1. Introduction
The introduction of chemicals, physical agents, and biological toxins to the environment, whether from accidental discharge, intentional release, or natural processes, can cause adverse changes in the environment. Identifying pollution sources, the causes, and links between changes in environmental conditions and adverse health effects will help prevent risk of harm to human health and the environment. Environmental health tracking (also called environmental health surveillance) is currently used by various organizations to better understand the impacts on human health from changes in environmental conditions and identify the most effective prioritising efforts and interventions. Some examples of international environmental health tracking systems are the World Health Organization (WHO) Europe Region Environmental Health Information System [
1], United States Centers for Disease Control and Prevention Environmental Public Health Tracking Network [
2], and Environmental Health Indicators New Zealand [
3].
Environment Protection Authority (EPA) Victoria in Australia is the state’s environmental regulator, responsible for protecting the environment from pollution and waste in the state of Victoria. In March 2016, the Victorian Ministerial Advisory Committee (MAC) released a report on an independent inquiry into EPA Victoria [
4]. One recommendation from the MAC report was the delivery of environmental health functions relevant to pollution and waste within the EPA. To strengthen its environmental health capability and better understand how environmental pollution from natural and man-made sources can affect public health, EPA Victoria is developing an environmental health tracking system. As defined by Thacker et al., environmental public health surveillance is “the ongoing collection, integration, analysis, and dissemination of data from environmental hazards monitoring, human exposure tracking, and health effect surveillance” [
5]. The Environmental Health Tracking System (EHTS) will be used to provide timely and scientific information for EPA and other decision makers in Victoria for implementing and evaluating policies to effectively manage environmental and health-related issues in Victoria. It will allow for a better understanding of the possible associations between environmental exposures and health outcomes. This will then guide interventions aimed at improving public health for Victorians.
Objectives for using an environmental health tracking system in Victoria are:
- (1)
To proactively investigate the short- and long-term temporal and spatial trends of environmental conditions and adverse health effects to help guide interventions and prevent harm to human health resulting from environmental pollution or waste.
- (2)
To have access to short- and long-term trends to respond to community concerns related to environmental public health issues.
- (3)
To make relevant environmental public health tracking data available to stakeholders (e.g., public, government departments, and researchers) on a spatial and temporal scale in an easy to understand format.
- (4)
To respond to emerging environmental health threats, clusters, and outbreaks by identifying populations at risk for adverse health effects.
- (5)
To investigate relationships between environmental contamination and health effects for specific cases.
- (6)
To develop routine tracking of adverse health effects on a small scale and identify areas warranting further investigation.
- (7)
To increase partnerships and collaborations between traditional environmental and health entities at federal, state, and local government levels by developing networks.
The successful implementation of an EHTS in Victoria will involve:
Investigating the feasibility of implementing EHTS in Victoria;
Developing a conceptual framework for the EHTS;
Developing and identifying environmental health indicators for the EHTS;
Developing a technical implementation plan for the system architecture of the EHTS;
Implementing the EHTS with available data; and
Evaluation of the effectiveness of the EHTS;
The outcome of the feasibility study indicated that an EHTS was feasible in Victoria, and this paper focused on step 2. The aim of this paper is to develop a conceptual framework for EPA Victoria’s EHTS. The proposed conceptual framework will support successful implementation of the EHTS in Victoria.
2. Strategy for Developing Environment Protection Authority (EPA)’s Environmental Health Tracking Conceptual Framework
In developing a conceptual framework for EPA’s environmental health tracking, a literature review and in-depth discussions with a wide range of experts via focused workshops were carried out. The expert workshops were organized by EPA Victoria’s Environmental Public Health Unit and attended by staff from Victoria’s Department of Health and Human Services (DHHS), EPA, and the Department of Environment, Land, Water, and Planning (DELWP). The workshops were useful in:
formulating objectives for EPA Victoria’s environmental health tracking and providing ideas for its conceptual framework design process;
reviewing available data sources for the EHTS;
identifying a suitable conceptual framework for EPA Victoria’s EHTS; and
conducting a preliminary case study within the context of the conceptual framework.
