1 1 2 SUPPLEMENTAL APPENDIX: NOISE EXPOSURE QUESTIONNAIRE The NEQ developed by Megerson (2010) was used in this study to quantify subjects’ 3 noise exposure background (NEB). The NEQ specifically assesses nine categories of noisy 4 activities by querying the frequency and duration of exposure. Responses were rated 5 categorically and assigned a numerical value (frequency: daily=200; weekly=50; monthly=12; 6 every few months=1; never=0; duration: 8 hrs or more=8; 4 to 8 hrs=6; 1 to 4 hrs=3; less than 1 7 hr=1). These values were used to estimate the total number of hrs spent in a given situation over 8 the past year. Exposure doses (D) using the following equation were computed for the nine noise 9 activities: 10 11 πΆ π· = [ ] × 100 π In the dose equation, C refers to the number of hrs/yr reported by the subject for the noisy 12 activity. To calculate C for questions relating to occupational noise exposure, subjects report on 13 average how many hrs/wk and how many wks they worked in a yr. For non-occupational noise 14 exposures, C is the multiplication of the assigned numerical values for the frequency and 15 duration of the noise exposure (e.g., weekly exposure to power tools for 1 to 4 hrs would yield 16 C=50x3=150 hrs). T represents the number of hrs/yr at which the activity is considered 17 hazardous using the NIOSH recommended exposure limit (REL) for noise (79 dBA with a 3-dB 18 exchange rate is the annual equivalent of the NIOSH 85 dBA REL): 19 20 π= 8760 2( πΏ−79⁄ ) 3 L is the continuous equivalent sound level in dB LAeq derived from the literature for that 21 specific noise exposure type. The L for each of the nine noisy activities categories are as follows: 22 power tools, 94 dB LAeq; heavy equipment/machinery, 97 dB LAeq; commercial 2 23 sporting/entertainment events, 94 dB LAeq; motorized vehicles, 98 dB LAeq; small/private aircraft, 24 91 dB LAeq; musical instrument playing, 87 dB LAeq; music listening via personal earphones, 76 25 dB LAeq; music listening via audio speakers, 78 dB LAeq; occupational exposure, 90 dB LAeq (all 26 from Megerson, 2010). 27 Because the LAeq8760h is an estimate of the amount of noise exposure encountered in one 28 yr, or 8760 hrs, the noise level of routine activities (e.g., shopping, eating, driving a car, etc.) not 29 readily associated with high noise environments also needs to be taken into account and a dose 30 percent needs to be calculated. The duration of the amount of time (C) spent engaging in routine 31 activities is calculated as 8760 hrs minus the subject’s reported number of hrs spent in the nine 32 noisy activity categories assessed by the NEQ (i.e., the remaining hrs in a year). The level (L) of 33 routine activities was defined as 64 dB LAeq (Neitzel et al., 2004a,b). 34 The ten doses were added arithmetically, resulting in a dose reflective of the overall 35 amount of time spent annually in noisy environments relative to NIOSH dose requirements. A 36 dose < 100% can be interpreted as not exceeding NIOSH recommendations and a dose > 100% 37 can be interpreted as exceeding NIOSH recommendations of what is considered a safe listening 38 environment (i.e., 79 dBA REL for 8760 hrs and a 3 dB exchange rate). The overall dose percent 39 is necessary to compute the LAeq8760h using the following equation: 40 41 42 43 π· πΏπ΄ππ8760β = [10 × log10 ( )] + 79 100 To demonstrate how individual responses on the NEQ affect the resulting LAeq8760h, two examples of NEQ calculations are listed below: 3 Example 1: Individual with a high NEB Reported hrs (C) L (LAeq) Reference hrs (T) D (%) Never (0) n/a 0 94 274 0% Heavy equipment & machinery Never (0) n/a 0 97 137 0% Commercial sporting & entertainment events Weekly (50) 4 to 8 hrs (6) 300 94 274 109.59% Motorized vehicles Never (0) n/a 0 98 109 0% Small/private aircraft Never (0) n/a 0 91 548 0% Musical instrument playing Daily (200) 1 to 4 hrs (3) 600 87 1380 43.49% Music listening via personal earphones Every few months (1) Less than 1 hr (1) 1 76 17520 0% Music listening via audio speakers Daily (200) Less than 1 hr (1) 200 78 11037 1.81% Occupational exposure Never (0) 0 90 690 0% 7659 64 280320 2.73% Activity Response Power tools Routine activities Total Dose 157.63% LAeq8760h 44 45 46 47 48 81 4 Example 2: Individual with a low NEB Reported hrs (C) L (LAeq) Reference hrs (T) D (%) Never (0) n/a 0 94 274 0% Heavy equipment & machinery Never (0) n/a 0 97 137 0% Commercial sporting & entertainment events Every few months (1) 1 hr to 4 hrs (3) 3 94 274 1.1% Motorized vehicles Every few months (1) Less than 1 hr (1) 1 98 109 0.92% Small/private aircraft Never (0) n/a 0 91 548 0% Musical instrument playing Never (0) n/a 0 87 1380 0% Music listening via personal earphones Every few months (1) Less than 1 hour (1) 1 76 17520 0.01% Music listening via audio speakers Daily (200) Less than 1 hour (1) 200 78 11037 1.81% Occupational exposure Never (0) 0 90 690 0% 8555 64 280320 3.05% Activity Response Power tools Routine activities Total Dose 6.89% LAeq8760h 49 67