<!DOCTYPE article PUBLIC "-//NLM//DTD JATS (Z39.96) Journal Archiving and Interchange DTD v1.0 20120330//EN" "JATS-archivearticle1.dtd">
<article xmlns:xlink="http://www.w3.org/1999/xlink">
  <front>
    <journal-meta />
    <article-meta>
      <contrib-group>
        <contrib contrib-type="author">
          <string-name>Stephanie Holmgren</string-name>
          <xref ref-type="aff" rid="aff2">2</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Charles Schmitt</string-name>
          <email>charles.schmitt@nih.gov</email>
          <xref ref-type="aff" rid="aff2">2</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Rima Habre</string-name>
          <email>habre@usc.edu</email>
          <xref ref-type="aff" rid="aff4">4</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Anne E Thessen</string-name>
          <email>annethessen@gmail.com</email>
          <xref ref-type="aff" rid="aff3">3</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Rebecca Boyles</string-name>
          <email>rboyles@rti.org</email>
          <xref ref-type="aff" rid="aff0">0</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Carmen Marsit</string-name>
          <email>carmen.j.marsit@emory.edu</email>
          <xref ref-type="aff" rid="aff1">1</xref>
        </contrib>
        <aff id="aff0">
          <label>0</label>
          <institution>Center for Data Modernization Solutions, RTI International.</institution>
          <addr-line>Durham, NC.</addr-line>
          <country country="US">USA</country>
        </aff>
        <aff id="aff1">
          <label>1</label>
          <institution>Gangarose Department of Environmental Health, Emory University Rollins School of Public Health</institution>
          ,
          <addr-line>Atlanta, GA</addr-line>
          ,
          <country country="US">USA</country>
        </aff>
        <aff id="aff2">
          <label>2</label>
          <institution>Office of Data Science, National Institute of Environmental Health Sciences (NIEHS)</institution>
          ,
          <addr-line>Research Triangle Park, North Carolina</addr-line>
          ,
          <country country="US">USA</country>
        </aff>
        <aff id="aff3">
          <label>3</label>
          <institution>University of Colorado Anschutz Medical Campus, Center for Health AI</institution>
          ,
          <addr-line>Aurora CO</addr-line>
          ,
          <country country="US">USA</country>
        </aff>
        <aff id="aff4">
          <label>4</label>
          <institution>University of Southern California</institution>
          ,
          <addr-line>Los Angeles, CA</addr-line>
          ,
          <country country="US">USA</country>
        </aff>
      </contrib-group>
      <fpage>4</fpage>
      <lpage>9</lpage>
      <abstract>
        <p>Standard language is critical for helping scientists share, compare, and reanalyze data. The increased use of automatization and AI technologies has made the adoption of machine interpretable language essential. Due to the broadness of the domains that are under the environmental health umbrella there is not yet a set of common standard terminologies. To address this lack of standardized language, NIEHS has launched the Environmental Health Language Collaborative (EHLC) https://www.niehs.nih.gov/research/progra ms/ehlc/index.cfm. This is a new initiative to advance community development and application of a harmonized language for describing Environmental Health Science (EHS) research. As a first step toward the development of standard terminology, a working group of environmental health researchers and NIEHS program officers established an initial set of four general use cases. Here we present one of the initial use cases on placebased exposures. This preliminary work is intended to be expanded as the community develops. EHLC is seeking larger community involvement as well as additional use cases. NIEHS encourages anyone interested in advancing this mission to engage in this community.</p>
      </abstract>
    </article-meta>
  </front>
  <body>
    <sec id="sec-1">
      <title>-</title>
      <p>1</p>
    </sec>
    <sec id="sec-2">
      <title>1. Introduction</title>
      <p>Environmental health (EH) is a science that
studies the effect of exposure to
environmental factors on human health. The
definition of environment is wide and
includes the “totality of exposures we face
throughout our lives, e.g., the food we ingest,
the air we breathe, the objects we touch, the
psychological stresses we face, the activities
in which we engage” [1] EH research is not
just focused on external exposures, but also
considers the molecules in our body that
derive from external exposures, the
environmental influences we receive through
our parents, the socio-economic factors that
play into disparities in health as well as
research that seeks to remediate and reduce
the impact of these factors, e.g., by
engineering plants that can remove or reduce
pollutants.</p>
      <p>The EH field covers a diversity of domains
and methodologies, such as environmental
epidemiology, toxicology, clinical and
translational research, immunology,
microbiology, exposure science, social
science, and environmental engineering.