3. Available Conceptual Frameworks for Environmental Health Tracking
A conceptual framework for environmental health tracking provides an organized approach that helps visualize, collate, and analyze issues related to actual or predicted environmental health relationships [
6,
7]. In addition, conceptual frameworks can connect individual monitoring programs and support development of new indicators, policies, and programmes [
8].
A literature search was conducted on conceptual frameworks for environment and health reporting globally, and several studies were identified that conducted a review on conceptual frameworks used for reporting environmental and health issues [
6,
7,
9,
10,
11,
12]. Thacker et al. [
5] conceptual framework, Driving Force-Pressure-State Exposure-Effect-Action (DPSEEA) [
13], Driving Force-Pressure-State-Impact-Response (DPSIR) [
14], and Pressure-State-Response (PSR) [
15] were the most common conceptual frameworks used in reporting environmental and health issues, and these were assessed for potential suitability in Victoria.
4. Choosing a Conceptual Framework
A conceptual framework is required to accurately and precisely identify relationships between sources that influence change in the environment, and health impacts that can be linked to these causes support effective intervention. It is essential to understand the components of conceptual frameworks to determine which one would be most suitable for EPA Victoria EHTS. The components of the four conceptual frameworks are listed in
Table 1.
In addition to understanding the components of the four conceptual frameworks, it is essential that a proposed conceptual framework enables the purposes and objectives of the environmental health tracking network to be achieved. A list of criteria for selecting a suitable conceptual framework for reporting environmental health issues is shown in
Table 2.
5. Availability of Data
The decision of including data into the tracking network will need to be based on relevance of the data, data quality, and compatibility of available data. Also, it would involve exploring how new and existing environmental, exposure, and adverse health effects data will be used [
16] in the EHTS. EPA has identified potential collaborative stakeholders, such as DHHS Victoria, DELWP Victoria, Bureau of Meteorology (BOM) Australia, Australian Bureau of Statistics (ABS), Commonwealth Scientific and Industrial Research Organisation (CSIRO), and other state government agencies as well as universities that can provide relevant data for the EHTS. The type of relevant data held by these organisations could include environmental data such as environmental monitoring and modeling of air and water quality, land use data, and health data from hospital emergency departments and ambulance services. However, exposure data (such as direct measurements of individual exposure from personal sampling) are not currently available for ongoing tracking. Linking environmental exposure and health effects back to their determining factors is important for the EHTS; however, the unavailability of exposure data at this point in time was taken into account when designing the conceptual framework.
6. Proposed Conceptual Framework for EPA’s Environmental Health Tracking
An important consideration for EPA’s conceptual framework is that it needs to be able to link changes in environmental conditions and health impacts to its determining factors so that effective action can be taken to reduce or eliminate risks of adverse health effects through interventions (
Table 1). Based on the information provided in the studies that were reviewed related to conceptual frameworks for environment and health reporting, DPSEEA and Thacker et al. [
5] methods were the two conceptual frameworks that could link environmental exposure to health effects. However, as shown in
Table 1, conceptual framework of Thacker et al. [
5] did not have an action component, meaning there were no intervention points along hazard, exposure, and health surveillance components or actions to minimize or mitigate risk of adverse health effects. On the other hand, the DPSEEA conceptual framework could link adverse human health effects with environmental exposure to action, making it possible for interventions to target either environmental exposure and adverse health effects, or both, as well as their determinants throughout the cause-effect chain (
Table 2) [
17]. Another important aspect of the DPSEEA conceptual framework was that it was flexible and could be modified depending on environmental health surveillance requirements [
7,
11,
17]. This is important, as EPA’s environmental health tracking requirements are expected to change over time.
Although it was noteworthy that DPSIR had an impact component, exposure was not a listed component, and it was not considered in the association between state (changes in environmental condition) and impact (effects on human health). Also, DPSIR was criticized for providing a static representation of the environment and ignoring significant interactions between components [
7,
11,
12]. This was a limitation, as the DPSIR conceptual framework could not be used to investigate relationships between environmental exposure to contaminants and possible health effects for specific cases.
In conclusion, the DPSEEA conceptual framework was the most suitable for EPA, as it had all the required components and criteria for environmental health tracking in Victoria (
Table 1 and
Table 2). Therefore, the DPSEEA conceptual framework was selected and modified to meet EPA’s environmental health tracking objectives by removing exposure and effect (
Figure 1).
