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A Multivariate Dynamic Spatial Factor Model for
Speciated Pollutants and Adverse Birth Outcomes
Montse Fuentes
Virginia Commonwealth University
August 23, 2017
Joint with with Kimberly Kaufeld, Brian Reich, Amy Herring, Gary Shaw and Maria Terres
Montse Fuentes Multivariate Factor Model for Birth Defects
Why Birth Defects?
Birth defects: a physical or biochemical abnormality that is
present at birth and that may be inherited or the result of
environmental influence.
Around 3% of all births result in a birth defect. Orofacial
defects are the most common.
Cause of cleft palate defects is unknown
Contributes to long-term disability, which may have significant
impacts on individuals, families, health-care systems, and
societies.
Figure: Cleft lip and palate http://www.wetherallgroup.com/cleft-palate/
Montse Fuentes Multivariate Factor Model for Birth Defects
Scientific Motivation
Maternal exposure to air pollutants have been related to
adverse birth outcomes
Preterm birth
Low birth weight
Birth defects, i.e. cleft lip/palate
Researchers believe that exposure to high concentrations of air
pollution during pregnancy may significantly increase the risk
of birth defects and other adverse birth outcomes.
Montse Fuentes Multivariate Factor Model for Birth Defects
Challenges:
Estimating mother’s exposure to pollutants with sparse
monitor locations
Current regulations put limits on total PM2.5 concentrations,
there are many speciated pollutants within this size class that
likely have varying effects on perinatal health.
Correlations between speciated pollutants it can be difficult to
decipher their effects in a model for birth outcomes.
Montse Fuentes Multivariate Factor Model for Birth Defects
Background-Birth Defects and Pollution
Orofacial cleft defects (cleft palate & or lip) appear in the first
trimester, weeks 3-8.
Orofacial cleft associations with air pollution
Gilboa et al. (2005) found a weak association between PM10
and isolated cleft lip with or without cleft palate.
Association of air pollution, CO and ozone, 03, exposure and
oral clefts (Ritz 2002).
Association between traffic density and cleft lip with or
without palate (Padula et al 2013)
Montse Fuentes Multivariate Factor Model for Birth Defects
Pollutant exposure assessment
Pollutant Data and Birth Defects
Mothers pollutant exposure assigned nearest air pollution
monitor (Ritz et al., 2002, Vrijheid et al., 2011).
Generally, mother’s residence is based on the home at time of
birth which doesn’t necessarily correspond to home during first
trimester.
Monitoring stations resulting in similar exposure over long
areas equals a community-wide variation in air pollution.
Montse Fuentes Multivariate Factor Model for Birth Defects
Statistical Challenges
Incorporate spatial analysis of environmental health data,
typically not considered in classical birth defect epidemiological
studies.
Incorporate spatial prediction for pollution to provide
measurements at the pregnant mothers’ homes to be used in a
model for birth outcomes.
Model multivariate birth defects to include multi-pollutant
level data at the same time.
Create statistical models to identify the specific
critical windows and spatial locations during the pregnancy
when high exposures to pollutants more negatively affect the
birth defects.
Characterize different sources of uncertainty in data and
models.
Montse Fuentes Multivariate Factor Model for Birth Defects
California National Birth Defects Data
Live births with and without any known birth defects where
Woman’s date of conception is based upon the estimated date
of delivery, the due date that the woman received from her
physician reported at the study interview; 2003-2006
Cases included live births, and controls are live births without
any known birth defects, identified randomly from selected
hospitals in California
Self reported survey where demographic and behavior
information was reported
There were a total of 208 cleft lip or cleft palate defects
reported and 358 controls
Montse Fuentes Multivariate Factor Model for Birth Defects
Birth Defect Geocoded Data
As part of the study women reported their complete residential
history during pregnancy.
Residences were geocoded each week during the first eight
weeks of pregnancy to assign exposure levels, to account for
mobility of the mothers during the study period
Woman’s date of conception based upon the estimated date of
delivery, due date that the woman received from her physician
which was reported at the study interview
Most of the data was collected in the San Joaquin Valley in
California the initial study region
Approximately 15% of the women moved during the study to
