Climate impact on ambient PM 2.5 elemental concentration in the - - PowerPoint PPT Presentation

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Climate impact on ambient PM 2.5 elemental concentration in the - - PowerPoint PPT Presentation

Climate impact on ambient PM 2.5 elemental concentration in the United States: a trend analysis over the last 30 years Weeberb Requia, Iny Jhun, Brent Coull, Petros Koutrakis Harvard University June, 2019 HSPH/MIT ACE Center RD83587201


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Climate impact on ambient PM2.5 elemental concentration in the United States: a trend analysis over the last 30 years

Weeberb Requia, Iny Jhun, Brent Coull, Petros Koutrakis Harvard University June, 2019 HSPH/MIT ACE Center – RD83587201

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Back Background und

  • Weather impacts on the chemical composition of PM2.5 varies

significantly over space and time

  • Diversity of particle components and the complex mechanisms

governing particle formation and removal

Temperature

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Ob Obje jectives

  • We quantified the impacts of climate change on ambient PM2.5

composition and levels in the US.

  • Specifically, we performed a trend analysis based on a large temporal

datasets of PM2.5 species concentrations and weather over the last 30 years.

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Ai Air q quality a and w weather d data c col

  • llection
  • n
  • We evaluated the impacts of weather changes on seven major

components of ambient PM2.5, including elemental carbon (EC),

  • rganic carbon (OC), nitrate, sulfate, sodium (Na+), ammonium, and

silicon.

  • Daily air pollution data for the period 1988 and 2017 were obtained

from the US Environmental Protection Agency (EPA)

  • Meteorological data were provided by the National Oceanic

Atmospheric Administration’s National Climatic Data Center (NOAA)

  • temperature
  • wind speed
  • relative humidity
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St Statistical a analysis

  • Step 1:
  • Past weather changes in ground-level temperature, wind speed, and relative

humidity

  • Step 2:
  • Weather-related increases in air pollution

General linear regression model GAM models Analyses were stratified by season (warm and cold) and regions Warm season (May – October); Cold season (November – April)

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Based on the National Mortality Air Pollution Study by HEI

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St Statistical ana nalysis

(step 2: Weather-related increases in air pollution)

§ Adjusted model:

Y = α + β!"#$%&'" %&'( + γ month + σ weekdays + s( temp + s) ws + s* rh + e

§ Unadjusted model: Y = α + β$+!"#$%&'" %&'( + γ month + σ weekdays + e

  • While the weather impact is incorporated into the unadjusted trends, the adjustment with

weather variables in model 1 removes the impact of inter-annual weather variation on air pollution trends.

  • We considered that any differences between the unadjusted and weather-adjusted trends

are entirely attributable to the impact of long-term weather changes.

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St Statistical ana nalysis

(step 2: Weather-related increases in air pollution)

β!"#$%&'" and β$(!"#$%&'" values to quantify past weather-related increases β$(!"#$%&'" − β!"#$%&'"

“Weather penalties”

A positive penalty (β$(!"#$%&'" > β!"#$%&'") suggests that an increase in species p of PM2.5 is associated with long-term weather changes in 1988-2017.

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St Statistical ana nalysis

(step 2: Weather-related increases in air pollution)

  • Bootstrap analysis to estimate standard error
  • Meta-analysis.

Adjusted Unadjusted Penalties

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Re Results (w (weath ther tr trends) )

  • Temperature increased in four regions:
  • Industrial Midwest (IM) and North East (NE) during the warm and cold season
  • Upper Midwest (UM) and West (W) only in the cold season.
  • NE was the region with the highest increases in the study period (1988-2017).
  • annual increase of 0.036 ºC (95% CI: 0.035; 0.037) during the warm season
  • annual increase of 0.031 ºC (95% CI: 0.030; 0.032) during cold season
  • Wind speed decreased in all regions (both warm and cold seasons), except in

the SW region during the cold season.

  • Trends of relative humidity varied significantly by season and region
  • During the warm season, relative humidity increased in most regions. Only the West

Coast regions (NW and W) exhibited decreases in relative humidity.

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Spatial distribution of weather penalties for each ch speci cies of PM2.

2.5, r

, region ( n (and na nd nationa nal me meta-an analy alysis is), an and seas ason in in 1988 – 2017 2017

Note: unit of the scale of the bar charts (µg/m3).

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Re Results (Tot

  • tal

al weath ther penalty alty betw tween 1988 an and 2017)

Cold season

  • EC: 0.037 µg/m3 (95%CI: 0.019 ; 0.055)
  • OC: 0.19 µg/m3 (95%CI: 0.16; 0.22)
  • Nitrate: 0.056 µg/m3 (95%CI: 0.048 ; 0.064 )
  • Sulfate: 0.04 µg/m3 (95%CI: 0.003 ; 0.06)
  • Sodium: -0.011 µg/m3 (95%CI: -0.004;-0.017 )
  • Ammonium: -0.024 µg/m3 (95%CI:-0.017;-0.066)
  • Silicon: 0.020 µg/m3 (95%CI: 0.012 ; 0.028)

Warm season

  • EC: 0.036 µg/m3 (95%CI: 0.032 ; 0.039)
  • OC: 0.21 µg/m3 (95%CI: 0.15 ; 0.24)
  • Nitrate: 0.039 µg/m3 (95%CI: 0.001; 0.08)
  • Sulfate: 0.35 µg/m3 (95%CI: 0.20; 0.47)
  • Sodium: -0.014 µg/m3 (95%CI:-0.017;-0.010 )
  • Ammonium: 0.074 µg/m3 (95%CI:0.04; 0.19 )
  • Silicon: 0.026 µg/m3 (95%CI: 0.023 ; 0.028 )
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Co Conclusio nclusions ns

  • Ambient PM2.5 components are strongly linked to weather variables

such as temperature, relative humidity, and wind conditions.

  • Our findings suggest that weather changes over the last 30 years

increased the ambient concentration of most PM2.5 components in the US.