7. EPA Victoria’s Drivers-Pressure-Environmental Condition-Health Impact-Action (DPEHA) Conceptual Framework
The DPSEEA was modified to “Drivers–Pressure–Environmental Condition–Health Impact–Action” (DPEHA) because of the unavailability of exposure data from personal monitoring or biomonitoring. However, DPEHA can use proxy indicators (for exposure), such as ground-level concentrations of pollution, combined with population information such as population density. The EHTS will continue to improve and change over time by adding new data, and in the future, when exposure data may become available, DPEHA can be modified to include an exposure component that is consistent with DPSEEA. Some of the benefits of developing DPEHA are to organize indicators in a causal chain, support the development of environmental health indicators, and help develop the technical architectural framework for the EHTS. As defined by Briggs et al. [
18] “
environmental health indicator is an expression of links between environment and health, targeted at a specific policy issue or management concern and presented in a form which facilitates interpretation for effective decision-making”.
As shown in
Figure 1, environmental condition and health impact are important components of the environmental health conceptual framework when describing the cause and effect relationships between environment and health in Victoria. The DPEHA conceptual framework provides an organized approach to describe ways in which drivers through human activities exert pressures on the environment. As a result, the pressure changes the environmental conditions, which in turn produces acute and chronic adverse health impacts through various exposure pathways for individuals, groups, and communities.
Figure 1 also shows how actions, such as environmental and economic policies, can control and manage efforts that would lead to prevention of harmful environmental conditions that could adversely impact human health. The arrows that start at action and link to the other components, such as health impacts and pressure on the environment, indicate the influence of action along the cause–effect chain; the thicker the arrow, the stronger the influence of the action on the component. The rationale for having a stronger action (thicker arrow) on environmental condition and health impact components is that actions will ultimately affect the drivers as well as immediate pressures on the environment through economic and environmental policies and programs developed by decision makers in Victoria. Policies that reduce or mitigate environmental exposure may result in improved environmental condition by effectively managing and controlling the release of contaminants to the environment or by limiting the interaction of people with certain areas and, therefore, avoiding being exposed. The benefit of the DPEHA is that associations between change in environmental conditions and health outcomes can still be made without an exposure component. Also, useful additions to the DPEHA conceptual framework are moderators for linking drivers to change in environmental conditions and subsequent health impacts. These moderators are “qualitative or quantitative factors such as gender, ethnicity, age, marital status, educational level, housing, income and poverty status, that specifies when or to whom something may happen” [
19]. The moderators will aid in providing information on diversity within a population. Also, the addition of moderators accounts for population vulnerability, which is useful in generating knowledge on spatial and temporal patterns of health, acute and chronic adverse health effects, as well as socioeconomic and demographic factors.
The DPEHA conceptual framework (
Figure 1) was tested by using it to examine some potential scenarios as discussed in the next section.
8. Potential Application of the Environmental Health Tracking System
Two case studies of environmental health issues were selected in applying the DPEHA conceptual framework for visualizing and evaluating environmental health links in the EHTS to:
provide scientific evidence for EPA Victoria for improved public health and the environment in the state;
provide information for Victorians in making informed decisions on things affecting their health; and
respond in a timely and effective way to community concerns on environmental health-related issues.
Scenario 1: understanding the spatial distribution of the health burden of noise from road traffic.
This project was an opportunity to demonstrate the concept of Victorian environmental health tracking in investigating the health burden of noise from road traffic in Melbourne using available data from noise mapping studies [
20,
21] and the ABS Census [
22].
Figure 2 depicts the preliminary results from the project, with maps showing noise levels modeled at a 10 m × 10 m grid, averaged noise level per mesh block (geographical area for which data were provided by the Australian Bureau of Statistics—generally consisting of between 30 and 60 residences), and the expected rate of ischemic heart disease deaths attributable to the estimated potential exposure levels in each small area population subgroup. This mapping tool will be useful for EPA and other stakeholders in evaluating the burden of disease from road traffic noise to provide scientific evidence that guides public health decision makers in Victoria. The mapping application tool will be available on request. It will ultimately be accessed via the internet as a risk assessment tool for epidemiologists and risk assessors to support public health. This will help to identify areas and/or populations that may be impacted by noise from road traffic.
