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  <front>
    <journal-meta />
    <article-meta>
      <title-group>
        <article-title>An Ontology For Specifying Spatiotemporal Scopes in Life Cycle Assessment</article-title>
      </title-group>
      <contrib-group>
        <contrib contrib-type="author">
          <string-name>Bo Yan</string-name>
          <xref ref-type="aff" rid="aff1">1</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Yingjie Hu</string-name>
          <xref ref-type="aff" rid="aff1">1</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Brandon Kuczenski</string-name>
          <xref ref-type="aff" rid="aff1">1</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Krzysztof Janowicz</string-name>
          <xref ref-type="aff" rid="aff1">1</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Andrea Ballatore</string-name>
          <xref ref-type="aff" rid="aff1">1</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Adila A. Krisnadhi</string-name>
          <xref ref-type="aff" rid="aff2">2</xref>
          <xref ref-type="aff" rid="aff3">3</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Yiting Ju</string-name>
          <xref ref-type="aff" rid="aff1">1</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Pascal Hitzler</string-name>
          <xref ref-type="aff" rid="aff3">3</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Sangwon Suh</string-name>
          <xref ref-type="aff" rid="aff1">1</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Wesley Ingwersen</string-name>
          <xref ref-type="aff" rid="aff0">0</xref>
        </contrib>
        <aff id="aff0">
          <label>0</label>
          <institution>US Environmental Protection Agency</institution>
          ,
          <country country="US">USA</country>
        </aff>
        <aff id="aff1">
          <label>1</label>
          <institution>University of California</institution>
          ,
          <addr-line>Santa Barbara</addr-line>
          ,
          <country country="US">USA</country>
        </aff>
        <aff id="aff2">
          <label>2</label>
          <institution>University of Indonesia</institution>
          ,
          <country country="ID">Indonesia</country>
        </aff>
        <aff id="aff3">
          <label>3</label>
          <institution>Wright State University</institution>
          ,
          <country country="US">USA</country>
        </aff>
      </contrib-group>
      <abstract>
        <p>Life Cycle Assessment (LCA) evaluates the environmental impact of a product through its entire life cycle, from material extraction to final disposal or recycling. The environmental impacts of an activity depend on both the activity's direct emissions to the environment as well as indirect emissions caused by activities elsewhere in the supply chain. Both the impacts of direct emissions and the provisioning of supply chain inputs to an activity depend on the activity's spatiotemporal scope. When accounting for spatiotemporal dynamics, LCA often faces significant data interoperability challenges. Ontologies and Semantic technologies can foster interoperability between diverse data sets from a variety of domains. Thus, this paper presents an ontology for modeling spatiotemporal scopes, i.e., the contexts in which impact estimates are valid. We discuss selected axioms and illustrate the use of the ontology by providing an example from LCA practice. The ontology enables practitioners to address key competency questions regarding the effect of spatiotemporal scopes on environmental impact estimation.</p>
      </abstract>
      <kwd-group>
        <kwd>Life cycle assessment</kwd>
        <kwd>ontology</kwd>
        <kwd>spatiotemporal scopes</kwd>
      </kwd-group>
    </article-meta>
  </front>
  <body>
    <sec id="sec-1">
      <title>-</title>
      <p>
        Life Cycle Assessment (LCA) is a method for analyzing the environmental impact of a
product or a service through all stages of its life cycle [
        <xref ref-type="bibr" rid="ref13 ref5">5, 13</xref>
        ]. LCA is designed to take
into consideration the entire life cycle and product chain, having a holistic viewpoint in
dealing with environmental issues. The life cycle of a product or a service normally
includes raw material acquisition, manufacturing process, trading process, product usage,
recycling process, and waste management. Due to the diverse types of information
required to conduct an LCA, knowledge from different domains needs to be gathered and
interpreted together. This process is challenging because there is no universal ontology
or vocabulary among (or even within) domains of study, creating substantial barriers
for information sharing and integration among different data providers.
      </p>
      <p>
        An important stage of LCA is the creation of a Life Cycle Inventory (LCI), which
consists of representing economic activities as a collection of unit processes linked
together through interdependency relations [
        <xref ref-type="bibr" rid="ref3">3</xref>
        ]. A global understanding of these economic
activities and the data that comes along require a clear capture of the interdependencies
and relationships between the used nomenclatures. Semantic technologies and
ontologies are promising methods to support interoperability in LCA. They foster semantic
interoperability without the need to enforce a single domain schema.
      </p>
      <p>
        Researchers have long been considering the significance of a spatial perspective in
LCA [
        <xref ref-type="bibr" rid="ref11 ref2 ref6">11, 2, 6</xref>
        ]. Because environmental impacts in LCA are driven by the emission of
substances into the environment, site-specific assessments are often necessary to deal
with spatial variation, which refers to differences in geology, topography, land cover,
and so forth [
        <xref ref-type="bibr" rid="ref12">12</xref>
        ]. The geographic location of a process can also be important in
determining the impacts of activities that occur elsewhere in the supply chain, such as
freight transport. Likewise, a number of studies have argued that a dynamic approach
is necessary to account for temporal variations in activities or impacts [
        <xref ref-type="bibr" rid="ref14 ref9">9, 14</xref>
        ]. These
investigations show that the spatiotemporal scope of assessed activities is important
to LCA. While recent studies [
        <xref ref-type="bibr" rid="ref18 ref3">3, 18</xref>
        ] have used semantic technologies for LCA, most
of them are too general and have not taken scoping into account. Here, we introduce
a compact ontology that formalizes the spatiotemporal scope of activities in LCA and
integrates well with previously published LCA-related ontology design patterns [
        <xref ref-type="bibr" rid="ref15 ref8">8, 15</xref>
        ].