areas outside of the initial study area, with the majority of the
women moving to the San Francisco Bay and Los Angeles area.
Montse Fuentes Multivariate Factor Model for Birth Defects
Birth Defect Geocoded Data
−124 −122 −120 −118 −116 −114
323436384042
Longitude
Latitude
Improve
STN
BD Residence
Fresno CA
Long Beach CA
Los Angeles CA
San Diego CA
San Francisco CA
San Jose CA
Figure: Representative BD Residences and pollutant monitor locations
Montse Fuentes Multivariate Factor Model for Birth Defects
NBDPS data
Covariates include:
Sex of the infant
Maternal age classifications
19 and under (baseline)
20-24
25-29
30-34
35 and older
Prediabetes
Maternal education (high school, some college and college)
High blood pressure during pregnancy
Smoking while pregnant (Yes/No)
Alcohol use while pregnant (Yes/No)
Montse Fuentes Multivariate Factor Model for Birth Defects
Cleft Lip/Palate Data
Montse Fuentes Multivariate Factor Model for Birth Defects
Pollutant Sources
Speciated Pollutants, PM2.5
Figure: PM 2.5 components, source: Guaita et al., 2011
Montse Fuentes Multivariate Factor Model for Birth Defects
Pollution Data
The Air Quality System (AQS) monitoring data
Ambient air pollution data collected by EPA, state, local, and
tribal air pollution control agencies in California
Measurements collected every three to six days for
Interagency Monitoring for Protected Visual Environments
(IMPROVE) - rural sites
STN sites - urban sites
40 monitors in CA where 20 are in the study region
Montse Fuentes Multivariate Factor Model for Birth Defects
Pollutant Data Sources
California, 2003-2006
Ammonium- Weekly average (ug/m3
)
Nitrate (NO3)- Weekly average (ug/m3
)
Sulfate (SO4)- Weekly average (ug/m3
)
Total Carbon- Weekly average (ug/m3
)
Calcium (Ca) - Weekly average (ug/m3
)
Iron (Fe) - Weekly average (ug/m3
)
Potassium (K)- Weekly average (ug/m3
)
Silicon (Si)- Weekly average (ug/m3
)
Sulfur (Su)- Weekly average (ug/m3
)
Montse Fuentes Multivariate Factor Model for Birth Defects
STN and IMPROVE Data Monitors
Figure: Active Monitors, 2003-2006 Blue-IMPROVE, Black-STN
Montse Fuentes Multivariate Factor Model for Birth Defects
Weekly Pollutant Data
Figure: STN and IMPROVE speciated components 2003-2006 weekly
averages for each site where the vertical lines separate each year.
0 50 100 150 200
−4−2024
Week
logAmmonium
STN
Improve
0 50 100 150 200
−4−2024
Week
logNitrate
0 50 100 150 200
−4−20123
Week
logSulfate
0 50 100 150 200
−4−2024
Week
logTotalCarbMass
0 50 100 150 200
−4−3−2−10
Week
logCalcium
0 50 100 150 200
−4−3−2−10
Week
logIron
0 50 100 150 200
−4−2012
Week
logPotassium
0 50 100 150 200
−4−201
Week
logSilicon
0 50 100 150 200−4−201
Week
logSulfur
Montse Fuentes Multivariate Factor Model for Birth Defects
Speciated Pollutant Correlations
Table: Pearson correlation coefficients of weekly speciated pollutants
from stations relevant to the study in the state of California, 2003-2006.
Nitrate Sulfate Total Calcium Iron Potassium Silicon Sulfur
Carbon
Mass
Sulfate 0.41
Total Carbon Mass 0.38 0.05
Calcium 0.03 0.08 0.20
Iron 0.19 0.11 0.48 0.77
Potassium 0.07 0.17 0.08 0.16 0.12
Silicon -0.03 0.01 0.05 0.85 0.78 0.13
Sulfur 0.41 0.97 0.03 0.10 0.12 0.20 0.04
Ammonium 0.96 0.60 0.34 0.05 0.19 0.06 -0.01 0.59
Montse Fuentes Multivariate Factor Model for Birth Defects
Multivariate Spatial-Temporal Model
Our model is a dynamic linear model with observation and
evolution equations.
Let Ytp(s) be the observation at location s on day t = 1, ..., T, for
pollutant p = 1, ..., P, and Yt(s) = [Yt1(s), · · · , YtP(s)]T .
Yt(s) = µt(s) + Λ(s)δt(s) + t(s)
δt(s) = Γ(s)δt−1(s) + wt(s)
where
t(s) = [ t1(s), · · · , tP(s)]T are errors with tj (s) ∼ N(0, σ2)
wt(s) = [wt1(s), · · · , wtM(s)]T denoted wtl ∼ GP[0, s2
w (φw )]
Montse Fuentes Multivariate Factor Model for Birth Defects
Factor model
The factor loading matrix, Λ(s) is:
The effect of factor f on pollutant p is determined by the
(p, f ) element of Λ(s), denoted by λpf (s).
To ensure identification we fix λpf (s) = 0 for f < p and
λpf (s) > 0 for p = 1, ..., M.
To induce spatial smoothness in the loadings log[λpp(s)] and
λpf (s) for f > p are GP[0, s2
Λf ,p
R(φΛf ,p
)].
Montse Fuentes Multivariate Factor Model for Birth Defects
Factor model
The propagation matrix Γ(s) is:
Diagonal with diagonal elements γ1(s), ..., γM(s)
To ensure stationarity in time the factor evolution coefficients
are restricted to the interval (−1, 1)
Yt(s) = µt(s) + Λ(s)δt(s) + t(s)
δt(s) = Γ(s)δt−1(s) + wt(s)
γf ∼ TN(−1,1)[0N, s2
Γf
R(φΓf
)]
λpf (s) ∼ GP[0, s2
Λf ,p
R(φΛf ,p
)]
δf ,0 ∼ GP[0, s2
δf
R(φδf
)]
Montse Fuentes Multivariate Factor Model for Birth Defects
Spatial Dynamic Factor Analysis Model