Scenario 2: Public health investigations of anthropogenic PM2.5 and exacerbation of respiratory-related illnesses
This scenario was a hypothetical example of how the DPEHA conceptual framework could be applied in estimating the burden of respiratory illnesses associated with anthropogenic PM
2.5 (as shown in
Figure 3). Common anthropogenic PM
2.5 sources included emissions from road vehicles, planned burns, and wood heaters for heating. This scenario made use of the data in
Table 3.
As shown in
Figure 3, the DPEHA not only provided a platform for collecting and integrating environment and health data, and data from other sources, into the EHTS, it could also be useful to better understand the links between environmental health problems and their causes through analysis and interpretation of the data. Outcomes from analysis of the data will provide scientific information for decision makers to drive policies such as measures to mitigate or minimize emissions of PM
2.5 associated with road traffic and public awareness. The possible action(s) will result in improved public health across Victoria.
9. Conclusions
The DPEHA conceptual framework has been developed for EPA’s environmental health tracking system from DPSEEA’s conceptual framework. DPEHA’s conceptual framework provides essential features that could link changes in the environment and associated adverse health effects, which allows for effective interventions that align with the purpose of this tracking. DPEHA also provides an organized approach that supports the visualization, collation, and analysis of environmental and health relationships in tracking. This environmental health tracking system will be used to investigate and track (temporally and spatially) major environmental public health issues in Victoria as demonstrated in the case studies here. It will also allow an evidence-based approach to develop effective interventions to mitigate and prevent associated health risks.
Author Contributions
Conceptualization, B.E., C.I., M.D.; methodology, B.E., C.I., I.H., J.I., M.D.; software, I.H.; formal analysis, I.H., M.D.; investigation, B.E., M.D.; data curation, I.H., M.D.; writing—original draft preparation, B.E.; writing—review and editing, C.I., I.H., B.G., P.C., N.A.-B., J.I., M.D.; visualization, C.I., I.H.; supervision, M.D.; project administration, B.E.
Funding
This research received no external funding.
Acknowledgments
We are grateful to Catherine Healy, Science Communications Adviser, EPA Victoria for her comments on this manuscript.
Conflicts of Interest
The authors declare no conflict of interest.
References
- World Health Organisation (WHO). Regional Office for Europe, European Centre for Environment and Health. Development of Environment and Health Indicators for the European Union Countries (ECOEHIS). Final Report. 2004. Available online: https://apps.who.int/iris/bitstream/handle/10665/107620/E85061.pdf?sequence=1 (accessed on 25 April 2019).
- Centres for Disease Control and Prevention. Guide to Building and Environmental Public Health Tracking Network. 2011. Available online: https://www.cdc.gov/nceh/tracking/pdfs/how_to_guide.pdf (accessed on 24 September 2018).
- Ministry of Health. Environmental Health Indicators for New Zealand 2008; Ministry of Health: Wellington, New Zealand, 2009. Available online: https://www.health.govt.nz/system/files/documents/publications/environmental-health-nz-08.pdf (accessed on 24 September 2018).
- Victoria State Government of Australia. Melbourne (AUST): Ministerial Advisory Committee, Victoria Government; Independent Inquiry into the Environment Protection Authority Victoria. 31 March 2016. Available online: http://epainquiry.vic.gov.au/__data/assets/file/0008/336698/Inquiry-report-EPA_June.pdf (accessed on 4 June 2018).