Progress in EH research depends on the
ability to compare, contrast, and integrate data
from across the field, which requires adoption
of the principles of Findable, Accessible,
Integrable, and Reusable (FAIR) [2, 3]data.
FAIR requires the use of either common or
comparable language in describing scientific
data, metadata, and findings.</p>
      <p>The breadth of the EH field challenges the use
of a common language, not only because there</p>
      <p>© 2022 Copyright for this paper by its authors. Use permitted under Creative
Commons License Attribution 4.0 International (CC BY 4.0).</p>
      <p>CEUR Workshop Proceedings (CEUR-WS.org)
are inconsistencies and gaps in the
terminologies and ontologies used within
subfields, but scientific language is often
domain-specific and standardizing or even
harmonizing language across subfields is
especially challenging.</p>
      <p>To address the need for common language,
NIEHS has launched the Environmental
Health Language Collaborative (EHLC)[4]
https://www.niehs.nih.gov/research/program
s/ehlc/index.cfm. This is a new initiative to
advance community development and
application of a harmonized language for
describing Environmental Health Science
(EHS) research.</p>
      <p>The proposed mission of this community is
to:
•
•
•
•
•</p>
      <p>Apply language standards and best
practices for accurate environmental
health data and knowledge
representation
Cultivate a vocabulary aware
environmental health community
through training and education
Foster community-based
development of harmonized
vocabularies, terminologies, and
ontologies
Identify use cases for applying
knowledge organization systems in
research
Promote and develop methods and
tools for applying harmonized
language in research
A first step towards a practical approach has
been asking what scientific questions would
benefit most from development and adoption
of a harmonized language standard? A
working group of environmental health
researchers and NIEHS program officers
developed an initial set of five general use
cases examples as starting points for
community discussion. Working groups led
by use case champions were formed from the
community to address each use case. The
working group teams decided to focus all the
use cases on the effect of Particulate Matter
(PM) main component of the air pollutants on
Asthma as a common theme to unite their
work. ‘Asthma is a disease of the respiratory
tract which is caused by a combination of
environmental and genetic factors’ [5, 6].
‘Particulate matter is an environmental material
which is composed of microscopic portions of
solid or liquid material suspended in another
environmental material’[7, 8]. PM derives
from multiple different sources, such as
vehicle and industrial emissions from fossil
fuel combustion, cigarette smoke, and
burning organic matter, such as wildfires, as
well as chemical reactions that can form PM
from precursors.</p>
      <p>WHO has estimated that 4.2 million deaths
occur as a result of exposure to ambient
(outdoor) air pollution. (
https://www.who.int/health-topics/airpollution - tab=tab_2 ).</p>
      <p>Although all the five use cases focus on
Asthma and PM, each of them is trying to
answer different questions:
1. What data exists for a given
chemical/endpoint/exposure
scenario?
2. How best to combine data from
multiple independent studies?
3. Given measures of biological
responses to one or more exposures,
what are the biological processes that
might be related to the observed
changes?
4. What are the biomarkers, phenotypes,
and/or outcomes that can be measured
and used as an indicator of exposure?
5. What do my unique exposure
conditions based on where I live and
work (E.g., Geographical Location,
Occupation, Regulations, Hobbies)
indicate about potential risks to my
health?
Due to space limitation, we present the very
preliminary work done for use case five to
begin building the ontological representation
of environmental exposures and social
stressors or factors assessed based on place
and geospatial information.
2.</p>
    </sec>
    <sec id="sec-3">
      <title>Methods and Results</title>
      <p>Geospatial data are composed of three general
components Object, Event, Location, and
each of these components has specific
characteristics that are time related Fig (1).</p>
      <p>Members of the Geospatial Working Group
started by looking at an available data set
from the Personalized Environment and
Genes Study (PEGS)
(https://www.niehs.nih.gov/research/clinical/
studies/pegs/index.cfm).</p>
      <p>The study’s panel of experts had already
identified the initial set of essential
components to represent the geospatial data.
