled apartments (ppb). Year N Min 25th Median 75th Max 2003 17 <10 <10 <10 <10 30 2004 17 10 10 10 20 30 2005 17 <7 <7 <7 8 95 2006 17 1 4 6 7 24 2007 17 5 16 37 82 350 Table S- 9. Comparison of formaldehyde concentrations to other studies (ppb). Studies N Median This building, 2003 - 2006 68 < 10 This building, 2007 17 37 RIOPA, apartments 67 16 RIOPA, overall 353 16.3 NHEXAS, Arizona 189 17.1 NYC TEACH 38 Mean 69 90th 95th Max Reference 20 95 This study 198 350 This study [8] [9] 26.4 37.4 9.8 332 [10] [4] REFERENCES [1] Salthammer, T.; Uhde, E. Emission studies. In Organic indoor air pollutants: occurrence, measurement, evaluation, 2nd Ed.; Wiley-VCH: New York, NY, 2009; 349-430. [2] Office of Environmental Health Hazard Assessment (OEEHA). Acute, 8-hour and Chronic Reference Exposure Level (REL)s. OEEHA. California Environmental Protection Agency: Sacramento, CA. http://www.oehha.ca.gov/air/allrels.html (accessed 3/8/2014). [3] Logue, J.M.; McKone, T.E.; Sherman, M.H.; Singer, B.C. Hazard assessment of chemical air contaminants measured in residences. Indoor Air 2011, 21 (2), 92-109. [4] Kinney, P.L.; Chillrud, S.N.; Ramstrom S.; Ross J.; Spengler, J.D. Exposures to multiple air toxics in New York City. Environ. Health Persp. 2002, 110 (Suppl 4), 539-546. [5] Weisel, C.P.; Alimokhtari, S.; Sanders, P.F. Indoor air VOC concentrations in suburban and rural New Jersey. Environ. Sci. Technol. 2008, 42 (22), 8231-8238. [6] Weisel, C.P.; Zhang, J.J.; Turpin, B.J.; Morandi, M.T.; Colome S.; Stock, T.H.; Spektor, D.M.; Korn L.; Winer A.; Kwon J.; Meng, Q.Y.; Zhang L.; Harrington R.; Liu W.; Reff A.; Lee, J.H.; Alimokhtari S.; Mohan K.; Shendell D.; Jones J.; Farrar L.; Maberti S.; Fan, T. Relationships of indoor, outdoor, and personal air (RIOPA). Part I. Collection methods and descriptive analyses. Res. Rep. - Health Eff. Inst 2005, 130 Pt 1, 1-107. [7] Rago, R.; McCafferty, R.; Rezendes, A. Summary of residential indoor air quality data. Massachusetts Indoor Air Background Study. Haley and Aldrich: Boston, MA, 2005. [8] Hun, D.E.; Corsi, R.L.; Morandi, M.T.; Siegel, J.A. Formaldehyde in residences: long-term indoor concentrations and influencing factors. Indoor Air 2010, 20 (3), 196-203. [9] Liu, W.; Zhang, J.; Zhang, L.; Turpin, B.J.; Weisel, C.P.; Morandi, M.T.; Stock, T.H.; Colome, S.; Korn, L.R. Estimating contributions of indoor and outdoor sources to indoor carbonyl concentrations in three urban areas of the United States. Atmos. Environ. 2006, 40 (12), 2202-2214. [10] Gordon, S.; Callahan, P.; Nishioka, M.; Brinkman, M.; O'Rourke, M.; Lebowitz, M.; Moschandreas, D. Residential environmental measurements in the National Human Exposure Assessment Survey (NHEXAS) pilot study in Arizona: preliminary results for pesticides and VOCs. J. Expo. Anal. Env. Epid. 1999, 9 (5), 456-470.