- Thacker, S.B.; Troup, D.F.; Parrish, R.G.; Anderson, H.A. Surveillance in environmental public health: Issues, systems, and sources. Am. J. Public Health 1996, 86, 633–641. [Google Scholar] [CrossRef] [PubMed]
- Waheed, B.; Khan, F.; Veitch, B. Linkage-Based Frameworks for Sustainability Assessment: Making a Case for Driving Force-Pressure-State-Exposure-Effect-Action (DPSEEA) Frameworks. Sustainability 2009, 1, 441–463. [Google Scholar] [CrossRef] [Green Version]
- Hambling, T.; Weinstein, P.; Slaney, D.A. Review of Frameworks for Developing Environmental Health Indicators for Climate Change and Health. Int. J. Environ. Res. Public Health 2011, 8, 2854–2875. [Google Scholar] [CrossRef] [PubMed]
- Dumanski, J.; Pieri, C. Application of the pressure-state-response framework for the land quality indicators (LQI) programme. In Land Quality Indicators and Their Use in Sustainable Agriculture and Rural Development, Proceedings of the Workshop, Rome, Italy, 25–26 January 1996; Land and Water Development Division, FAO Agriculture Department and the Research, Extension and Training Division, FAO Sustainable Development Department: Rome, Italy, 1997. [Google Scholar]
- von Schirnding, Y.E. Health-and-environment indicators in the context of sustainable development. Can. J. Public Health 2002, 93, 9–15. [Google Scholar]
- World Health Organisation. Framework for Linkages between Health, Environment and Development. Available online: http://www.who.int/mediacentre/events/IndicatorsChapter7.pdf (accessed on 14 October 2018).
- Liu, H.Y.; Bartonova, A.; Pascal, M.; Smolders, R.; Skjetne, E.; Dusinska, M. Approaches to integrated monitoring for environment and health impact assessment. Environ. Health 2012, 11, 88. [Google Scholar] [CrossRef] [PubMed]
- Lam, S.; Leffley, A.; Cole, D.C. Applying an Ecohealth perspective in a state of the environment report: Experiences of a local public health unit in Canada. Int. J. Environ. Res. Public Health 2014, 12, 16–31. [Google Scholar] [CrossRef] [PubMed]
- Corvalán, C.; Nurminen, M.; Pastides, H.; World Health Organization; Office of Global and Integrated Environmental Health. Linkage Methods for Environment and Health Analysis: Technical Guidelines: A Report of the Health and Environment Analysis for Decision-Making; World Health Organization: Geneva, Switzerland, 1997; Available online: http://www.who.int/iris/handle/10665/63490 (accessed on 11 November 2018).
- European Environment Agency. EEA Core Set of Indicators–Guide. EEA Technical Report 2005. Available online: File: https://www.eea.europa.eu/publications/technical_report_2005_1 (accessed on 11 August 2018).
- Organisation for Economic Co-operation and Development. OECD core set of indicators for environmental performance reviews: A synthesis report by the Group on the State of the Environment. Environ. Monogr. 1993, 83, 1–39. [Google Scholar]
- McGeehin, M.A.; Qualters, J.R.; Niskar, A.S. National Environmental Public Health Tracking Program: Bridging the Information Gap. Environ. Health Perspect. 2004, 112, 1409–1413. [Google Scholar] [CrossRef] [PubMed] [Green Version]
- Gentry, S.J.; Bartram, J. Human health and the water environment: Using the DPSEEA framework to identify the driving forces of disease. Sci. Total Environ. 2013, 468–469, 306–314. [Google Scholar]
- Briggs, D.; Corvalan, C.; Nurminen, M. Linkage Methods for Environment and Health Analysis; UNEP/US EPA/WHO: Geneva, Switzerland, 1996. [Google Scholar]
- Sandifer, P.A.; Knapp, L.C.; Collier, T.K.; Jones, A.L.; Juster, R.P.; Kelble, C.R.; Sutton-Grier, A.E. A conceptual model to assess stress-associated health effects of multiple ecosystem services degraded by disaster events in the Gulf of Mexico and elsewhere. GeoHealth 2017, 1, 17–36. [Google Scholar] [CrossRef] [PubMed]
- Hinze, B. Estimation of Environmental Noise Exposure–Greater Melbourne; WSP Acoustics, Parsons Brinckerhoff: Melbourne, Victoria, Australia, 2013. [Google Scholar]
- Australian Institute of Health and Welfare (AIHW). Mortality Over Regions and Time (MORT) Books Local Government Area (LGA), 2011–2015 Table 2: Leading Causes of Death by Sex, 2011–2015; Australian Institute of Health and Welfare (AIHW): Canberra, Australia, 2015.
- Australian Bureau of Statistics (ABS). Census Data. Available online: http://www.abs.gov.au/ (accessed on 30 November 2018).
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