chronic health effects and injury associated with environmental noise pollution · 2018-05-17 ·...

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Chronic health effects and injury associated with environmental noise pollution Rick Neitzel, PhD, CIH, FAIHA Associate Professor and Associate Chair University of Michigan Department of Environmental Health Sciences Centers for Disease Control and Prevention, 17 May 2018

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  • Chronic health effects and injury associated with environmental noise

    pollution

    Rick Neitzel, PhD, CIH, FAIHA Associat e Professo r an d Associat e Chair

    Universit y of Michigan Department of Environmental Healt h Sciences

    Centers for Disease Control and Prevention, 17 May 2018

  • • Substantial adverse public health impacts

    – Likely among most common exposures

    • Treated differently than other pollutants

    – Air, water, soil, food, etc

    – Ignored in US for 40 yrs

    Introduction to noise pollution CDC National Environmental Public Health Tracking

    Noise?

    https://ephtracking.cdc.gov/showRiskLandingSolution.action

    2

    https://ephtracking.cdc.gov/showRiskLandingSolution.action

  • Noise exposure: measurements

    • Area measurements

    • Personal measurements

    • Models

    • Usually focus on average or maximum exposure

    3

  • Noise exposure: units, weighting

    4

    http://www.cirrusresearch.co.uk/blog/wp-content/uploads/2011/08/Frequency-Weighting-Curves.jpg

    1X

    10X

    100X

    1000X

    10,000X

    70 dB 80 dB 90 dB 100 dB 110 dB

    Units: decibels (dB)

    A-weighting typically used

  • Noise exposure: quantification

    • Equivalent continuous noise level (LEQ) is foundation of noise exposure assessment

    https://www.fhwa.dot.gov/Environment/noise/regulations_and_guidance/analysis_and_abatement_guidance/fig1.gif

    https://www.fhwa.dot.gov/Environment/noise/regulations_and_guidance/analysis_and_abatement_guidance/fig1.gif

  • +10 dB

    �Day | Night�

    Common environmental noise metrics

    1. LEQ – Assumes all periods contribut e equall y t o risk

    2. LDN (Day-Nigh t Level )

    – LEQ wit h 1 0 dB penalt y adde d fo r nighttim e nois e (1 0 PM t o 7 AM)

    – Accounts fo r increase d sensitivity/ disruptio n at night

  • What do we know about US occupational noise?

    • Occupational Safety and Health Administration (OSHA) measurements

    – ~750,000 Permissible Exposure Limit (PEL)

    – ~320,000 Action Level (AL)

    Sayler et al, manuscript submitted

    7

  • What do we know about US environmental noise?

    • From 1981 until very recently, not much

    • Several efforts in last recent years have shed light on ambient noise levels in US

    – Additional efforts at local (i.e., city) level

    • Most efforts based on modeling; few on measurements

    EPA, 1981

    8

  • Why differentiate modeling from measurements?

    9

  • Noise map: modeled road and air, dBA

    United States

    https://www.transportation.gov/highlights/national-transportation-noise-map

    10

    https://www.transportation.gov/highlights/national-transportation-noise-map

  • Noise map: modeled road and air, dBA

    Atlanta

    https://www.transportation.gov/highlights/national-transportation-noise-map

    11

    https://www.transportation.gov/highlights/national-transportation-noise-map

  • Noise map: modeled road and air, dBA

    CDC

    https://www.transportation.gov/highlights/national-transportation-noise-map

    12

    https://www.transportation.gov/highlights/national-transportation-noise-map

  • Noise map: modeled conditions, dBA

    CDC

    https://www.nps.gov/subjects/sound/soundmap.htm

    13

    https://www.nps.gov/subjects/sound/soundmap.htm

  • Noise map: modeled…?

    Atlanta

    http://howloud.com/

    14

    http:http://howloud.com

  • Noise map: modeled road, dBA

    http://maps.sfplanning.org/Noise.pdf

    15

    http://maps.sfplanning.org/Noise.pdf

  • Noise map: measured, dBA

    http://boston.noiseandthecity.org/a-weighted-sound-levels-by-dba-day

    Boston

    16

  • Noise map: measured, dBA

    McAlexander et al. Environ Health 2015.

    Manhattan

    17

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    Exp

    osu

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    Noise maps are great. But they will never be enough

    • Do not account for variations in behavior, activities

    • Do not estimate personal exposures

    • Often do not account for temporal variability

    • Questionable assumptions, validation?

