Edward J. Trapido, Sc.D., F.A.C.E. Associate Dean for Research

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Longer Term Public Health Implications of Disasters: The Deepwater Horizon Oil Spill Edward J. Trapido, Sc.D., F.A.C.E. Associate Dean for Research LSUHSC School of Public Health Professor and Wendell Gauthier Chair for Cancer Epidemiology Coordinator of Gulf Oil Spill Research, LSU Health Sciences Center at New Orleans Photo: 6/26/10

DWH KATRINA Natural or (Hu)Man-Made Disasters EAST BR ANDREW

Disasters & Public Health Lead to increased death, illness, and disability Large economic impacts Large social impacts Impact invariably unequal across populations

Number of deaths per income group (1994-2013), and Number Per million inhabitants Very old, very young and very sick are most vulnerable

Public Health Needs The main relief needs in natural disasters are clean water, food, sanitation, and shelter In acute disasters, such as earthquakes and cyclones, physical trauma may require specialized interventions The probability of survival from serious injury decreases substantially 12 to 24 hours after the disaster strikes, and good outcomes in most cases are thus highly dependent on the rapidity of appropriate medical and surgical responses http://www.nejm.org/doi/full/10.1056/NEJMra1109877

Case Example: 9/11 Attack

Identifying Persons Health/Disease Related Services Rarely a surveillance system Development of protocol for identification of illnesses and disease follow-up (harder to do when infrastructure destroyed) Few trained to assess mental and physical health effects of complex exposures Some verifiable, others not Who pays for treatment

Exposure Not a Single Point in Time Spill began 4/20/2010 and was capped 9/21/2010 Active clean-up ended 4/16/2014 Litigation continues Most of population had been through Katrina, Rita, Gustavo, so it was already stressed Every tropical storm, hurricane, oil spill, news story, movie, anniversary, ad for litigation, etc. may rekindle feelings and thoughts

Determining Exposure General populations, first responders, clean-up workers, medical personnel, patients, occupational groups Children, pregnant and non-pregnant women, men, elderly, immunocompromised or handicapped individuals, etc.

Exposures from Oil Spills Direct Exposure Crude oil contains toxic components to humans Aromatic/aliphatic hydrocarbons Hydrogen sulfide gas Sulfonic acid Exposures could result in respiratory and dermal irritations, central nervous system depression, etc. Indirect Exposure Social and economic disruption May lead to mental and physical health consequences Physical problems may lead to mental health consequences Specific to the DHOS, residents rely on the fishing and tourism industries for their livelihood, which were severely affected by the DHOS

Health Effects Immediate Physical Effects Immediate Mental Effects Death, injuries Some depend upon routes of exposure: burns, respiratory, GI, ocular, nausea, dizziness, work related Immediate Mental Effects shock, grief, fear, disorientation, anger, behavioral, psychological manifestations of physical disease and vice versa

Health Effects Midterm effects: Long term effects: Genotoxic effects modified by changes in diet, displaced populations, changes in behaviors (e.g., tobacco use); above plus pregnancies, birth outcomes, depression, anxiety Long term effects: rare diseases, like cancer, are hard to measure and attribute Genotoxic effects

Edward Trapido, ScD, FACE Principle Investigator, WATCH Study Louisiana State University School of Public Health

WaTCH Aims: Women To estimate the association between oil spill “exposure” and physical and emotional health outcomes including respiratory disease, rashes, headaches, depression and emotional distress. Children To understand the impacts of the Deepwater Horizon oil spill on children's development and well-being, and to examine how parental and social forces changes the spill's effects on children. Ongoing, prospective cohort study examining the short and long-term physical, mental, and community health effects resulting from the Deepwater Horizon Oil Spill among adult women and children residing in Southeastern Louisiana