Y 1
t
Y 2
t
...
Y P
t





=





µ1
1N
µ2
1N
...
µP
1N





+





Λ1
1 Λ1
2 . . . Λ1
m
0 Λ2
2 . . . Λ2
m
...
...
...
...
0 0 . . . ΛP
m










δ1,t
δ2,t
...
δm,t





+





1
t
2
t
...
P
t










δ1,t
δ2,t
...
δm,t





=





Γ1 0 . . . 0
0 Γ2 . . . 0
...
...
...
...
0 0 . . . Γm










δ1,t−1
δ2,t−1
...
δm,t−1





+





w1,t
w2,t
...
wm,t





where µp
is the mean of pollutant p across all time points and locations
Montse Fuentes Multivariate Factor Model for Birth Defects
Factor updates: FFBS
The factors are updated through a Forward Filtering Backwards
Sampling (FFBS) algorithm (Carter & Kohn 1994,
Frühwirth-Schnatter 1994:
Forward Filtering : For t = 1, . . . , T, compute mt = at + At (Yt − ˜Yt ) and
Ct = Rt − At Qt At , where at = Γmt−1, At = Rt Λ Q−1
t ,
Qt = ΛRt Λ + Σ , Rt = ΓCt−1Γ + Σw , and ˜Yt = µ + Λat .
Then sample δT ∼ N(mT , CT ).
Backwards Sampling : For t = (T − 1), . . . , 0 sample δt ∼ N(˜at , ˜Ct ) where
˜at = mt + Bt (δt+1 − at+1), ˜Ct = Ct − Bt Rt+1Bt , and
Bt = Ct Γ R−1
t+1.
Montse Fuentes Multivariate Factor Model for Birth Defects
Pollutant Means
The pollutant data are from two observation networks, STN for
urban sites, and IMPROVE (IMP) for rural sites. We allow the
mean and error variances to differ based upon the pollutants sites
in the model by accounting for the two networks as follows,
µtp(s) =
¯µ0p if s is an IMPROVE site
¯µ0p + ¯µ1p if s is a STN site
and t,p(s) ∼ N[0, σ2
p(s)] where
σ2
tp =
σ2
STN,p
σ2
IMP,p.
Montse Fuentes Multivariate Factor Model for Birth Defects
Birth Defect Model
The California birth defect data has two binary responses denoted
˜Yi1 =
0 no cleft palate defect
1 cleft palate defect for individual i
˜Yi2 =
0 no cleft lip defect
1 cleft lip defect for individual i.
Montse Fuentes Multivariate Factor Model for Birth Defects
Defect Model
The probability of having a cleft defect we assume a set of latent
variables, Zi = (Zi1, Zi2) such that ˜Yij = I(Zij > 0) and
Zi = βT
xi +
M
m=1
L=8
=3
wT
mδi m + i
where
xi contains individual-level covariates such as maternal age
β is a matrix of regression coefficients specific to the birth
defect
wT
m represents the effect of exposure factor m during
gestation week
i ∼ N(0, Ω)
Montse Fuentes Multivariate Factor Model for Birth Defects
Weekly Coefficients on Pollutant Indices
Zi = βT
xi +
M
m=1
L=8
=3
wT
mδi m + i
The temporal covariates from the M factors are accounted for by
wT
m ∼ GP[0, R(φ)]
where the coefficients are allowed to change smoothly across
pregnancy weeks.
In this case, wT
m are the coefficients for each of the Zi clefts (cleft
lip and cleft palate) weekly measurements of pollutant index M
(factors)
Montse Fuentes Multivariate Factor Model for Birth Defects
Correlated cleft defects
Zi = βT
xi +
M
m=1
L=8
=3
wT
mδi m + i
The defects are correlated, to account for this we use an inverse
Wishart for the covariance structure in i ∼ N(0, Ω)
Ω ∼ IW (Σ, ν)
where Σ = I2 and ν = 2.
Montse Fuentes Multivariate Factor Model for Birth Defects
Model comparison
We compare M = 1, 2, and 3 factor models using the deviance
information criterion (DIC) (Spiegelhalter 2002)
Factors DIC
1 1624.06
2 1628.15
3 1629.98
In addition to DIC,the impact of the pollutants at the weekly level
are more clearly defined in the one-factor model.