    40

    50

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    Exposure

    Time

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    6:00

    Expo

    sure

    7:30 9:00 10:30 12:00 13:30 15:00 16:30

    18

  • If you remember nothing else today…

    • Three equally important components for any environmental exposure

    – Exposure frequency (how often)

    – Exposure duration (how long)

    – Exposure intensity/level (how much)

    • Without information about all three, cannot estimate health risk

    +

    19

  • Personal monitoring gets us all three

    91% of 4436 NYC subjects > EPA

    limit from all noise sources combined

    and at risk of NIHL; mean 76.8

    dBA

    EPA recommended

    annual limit

    Neitzel et al,

    Environ Sci Tech,

    2011

    Noise maps would suggest exposures of 55-80 dBA

    20

  • What personal monitoring shows

    Primary exposure source for 59% of 4436 subjects = music! Neitzel et al, Environ Sci Tech, 2011

    21

  • Conclusions: noise exposure

    • Need better estimates of noise exposure in US

    • Use combination of mapping and personal measurements

    • Exposure estimates essential to evaluate public health impacts Hammer et al, Environ Health Persp, 2014

    22

  • Health effects of environmental noise

    • Noise-induced hearing loss (duh)

    • Cardiovascular disease (ischemic heart disease, hypertension)

    • Injuries?

    • Diabetes and/or endocrine disruption?

    • Psychological/mental health effects?

    • Cognitive effects? https://www.pinterest.com/pin/464081936578774649/

    23

    https://www.pinterest.com/pin/464081936578774649

  • Noise-induced hearing loss (NIHL)

    • Chronic exposures cause metabolic damage to cochlea, eventual cell death

    – Neuronal destruction possible � adequate detection, poor understanding

    – Well-understood dose-response; risk begins at 70 dBA LEQ(24)

    • Mechanical damage (acoustic trauma)

    www.osha.gov/dts/osta/otm/new_noise/• Tinnitus and hyperacusis 24

    www.osha.gov/dts/osta/otm/new_noise

  • NIHL in US children

    Su et al, JAMA-OHNS, 2011

    25

  • NIHL in US adults

    CDC, MMWR, 2017 Hoffman et al, JAMA-OHNS, 2016

    26

  • Economic impacts of NIHL

    • HL in estimated 13.4% of working population

    • Impacts on those with HL

    – Reduced wages (25% less than normal hearing)

    – 2.5 times as likely to be unemployed

    • If the 20% of HL from noise were prevented

    – $58-152B benefit annually ($123B core estimate)

    • Conservative; does not consider additional costs

    – Health care and special education

    27 Neitzel et al, JSLHR, 2017

  • Noise and cardiovascular

    disease

    Babisch W, N ise Health, 2004

    28

  • Evidence fo r noise ���� CVD

    • Consistent associations

    – Mixed study designs, locations, durations

    – Mainly airport, road noise

    – Effects start at 45-55 dBA LDN – Occupational evidence, too

    • Strong evidence from Europe

    Mainly hypertension, myocardial infarction

    Basner et al, Lancet, 2014 29

  • CVD from noise impacts in US

    • Estimated CVD savings from 5 dB reduction in US population noise in 2014: $3.9 billion

    Swinburn et al, Am J Prev Med, 2015

    30

  • Noise and injuries

    Neitzel, manuscript in preparation

    31

  • Evidence fo r noise ���� injuries

    • Moderate evidence from occupational cohort studies

    – Acute injuries, mild to serious

    – Consistent associations

    – Effects start ~85 dBA 8-hr LEQ

    • Environmental noise studies lacking

    Mixed study designs, locations, durations

    Neitzel et al, Ann Occup Hyg, 2016 32

  • Noise and diabetes

    Jerrett et al, Environ Health, 2014

    33

  • Noise and diabetes

    • Few studies, many ecological study design

    – Long-term and short-term road noise increased risk of diabetes mortality in men in Barcelona (Barcelo et al, Environ Res, 2016; Recio et al, Environ Res, 2016)

    – 10 dB increase in long-term road noise increased risk of diabetes in Denmark (Sørensen et al, Environ Health Persp, 2013)

    – No clear associations between long-term air traffic noise and diabetes (Eriksson et al, Environ Health Persp, 2014)