Because we are using an existing list of data
elements, the first step was to look at the OBO
Foundry ontologies [9] to see if those data
elements were already captured in existing
ontologies. Figure 2 shows a representation of
the data elements that were captured and their
relations. The different box color represents
the different ontologies from which the terms
were imported: Exposure Ontology (ExO)
[10], Gazetteer (GZ)
(http://environmentontology.github.io/gaz/),
Ontology of Biomedical Investigations (OBI)
[11, 12], phenotype and trait ontology
(PATO) [13]. In italic are the relations from
the relation Ontology (RO) [14] that we have
used to link the terms. In addition to the
imported terms, new terms have been
identified as ‘stressor detection assay’ and
‘stressor detector’. For the stressor detection
assay we are proposing the following
definition: ‘an assay that aims to detect
exposure stressor’. We are proposing the
stressor detection to be a child of a more
general term assay defined in OBI.</p>
      <p>The second additional term is a stressor
detector.</p>
      <p>We are proposing the following definition: Is
a role that inheres in a material entity, and
which is realized through a process of
exposure stressor detection.</p>
      <p>These two new terms as well as their
definitions have been proposed to the
ontology community.</p>
      <p>The red triangle in Figure 2 represents the
term that is the linking node between Figures
2 and 3.</p>
      <p>We then explored the ability of ontology to
capture more specific geographical types of
information. Figure 3 shows a list of terms
related to geographic location. There are
terms like latitude measurement datum,
longitude measurement datum that have been
already described in Ontology of Biomedical
Investigations. Other terms like geographical
identifier (GEO ID) and Buffer zone, which
are commonly used in geospatial studies, are
not present in any ontology.</p>
      <p>The Census Bureau and other state and
federal agencies are responsible for assigning
geographic identifiers, or GEOIDs, to
geographic entities to facilitate the
organization, presentation, and exchange of
geographic and statistical data.
(https://www.census.gov/programssurveys/geography/guidance/geoidentifiers.html)
We have classified the GEO ID term as
identifier class defined in the IAO
(https://obofoundry.org/ontology/iao.html).
We have modified the Census Bureau
definition for the GEO ID to be ‘is an
identifier composed by numeric codes that
uniquely identify all administrative/legal and
statistical geographic areas for which the
Census Bureau tabulates data.’
Another term that we needed to represent is a
Buffer Zone. This is a very common term used
to define a zone and its characteristics, that
are the object of the study. Although there is
this term in ENVO its classification under
administrative region does not fit with our
usage of the term. In our use case the buffer
zone is used to define a zone from which
collecting data (point, line, area) that is
equidistant from the stressor.</p>
      <p>As is shown in Figure 3 classification of this
term is still under discussion as well as how
to relate it to a specific geographic location.</p>
    </sec>
    <sec id="sec-4">
      <title>3. Discussion</title>
      <p>Geospatial studies use several heterogeneous
data types. Although some efforts have been
developed to create a common language like
the Open Geospatial Consortium (OGC)
(https://www.ogc.org/), there is still a lack of
standardized machine-readable terminology.
As ontology good practice we are reusing
several terms from other OBO Foundry
ontologies. We are creating new relations
between these terms to better represent
geospatial information. For the terms that
were not found in other ontologies we have
created a new term and definitions.</p>
      <p>This is a preliminary attempt to use an
ontological representation of the geospatial
data for an exposure. Our near future goal for
the use cases is to extract and represent the
minimal information necessary for capturing use
cases data. That could serve as reference for the
environmental data
These efforts are being developed under the
community-driven Environmental Health
Language Collaborative to ensure an open
and broad community participation and
development of harmonized language</p>
    </sec>
    <sec id="sec-5">
      <title>4. Acknowledgements</title>
      <p>Environmental Health Language
Collaborative. Members of Environmental
Health Language Collaborative Geospatial
working group</p>
    </sec>
    <sec id="sec-6">
      <title>5. References</title>
      <p>Uncategorized References
1.
2.
3.
4.</p>
    </sec>
  </body>
  <back>
    <ref-list>
      <ref id="ref1">
        <mixed-citation>
          <string-name>
            <surname>Miller</surname>
            ,
            <given-names>G.</given-names>
          </string-name>
          ,
          <source>The Exposome: A primer</source>
          <year>2014</year>
          , https://doi.org/10.1016/C2013- 0-06870-3:
          <string-name>
            <given-names>Elseview</given-names>
            <surname>Inc</surname>
          </string-name>
          .