Montse Fuentes Multivariate Factor Model for Birth Defects
Model comparison
Classification of defects:
Analyzed the predicted probabilities to assess the performance
of the one factor model.
Checked to see how well it classified defects.
Percent of defects correctly identified as defects,
P( ˜Y |Y = 1) = 0.92.
Montse Fuentes Multivariate Factor Model for Birth Defects
Impacts on Oral Cleft Risks
Figure: Covariate effects for the multivariate binary probit model. The posterior
means (dots) and 95% credible intervals (lines) for a change in cleft defects with a
one-standard deviation increase in maternal age, education, maternal smoking, and
maternal alcohol consumption in the California National Birth Defects Prevention
Study, 2003-2006.
Montse Fuentes Multivariate Factor Model for Birth Defects
Latent Factor Results
Figure: Weekly association of latent pollutants factors (w m) for the one-factor
model.
Montse Fuentes Multivariate Factor Model for Birth Defects
Pollutants
Figure: The standardized pollutants, Ammonium, Total Carbon Mass and
Sulfate. STN and IMPROVE monitoring sites with actual data values
shaded in the dots.
Montse Fuentes Multivariate Factor Model for Birth Defects
Pollutants
Figure: The standardized pollutants, Silicon, Iron, and Latent Factor
Values. STN and IMPROVE monitoring sites with actual data values
shaded in the dots.
Montse Fuentes Multivariate Factor Model for Birth Defects
Factor Loadings
Figure: California factor loadings. The Λp(s) for Ammonium, Nitrate,
Sulfate, The dots represent the STN and IMPROVE monitoring sites.
Montse Fuentes Multivariate Factor Model for Birth Defects
Factor Loadings
Figure: California factor loadings. The Λp(s) are Total Carbon Mass,
Calcium, Iron. The dots represent the STN and IMPROVE monitoring
sites.
Montse Fuentes Multivariate Factor Model for Birth Defects
Factor Loadings
Figure: California factor loadings. The Λp(s) are Potassium, Silicon, and
Sulfur. The dots represent the STN and IMPROVE monitoring sites.
Montse Fuentes Multivariate Factor Model for Birth Defects
Conclusions
Our multivariate spatiotemporal model
Accounts for the bias in the monitoring stations, STN and
IMPROVE
Incorporates factors that are both spatial and temporal
through Gaussian processes, unlike some previous work
Weekly averages speciated pollutants to identify the impacts
of pollutants and weeks when the fetus is more susceptible to
pollutants in the air which we note as weeks 3-8
Accounts for mothers’ mobility at the time of pregnancy
Montse Fuentes Multivariate Factor Model for Birth Defects
Health model conclusions
The health component shared information across two types of
cleft defects, lip and palate
Identify factors that increase the risks of cleft lip and cleft
palate defects, in particular mother’s that had diabetes.
Identified gestation weeks where the fetus is at the greatest
risk of birth defects based upon the latent factor of pollutants
that mother’s were exposed to at the time of gestation
Identify pollutants in the study region that weighted more
heavily than other pollutants
Montse Fuentes Multivariate Factor Model for Birth Defects
Acknowledgements
Montse Fuentes Multivariate Factor Model for Birth Defects
Thank you
Montse Fuentes Multivariate Factor Model for Birth Defects