    • Some evidence, no clear threshold

    34

  • Noise and mental health effects

    Van Kempen et al, Environ Health Persp, 2002

    35

  • Evidence fo r noise ���� mental health

    • Few studies, limited range of designs

    • Several studies showed increased behavioral problems in children exposed to noise

    • One study showed increased dementia-related emergencies with higher noise

    • Some evidence, no clear threshold Orban et al, Environ Health Persp, 2016

    36

  • Noise and cognitive effects

    Ising et al, Noise Health, 2004

    37

  • Evidence fo r noise ���� cognitive effects

    • Limited number of studies, primarily on children

    • memory, executive function with increased noise

    • Moderate evidence, no clear threshold

    Elmenhorst et al, Int Arch Occup Environ Health, 2010

    Several show reduced reading comprehension,

    38

  • CD C systematic review of noise effects

    • Hearing loss

    • Ischemic heart disease

    • Hypertension

    • Psychological or mental health issues

    • Injuries

    • Endocrine disruption

    • Cancer/tumorigenesis

    • Cognition

    • Sleep disturbance

    • Low birthweight or premature birth

    • Obesity/overweight

    39

  • Goals of systematic review

    • Evaluate association between noise exposure and each health impact

    – What noise levels, and for how long, are associated with each health impact?

    • Evaluate strength of evidence

    • Recommend “safe” exposure limits https://ntp.niehs.nih.gov/pubhealth/hat/review/index-2.html

    40

    https://ntp.niehs.nih.gov/pubhealth/hat/review/index-2.html

  • Example “safe” NIHL exposure limits

    • Occupational Safety and Health Administration

    – 8-hr Permissible Exposure Limit of 90 dBA

    – Will result in NIHL in >25% of individuals after 40 years

    • National Institute for Occupational Safety and Health

    – 8-hr Recommended Exposure Limit of 85 dBA

    – Will result in NIHL in 8% of exposed individuals after 40 years

    41

  • Example “safe” NIHL exposure limits

    • European Union

    – 8-hour Lower Action Value of 80 dBA

    – Will result in NIHL in

  • “Safe” limits for other health effects

    • WHO has recommendations to protect against other effects

    – Sleep disturbance, speech intelligibility, annoyance

    • ACGIH* noted in 2018 that CVD possible 85 dBA 8-hr occupational exposure

    WHO, 1999

    *American Conference of Governmental Industrial Hygienists 43

  • Conclusions

    • Need to protect public health

    – Exposures substantial, widespread, cumulative across sources and lifetime

    • Exposure assessment challenging

    • Health impacts extend beyond NIHL

    • Exposure limits and interventions needed to improve health http://sunnyspellsandscatteredshowers.org/tip-of-the-iceberg/

    44

    http://sunnyspellsandscatteredshowers.org/tip-of-the-iceberg

  • For More Information

    • Rick Neitzel, [email protected] or 734-763-2870

    • University of Michigan Exposure Research Lab

    – https://umexposureresearch.org/

    45

    http:https://umexposureresearch.orgmailto:[email protected]

    Structure BookmarksChronic health effects and injury associated with environmental noise pollution Rick Neitzel, PhD, CIH, FAIHA Associat e Professo r an d Associat e Chair Universit y of Michigan Department of Environmental Healt h Sciences Introduction to noise pollution Noise exposure: measurements Noise exposure: quantification Common environmental noise metrics What do we know about US occupational noise? What do we know about US environmental noise? Why differentiate modeling from measurements? Noise map: modeled road and air, dBA Noise map: modeled road and air, dBA Noise map: modeled road and air, dBA Noise map: modeled conditions, dBA Noise map: modeled…? Noise map: modeled road, dBA Noise map: measured, dBA Noise map: measured, dBA Noise maps are great. But they will never be enough If you remember nothing else today… Personal monitoring gets us all three What personal monitoring shows Conclusions: noise exposure Health effects of environmental noise Noise-induced hearing loss (NIHL) NIHL in US children NIHL in US adults Economic impacts of NIHL Noise and cardiovascular disease Evidence fo r noise .... CVD CVD from noise impacts in US Noise and injuries Evidence fo r noise .... injuries Noise and diabetes Noise and diabetes Noise and mental health effects Evidence fo r noise .... mental health Noise and cognitive effects Evidence fo r noise .... cognitive effects CD C systematic review of noise effects Goals of systematic review Example “safe” NIHL exposure limits Example “safe” NIHL exposure limits “Safe” limits for other health effects Conclusions For More Information