        </mixed-citation>
      </ref>
      <ref id="ref2">
        <mixed-citation>
          <string-name>
            <surname>Wilkinson</surname>
          </string-name>
          ,
          <string-name>
            <surname>M.D.</surname>
          </string-name>
          , et al.,
          <article-title>The FAIR Guiding Principles for scientific data management and stewardship</article-title>
          .
          <source>Sci Data</source>
          ,
          <year>2016</year>
          . 3: p.
          <fpage>160018</fpage>
          .
        </mixed-citation>
      </ref>
      <ref id="ref3">
        <mixed-citation>
          <string-name>
            <surname>Wilkinson</surname>
          </string-name>
          ,
          <string-name>
            <surname>M.D.</surname>
          </string-name>
          , et al.,
          <article-title>Addendum: The FAIR Guiding Principles for scientific data management and stewardship</article-title>
          .
          <source>Sci Data</source>
          ,
          <year>2019</year>
          .
          <volume>6</volume>
          (
          <issue>1</issue>
          ): p.
        </mixed-citation>
      </ref>
      <ref id="ref4">
        <mixed-citation>
          <string-name>
            <surname>Holmgren</surname>
            ,
            <given-names>S.D.</given-names>
          </string-name>
          , et al.,
          <article-title>Catalyzing Knowledge-Driven Discovery in Environmental Health Sciences through a Community-Driven Harmonized Language</article-title>
          .
          <source>Int J Environ Res Public Health</source>
          ,
          <year>2021</year>
          .
          <volume>18</volume>
          (
          <issue>17</issue>
          ).
        </mixed-citation>
      </ref>
      <ref id="ref5">
        <mixed-citation>
          <string-name>
            <surname>Schriml</surname>
            ,
            <given-names>L.M.</given-names>
          </string-name>
          , et al.,
          <source>The Human Disease Ontology 2022 update.</source>
        </mixed-citation>
      </ref>
      <ref id="ref6">
        <mixed-citation>
          <source>Nucleic Acids Res</source>
          ,
          <year>2022</year>
          .
          <volume>50</volume>
          (
          <issue>D1</issue>
          ): p.
        </mixed-citation>
      </ref>
      <ref id="ref7">
        <mixed-citation>
          <string-name>
            <surname>D1255-D1261.</surname>
          </string-name>
        </mixed-citation>
      </ref>
      <ref id="ref8">
        <mixed-citation>
          <string-name>
            <surname>Schriml</surname>
            ,
            <given-names>L.M.</given-names>
          </string-name>
          , et al.,
          <source>Human Disease Ontology 2018 update: classification, content and workflow expansion.</source>
        </mixed-citation>
      </ref>
      <ref id="ref9">
        <mixed-citation>
          <source>Nucleic Acids Res</source>
          ,
          <year>2019</year>
          .
          <volume>47</volume>
          (
          <issue>D1</issue>
          ): p.
        </mixed-citation>
      </ref>
      <ref id="ref10">
        <mixed-citation>
          <string-name>
            <surname>D955-D962.</surname>
          </string-name>
        </mixed-citation>
      </ref>
      <ref id="ref11">
        <mixed-citation>
          <string-name>
            <surname>Buttigieg</surname>
            ,
            <given-names>P.L.</given-names>
          </string-name>
          , et al.,
          <article-title>The environment ontology: contextualising biological and biomedical entities</article-title>
          .
          <source>J Biomed Semantics</source>
          ,
          <year>2013</year>
          .
          <volume>4</volume>
          (
          <issue>1</issue>
          ): p.
          <fpage>43</fpage>
          .
        </mixed-citation>
      </ref>
      <ref id="ref12">
        <mixed-citation>
          <string-name>
            <surname>Buttigieg</surname>
            ,
            <given-names>P.L.</given-names>
          </string-name>
          , et al.,
          <article-title>The environment ontology in 2016: bridging domains with increased scope, semantic density, and interoperation</article-title>
          .
          <source>J Biomed Semantics</source>
          ,
          <year>2016</year>
          .
          <volume>7</volume>
          (
          <issue>1</issue>
          ): p.
          <fpage>57</fpage>
          .
        </mixed-citation>
      </ref>
    </ref-list>
  </back>
</article>