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Program on Mathematical and Statistical Methods for Climate and the Earth System Opening Workshop, A Multivariate Dynamic Spatial Factor Model for Speciated Pollutants and Adverse Birth Outcomes - Montse Fuentes, Aug 23, 2017

  • 1. A Multivariate Dynamic Spatial Factor Model for Speciated Pollutants and Adverse Birth Outcomes Montse Fuentes Virginia Commonwealth University August 23, 2017 Joint with with Kimberly Kaufeld, Brian Reich, Amy Herring, Gary Shaw and Maria Terres Montse Fuentes Multivariate Factor Model for Birth Defects
  • 2. Why Birth Defects? Birth defects: a physical or biochemical abnormality that is present at birth and that may be inherited or the result of environmental influence. Around 3% of all births result in a birth defect. Orofacial defects are the most common. Cause of cleft palate defects is unknown Contributes to long-term disability, which may have significant impacts on individuals, families, health-care systems, and societies. Figure: Cleft lip and palate http://www.wetherallgroup.com/cleft-palate/ Montse Fuentes Multivariate Factor Model for Birth Defects
  • 3. Scientific Motivation Maternal exposure to air pollutants have been related to adverse birth outcomes Preterm birth Low birth weight Birth defects, i.e. cleft lip/palate Researchers believe that exposure to high concentrations of air pollution during pregnancy may significantly increase the risk of birth defects and other adverse birth outcomes. Montse Fuentes Multivariate Factor Model for Birth Defects
  • 4. Challenges: Estimating mother’s exposure to pollutants with sparse monitor locations Current regulations put limits on total PM2.5 concentrations, there are many speciated pollutants within this size class that likely have varying effects on perinatal health. Correlations between speciated pollutants it can be difficult to decipher their effects in a model for birth outcomes. Montse Fuentes Multivariate Factor Model for Birth Defects
  • 5. Background-Birth Defects and Pollution Orofacial cleft defects (cleft palate & or lip) appear in the first trimester, weeks 3-8. Orofacial cleft associations with air pollution Gilboa et al. (2005) found a weak association between PM10 and isolated cleft lip with or without cleft palate. Association of air pollution, CO and ozone, 03, exposure and oral clefts (Ritz 2002). Association between traffic density and cleft lip with or without palate (Padula et al 2013) Montse Fuentes Multivariate Factor Model for Birth Defects
  • 6. Pollutant exposure assessment Pollutant Data and Birth Defects Mothers pollutant exposure assigned nearest air pollution monitor (Ritz et al., 2002, Vrijheid et al., 2011). Generally, mother’s residence is based on the home at time of birth which doesn’t necessarily correspond to home during first trimester. Monitoring stations resulting in similar exposure over long areas equals a community-wide variation in air pollution. Montse Fuentes Multivariate Factor Model for Birth Defects
  • 7. Statistical Challenges Incorporate spatial analysis of environmental health data, typically not considered in classical birth defect epidemiological studies. Incorporate spatial prediction for pollution to provide measurements at the pregnant mothers’ homes to be used in a model for birth outcomes. Model multivariate birth defects to include multi-pollutant level data at the same time. Create statistical models to identify the specific critical windows and spatial locations during the pregnancy when high exposures to pollutants more negatively affect the birth defects. Characterize different sources of uncertainty in data and models. Montse Fuentes Multivariate Factor Model for Birth Defects
  • 8. California National Birth Defects Data Live births with and without any known birth defects where Woman’s date of conception is based upon the estimated date of delivery, the due date that the woman received from her physician reported at the study interview; 2003-2006 Cases included live births, and controls are live births without any known birth defects, identified randomly from selected hospitals in California Self reported survey where demographic and behavior information was reported There were a total of 208 cleft lip or cleft palate defects reported and 358 controls Montse Fuentes Multivariate Factor Model for Birth Defects