Methods Cohort of women from 7 Southeastern LA parishes Sample of ~2800 women and ~600 children Address based sampling frame of household telephone numbers Inclusion criteria: 18-80 years (women); 10-17 years (children) Lived in one of seven target parishes on April 20, 2010 Acadia Allen Ascension Assumption Avoyelles Beauregard Bienville Bossier Caddo Calcasieu Caldwell Cameron Catahoula Claiborne Concordia DeSoto E. Baton Rouge Evangeline Franklin Grant Iberia Iberville Jackson Jefferson Davis Lafayette Lafourche La Salle Lincoln Livingston Madison Morehouse Natchitoches Orleans Ouachita Plaquemines Rapides Red River Richland Sabine St. Bernard St. Charles Helena James John St. Landry St. Martin St. Mary St. Tammany Tangipahoa Tensas Terrebonne Union Vermilion Vernon Washington Webster WBR West Carroll Feliciana Winn Pointe Coupee East Women were identified through: Address-based sampling Referrals of friends and neighbors Volunteers Data collection Computer-assisted telephone survey Home visit Biospecimens and anthropometric measureme

Participation Wave I: July 2012 - August 2014 2,852 women The questionnaire included detailed questions on demographic characteristics, physical and mental health history, exposure to the oil spill or its clean-up, medication use, lifestyle characteristics such as diet, smoking, alcohol consumption, physical activity, occupational history, and exposure to prior hurricanes and other exposure information. There were also questions regarding healthcare access, social support, social capital, resource loss, financial or economic hardship and other measures of resiliency. Wave II: September 2014-June 2016 2038 women Follow-up questions reassessed information collected during the baseline phone interview, including demographics, physical and mental health, behaviors and other exposures. New modules were added including questions to assess the following personal characteristics: conservation and loss of resources, resiliency, social capital, perceived stress, life events and post-traumatic stress. 43.3% response rate = calculated by dividing the number of complete interviews by the number of eligible women using an estimate of the proportion of unknown eligibility cases that are eligible AAPOR – American Association for Public Opinion Research

Exposure Assessment N (%) Characteristic Economic Exposure DHOS Lost HH income due to employment disruption/closing of business because of oil spill 662 (26.6) Hit harder by oil spill compared to others in community 167 (6.0) Oil spill had somewhat or very negative influence on HH financial situation 1064 (37.84) Physical/Environmental Exposure to DHOS Oil spill caused damage to areas fished commercially 195 (6.8) Extent and frequency of smelling oil No smell 1694 (62.4) Low smell 293 (10.78) Medium smell 472 (17.4) High smell 258 (9.4) Came into physical contact with oil in other ways 624 (22.10) Oil spill directly affected recreational hunting/fishing/other activities of household 452 (15.9) Work on any of the oil spill cleanup activities? 47 (2.0) Property that was lost or damaged because of the oil spill or cleanup? 58 (2.4) Nine Binary Indicators

Physical Effects Wave I

Physical Effects Wave II (unpublished data)

Mental Health   Wave 1 Wave 2 Characteristic Mean SD Depressive Symptoms 11.9 12.52 14.5 13.5 *** Presence of depressive symptoms (CESD >= 16) (n, %) 572 28% 722 36% No depressive symptoms (CESD < 16) (n, %) 1459 72% 1310 65% Mental Distress 6.2 5.28 5.9 5.38 Severe mental distress (K6 >= 13) (n, %) 262 13% 268 Moderate mental distress (K6 = 8-12) (n, %) 406 20% 321 16% No mental distress (K6 < 8) (n, %) 1359 67% 1446 7% *p<0.05, **p<0.001, ***p<0.0001 from Wilcoxon-signed rank tests between Waves 1 and 2 Missing data: Depressive symptoms (W1 n=7, W2 n=6); mental distress (W1 n=11, W2 n=3) Note: Depressive symptoms measured with the Centers for Epidemiological Studies-Depression (CESD) scale; mental distress measured with the K6 scale. scores calculated as sum of affirmative responses PTSD, measured by the PCL, was also associated with exposure. https://www.mirecc.va.gov/docs/visn6/3_PTSD_CheckList_and_Scoring.pdf

Behavioral Health Increase in tobacco use, alcohol use, intensity of family fights Recidivism of these behaviors Clear implications for actions/services