  • 9. Birth Defect Geocoded Data As part of the study women reported their complete residential history during pregnancy. Residences were geocoded each week during the first eight weeks of pregnancy to assign exposure levels, to account for mobility of the mothers during the study period Woman’s date of conception based upon the estimated date of delivery, due date that the woman received from her physician which was reported at the study interview Most of the data was collected in the San Joaquin Valley in California the initial study region Approximately 15% of the women moved during the study to areas outside of the initial study area, with the majority of the women moving to the San Francisco Bay and Los Angeles area. Montse Fuentes Multivariate Factor Model for Birth Defects
  • 10. Birth Defect Geocoded Data −124 −122 −120 −118 −116 −114 323436384042 Longitude Latitude Improve STN BD Residence Fresno CA Long Beach CA Los Angeles CA San Diego CA San Francisco CA San Jose CA Figure: Representative BD Residences and pollutant monitor locations Montse Fuentes Multivariate Factor Model for Birth Defects
  • 11. NBDPS data Covariates include: Sex of the infant Maternal age classifications 19 and under (baseline) 20-24 25-29 30-34 35 and older Prediabetes Maternal education (high school, some college and college) High blood pressure during pregnancy Smoking while pregnant (Yes/No) Alcohol use while pregnant (Yes/No) Montse Fuentes Multivariate Factor Model for Birth Defects
  • 12. Cleft Lip/Palate Data Montse Fuentes Multivariate Factor Model for Birth Defects
  • 13. Pollutant Sources Speciated Pollutants, PM2.5 Figure: PM 2.5 components, source: Guaita et al., 2011 Montse Fuentes Multivariate Factor Model for Birth Defects
  • 14. Pollution Data The Air Quality System (AQS) monitoring data Ambient air pollution data collected by EPA, state, local, and tribal air pollution control agencies in California Measurements collected every three to six days for Interagency Monitoring for Protected Visual Environments (IMPROVE) - rural sites STN sites - urban sites 40 monitors in CA where 20 are in the study region Montse Fuentes Multivariate Factor Model for Birth Defects
  • 15. Pollutant Data Sources California, 2003-2006 Ammonium- Weekly average (ug/m3 ) Nitrate (NO3)- Weekly average (ug/m3 ) Sulfate (SO4)- Weekly average (ug/m3 ) Total Carbon- Weekly average (ug/m3 ) Calcium (Ca) - Weekly average (ug/m3 ) Iron (Fe) - Weekly average (ug/m3 ) Potassium (K)- Weekly average (ug/m3 ) Silicon (Si)- Weekly average (ug/m3 ) Sulfur (Su)- Weekly average (ug/m3 ) Montse Fuentes Multivariate Factor Model for Birth Defects
  • 16. STN and IMPROVE Data Monitors Figure: Active Monitors, 2003-2006 Blue-IMPROVE, Black-STN Montse Fuentes Multivariate Factor Model for Birth Defects
  • 17. Weekly Pollutant Data Figure: STN and IMPROVE speciated components 2003-2006 weekly averages for each site where the vertical lines separate each year. 0 50 100 150 200 −4−2024 Week logAmmonium STN Improve 0 50 100 150 200 −4−2024 Week logNitrate 0 50 100 150 200 −4−20123 Week logSulfate 0 50 100 150 200 −4−2024 Week logTotalCarbMass 0 50 100 150 200 −4−3−2−10 Week logCalcium 0 50 100 150 200 −4−3−2−10 Week logIron 0 50 100 150 200 −4−2012 Week logPotassium 0 50 100 150 200 −4−201 Week logSilicon 0 50 100 150 200−4−201 Week logSulfur Montse Fuentes Multivariate Factor Model for Birth Defects
  • 18. Speciated Pollutant Correlations Table: Pearson correlation coefficients of weekly speciated pollutants from stations relevant to the study in the state of California, 2003-2006. Nitrate Sulfate Total Calcium Iron Potassium Silicon Sulfur Carbon Mass Sulfate 0.41 Total Carbon Mass 0.38 0.05 Calcium 0.03 0.08 0.20 Iron 0.19 0.11 0.48 0.77 Potassium 0.07 0.17 0.08 0.16 0.12 Silicon -0.03 0.01 0.05 0.85 0.78 0.13 Sulfur 0.41 0.97 0.03 0.10 0.12 0.20 0.04 Ammonium 0.96 0.60 0.34 0.05 0.19 0.06 -0.01 0.59 Montse Fuentes Multivariate Factor Model for Birth Defects
  • 19. Multivariate Spatial-Temporal Model Our model is a dynamic linear model with observation and evolution equations. Let Ytp(s) be the observation at location s on day t = 1, ..., T, for pollutant p = 1, ..., P, and Yt(s) = [Yt1(s), · · · , YtP(s)]T . Yt(s) = µt(s) + Λ(s)δt(s) + t(s) δt(s) = Γ(s)δt−1(s) + wt(s) where t(s) = [ t1(s), · · · , tP(s)]T are errors with tj (s) ∼ N(0, σ2) wt(s) = [wt1(s), · · · , wtM(s)]T denoted wtl ∼ GP[0, s2 w (φw )] Montse Fuentes Multivariate Factor Model for Birth Defects
  • 20. Factor model The factor loading matrix, Λ(s) is: The effect of factor f on pollutant p is determined by the (p, f ) element of Λ(s), denoted by λpf (s). To ensure identification we fix λpf (s) = 0 for f < p and λpf (s) > 0 for p = 1, ..., M. To induce spatial smoothness in the loadings log[λpp(s)] and λpf (s) for f > p are GP[0, s2 Λf ,p R(φΛf ,p )]. Montse Fuentes Multivariate Factor Model for Birth Defects
  • 21. Factor model The propagation matrix Γ(s) is: Diagonal with diagonal elements γ1(s), ..., γM(s) To ensure stationarity in time the factor evolution coefficients are restricted to the interval (−1, 1) Yt(s) = µt(s) + Λ(s)δt(s) + t(s) δt(s) = Γ(s)δt−1(s) + wt(s) γf ∼ TN(−1,1)[0N, s2 Γf R(φΓf )] λpf (s) ∼ GP[0, s2 Λf ,p R(φΛf ,p )] δf ,0 ∼ GP[0, s2 δf R(φδf )] Montse Fuentes Multivariate Factor Model for Birth Defects
  • 22. Spatial Dynamic Factor Analysis Model      Y 1 t Y 2 t ... Y P t      =      µ1 1N µ2 1N ... µP 1N      +      Λ1 1 Λ1 2 . . . Λ1 m 0 Λ2 2 . . . Λ2 m ... ... ... ... 0 0 . . . ΛP m           δ1,t δ2,t ... δm,t      +      1 t 2 t ... P t           δ1,t δ2,t ... δm,t      =      Γ1 0 . . . 0 0 Γ2 . . . 0 ... ... ... ... 0 0 . . . Γm           δ1,t−1 δ2,t−1 ... δm,t−1      +      w1,t w2,t ... wm,t      where µp is the mean of pollutant p across all time points and locations Montse Fuentes Multivariate Factor Model for Birth Defects
  • 23. Factor updates: FFBS The factors are updated through a Forward Filtering Backwards Sampling (FFBS) algorithm (Carter & Kohn 1994, Frühwirth-Schnatter 1994: Forward Filtering : For t = 1, . . . , T, compute mt = at + At (Yt − ˜Yt ) and Ct = Rt − At Qt At , where at = Γmt−1, At = Rt Λ Q−1 t , Qt = ΛRt Λ + Σ , Rt = ΓCt−1Γ + Σw , and ˜Yt = µ + Λat . Then sample δT ∼ N(mT , CT ). Backwards Sampling : For t = (T − 1), . . . , 0 sample δt ∼ N(˜at , ˜Ct ) where ˜at = mt + Bt (δt+1 − at+1), ˜Ct = Ct − Bt Rt+1Bt , and Bt = Ct Γ R−1 t+1. Montse Fuentes Multivariate Factor Model for Birth Defects
  • 24. Pollutant Means The pollutant data are from two observation networks, STN for urban sites, and IMPROVE (IMP) for rural sites. We allow the mean and error variances to differ based upon the pollutants sites in the model by accounting for the two networks as follows, µtp(s) = ¯µ0p if s is an IMPROVE site ¯µ0p + ¯µ1p if s is a STN site and t,p(s) ∼ N[0, σ2 p(s)] where σ2 tp = σ2 STN,p σ2 IMP,p. Montse Fuentes Multivariate Factor Model for Birth Defects
  • 25. Birth Defect Model The California birth defect data has two binary responses denoted ˜Yi1 = 0 no cleft palate defect 1 cleft palate defect for individual i ˜Yi2 = 0 no cleft lip defect 1 cleft lip defect for individual i. Montse Fuentes Multivariate Factor Model for Birth Defects
  • 26. Defect Model The probability of having a cleft defect we assume a set of latent variables, Zi = (Zi1, Zi2) such that ˜Yij = I(Zij > 0) and Zi = βT xi + M m=1 L=8 =3 wT mδi m + i where xi contains individual-level covariates such as maternal age β is a matrix of regression coefficients specific to the birth defect wT m represents the effect of exposure factor m during gestation week i ∼ N(0, Ω) Montse Fuentes Multivariate Factor Model for Birth Defects
  • 27. Weekly Coefficients on Pollutant Indices Zi = βT xi + M m=1 L=8 =3 wT mδi m + i The temporal covariates from the M factors are accounted for by wT m ∼ GP[0, R(φ)] where the coefficients are allowed to change smoothly across pregnancy weeks. In this case, wT m are the coefficients for each of the Zi clefts (cleft lip and cleft palate) weekly measurements of pollutant index M (factors) Montse Fuentes Multivariate Factor Model for Birth Defects