Resiliency “the capacity of a system to withstand or recover from significant disturbances that threaten it” Resilience has been an often-discussed concept in the disaster field. We view it as a process rather than an outcome, and define it as the capacity of a system to withstand or recover from significant disturbances that threaten it. Recently, there have been many calls for more research on resilience that can be applied to post-disaster settings. Specifically, we are interested in how mental health in a post-disaster setting is shaped by resilience Social ties How people socialize, live, interact, relate to each other Evidence linking this with health Resilience Capacity of a system to recover from significant disturbances Process rather than outcome

Resiliency Attributes Individual and community attributes. Individual resilience General Self-Efficacy, 10 item questionnaire Social support, 6 item questionnaire Community resilience Social cohesion Informal social control Neighborhood organization participation Resilience activation whether any of 8 services were needed in the year following the oil spill. e.g. food, utilities, etc. Needed and did not receive the service, did not need the service, and needed and received the service.

SEM Model Results - - + + Community resilience attributes Resilience activation: receipt of needed services -.060 Individual resilience attributes + .250 -.505 - -.166 Total direct: 0.188 (.049), p<.001 Total indirect: .084 (.016), p<.001 Total: .272 (.047), p<.001 1. The first thing we see is that exposure to the oil spill is positively associated w/depression (more exposure, more depression). 2. We also see that both individual and community resilience attributes were significantly associated with resilience activation. Individual resilience attributes were positively associated with resilience activation, which was expected, meaning that things like more self efficacy and more social support were related to more receipt of needed services. But community resilience was negatively associated with receipt of needed services, which was not expected. In other words, the more social cohesion and informal social control, the LESS activation occurred. This was unexpected and we will want to take a closer look at it. It is possible that exposure negatively affected community resilience attributes, which then negatively affected resilience activation. 3. We also see that exposure is negatively associated with resilience activation. (more exposure, less activation or receipt of needed services) 4. And that resilience activation negatively associated with depression. (more activation or more receipt of needed services, less depression) (these were in expected direction) 5. Moreover, this indirect pathway from exposure to activation to depression was also significant, meaning that resilience activation/receipt of needed services partially mediates the relationship between exposure and depression. 31% of the total effect of exposure to the spill on depression was explained by the mediating factor of resilience activation. Exposure to oil spill + .188 Depression

Resiliency Results Resilience attributes, particularly individual ones such as general self-efficacy and social support, are predictive of resilience activation (receipt of needed services). Resilience activation mediates the relationship between exposure to the oil spill and increased depression. Relationship between exposure to the spill and increased depression is partially explained by the ability of participants to activate their resilience attributes, or to receive specific services that they needed.

Economic Effects Clean-up and containment costs Lost jobs Mitigation claims Damage claims Civil penalties Criminal penalties Loss of productivity Loss of tourism Lost jobs Health effects require money for diagnosis, treatment, rehabilitation Resettlement costs Rebuilding costs

Need for Health Policy Formation Overarching policy focus: Are harms mitigated? Are services available? How are services financed? Timing Initial emergency Acute phase Longer-term, chronic phase

Longer-Term, Chronic Phase (More than 5 years post-event) Emphasis on Ongoing needs of those still affected Who is still sick Why are they still sick What needs are still not being met and why Less interest by Federal Agencies

9/11 Policy Making: Lessons Learned Interplay between policymaking and scientific processes can be challenging and mistrustful Developing mechanisms to interpret and communicate scientific finding to policymakers and the public may reduce mistrust Synthesize emerging findings into non-scientific reports (maintaining rigor) Develop mechanisms to help policymakers and media access body of evidence to date

Lessons Learned Disasters often expose or exacerbate larger structural inequities and challenges in communities Healthcare system inequities, inefficiencies, and expense; Disability adjudication problems Longstanding physical and mental health disparities Solutions for populations at risk for unmet health needs are a policy priority in most disasters Screen and refer directly affected groups for mental health symptoms Need for trained providers Dedicated outreach efforts to unaffiliated or marginalized groups Clean up and lower-skilled construction workers Lower SES affected communities

A team effort: Edward Trapido (me) Ariane Rung Daniel Harrington Evrim Oral Samaah Sullivan Symielle Gaston Daesy Behrhorst Lorna Thorpe, for WTC material NIEHS

Thank you. etrapi@lsuhsc.edu