  • 28. Correlated cleft defects Zi = βT xi + M m=1 L=8 =3 wT mδi m + i The defects are correlated, to account for this we use an inverse Wishart for the covariance structure in i ∼ N(0, Ω) Ω ∼ IW (Σ, ν) where Σ = I2 and ν = 2. Montse Fuentes Multivariate Factor Model for Birth Defects
  • 29. Model comparison We compare M = 1, 2, and 3 factor models using the deviance information criterion (DIC) (Spiegelhalter 2002) Factors DIC 1 1624.06 2 1628.15 3 1629.98 In addition to DIC,the impact of the pollutants at the weekly level are more clearly defined in the one-factor model. Montse Fuentes Multivariate Factor Model for Birth Defects
  • 30. Model comparison Classification of defects: Analyzed the predicted probabilities to assess the performance of the one factor model. Checked to see how well it classified defects. Percent of defects correctly identified as defects, P( ˜Y |Y = 1) = 0.92. Montse Fuentes Multivariate Factor Model for Birth Defects
  • 31. Impacts on Oral Cleft Risks Figure: Covariate effects for the multivariate binary probit model. The posterior means (dots) and 95% credible intervals (lines) for a change in cleft defects with a one-standard deviation increase in maternal age, education, maternal smoking, and maternal alcohol consumption in the California National Birth Defects Prevention Study, 2003-2006. Montse Fuentes Multivariate Factor Model for Birth Defects
  • 32. Latent Factor Results Figure: Weekly association of latent pollutants factors (w m) for the one-factor model. Montse Fuentes Multivariate Factor Model for Birth Defects
  • 33. Pollutants Figure: The standardized pollutants, Ammonium, Total Carbon Mass and Sulfate. STN and IMPROVE monitoring sites with actual data values shaded in the dots. Montse Fuentes Multivariate Factor Model for Birth Defects
  • 34. Pollutants Figure: The standardized pollutants, Silicon, Iron, and Latent Factor Values. STN and IMPROVE monitoring sites with actual data values shaded in the dots. Montse Fuentes Multivariate Factor Model for Birth Defects
  • 35. Factor Loadings Figure: California factor loadings. The Λp(s) for Ammonium, Nitrate, Sulfate, The dots represent the STN and IMPROVE monitoring sites. Montse Fuentes Multivariate Factor Model for Birth Defects
  • 36. Factor Loadings Figure: California factor loadings. The Λp(s) are Total Carbon Mass, Calcium, Iron. The dots represent the STN and IMPROVE monitoring sites. Montse Fuentes Multivariate Factor Model for Birth Defects
  • 37. Factor Loadings Figure: California factor loadings. The Λp(s) are Potassium, Silicon, and Sulfur. The dots represent the STN and IMPROVE monitoring sites. Montse Fuentes Multivariate Factor Model for Birth Defects
  • 38. Conclusions Our multivariate spatiotemporal model Accounts for the bias in the monitoring stations, STN and IMPROVE Incorporates factors that are both spatial and temporal through Gaussian processes, unlike some previous work Weekly averages speciated pollutants to identify the impacts of pollutants and weeks when the fetus is more susceptible to pollutants in the air which we note as weeks 3-8 Accounts for mothers’ mobility at the time of pregnancy Montse Fuentes Multivariate Factor Model for Birth Defects
  • 39. Health model conclusions The health component shared information across two types of cleft defects, lip and palate Identify factors that increase the risks of cleft lip and cleft palate defects, in particular mother’s that had diabetes. Identified gestation weeks where the fetus is at the greatest risk of birth defects based upon the latent factor of pollutants that mother’s were exposed to at the time of gestation Identify pollutants in the study region that weighted more heavily than other pollutants Montse Fuentes Multivariate Factor Model for Birth Defects
  • 40. Acknowledgements Montse Fuentes Multivariate Factor Model for Birth Defects
  • 41. Thank you Montse Fuentes Multivariate Factor Model for Birth Defects