      </p>
      <p>While our work is concerned with LCA as a diverse field that will benefit from the
ontological modeling of its data and workflows, spatiotemporal scopes are relevant for
a multitude of other domains. Thus, the core part of our ontology can be regarded as an
ontology design pattern (ODP).
2</p>
    </sec>
    <sec id="sec-2">
      <title>Competency Questions</title>
      <p>Designing an ontology requires generic use cases to capture the recurring problems in
one or multiple domains. Competency questions have been recognized as an effective
approach to identify such use cases. Competency questions are frequent queries that
subject matter experts would like to submit to a knowledge base to find answers. The
following listing shows examples of competency questions that have been identified by
international LCA experts during the GeoVoCamp Santa Barbara 2015:
– Question 1: "What is the emission of activity a at place p at time t?"
– Question 2: "What are the supply chain requirements of activity a when it happens
at place p1 and time t1?"
– Question 3: "What is the difference of activity a at places p1 and p2 at the same
time t?"
– Question 4: "What is the difference of activity a at times t1 and t2 at the same
place p?"</p>
      <p>As can be seen, answering the four competency questions requires four main
concepts: Activity, Flow, Place, and Time. An activity in LCA may have Requirement
(Question 2) and Outcome (e.g., emission) (Question 1), which collectively make up
flows. To effectively link these concepts, proper relations have also been specified.
3</p>
    </sec>
    <sec id="sec-3">
      <title>Spatiotemporal Scoping Ontology</title>
      <p>
        The ontology for spatiotemporal scopes5 is developed based on the existing Activity
ODP, [
        <xref ref-type="bibr" rid="ref1">1</xref>
        ] which also includes concepts such as Activity, Requirement, and Outcome.
Since the Activity ODP focuses on human activities, we modify and extend it to fit
5 http:==descartes-core:org=ontologies=lca=1:0=stscope:owl
the activities in the domain of LCA and add the scoping on top of the resulting model.
Figure 1 provides an overview of the spatiotemporal scoping ontology. In the following,
we describe the classes and relations by showing selected description logics axioms.
      </p>
      <p>SpatiotemporalScope: This class represents the spatial and temporal context
under which an LCA activity occurs. We define this class instead of directly using Place
and Time, because many requirements and outcomes are associated with the
spatiotemporal contexts rather than places and time (intervals) alone. SpatiotemporalScope is
associated with the classes Place and Time through the relations occursAtPlace and
occursAtTime. Time should be an interval because an LCA activity generally represents
the performance of a typical facility or a set of facilities over a time period, rather than
at a specific moment. A place is some, typically named, extent in geographic space,
e.g., a country or region. We do not specify both classes here and refer to OWL-Time
and GeoSPARQL for details (which implies that geometry types such as multi-part
polgyons can be used as spatial footprints of places). We assert that each spatiotemporal
scope has at least one place and time (see Eq. 1).</p>
      <sec id="sec-3-1">
        <title>SpatiotemporalScope v 9occursAtP lace:P lace u 9occursAtT ime:T ime u 9hasSpatiotemporalScope :Activity</title>
        <p>Note that we also provide role chains in the ontology (see Eq. 2 as example) but do not
discuss them here for lack of space.</p>
        <p>
          hasSpatiotemporalScope occursAtP lace v scopedByP lace
hasSpatiotemporalScope occursAtT ime v scopedByT ime
Activity: The Activity class represents activities in the LCA sense and thereby differs
from other conceptualizations of activities. An activity roughly corresponds to a unit
process as defined in the ISO 14044 standard [
          <xref ref-type="bibr" rid="ref7">7</xref>
          ], but may also indicate a reservoir,
stock, or natural process such as dissolution into fresh water. An activity always occurs
at a certain place (e.g. in a particular factory or river) in a particular time span. We
link Activity to SpatiotemporalScope through the relation hasSpatiotemporalScope. An
activity in LCA also has Requirement and Outcome.
        </p>
        <p>Activity v 9hasRequirement:Requirement u 9produces:Outcome
(4)
u 9hasSpatiotemporalScope:SpatiotemporalScope : : :
(1)
(2)
(3)</p>
        <p>Flow: A Flow is a highly generic concept in LCA mainly defined as a counterpart to
an activity. A flow may represent the transfer of matter, such as an emission of
combustion gases, or an exchange of services, such as transporting a good. A flow is exchanged
between an activity and another activity. Although flows are the products of processes,
many flows can exist independently of any process, can be accumulated in reservoirs,
and can have properties, such as economic value. A flow can play a role in both the
Requirement of one activity and Outcome of another, and thus, we define the relation of
hasRole. If the two activities in the exchange are industrial unit processes, the flow is
referred to as an intermediate flow. The two activities can be described as “partners” to
the exchange. A flow exchanged with the natural environment is called an elementary
flow. We formalize the class of Flow as below:</p>
      </sec>
      <sec id="sec-3-2">
        <title>F low v 9hasRole:(Requirement t Outcome)</title>
        <p>
          An ontology for flows has recently been developed and formally specifies the
distinctions made above [
          <xref ref-type="bibr" rid="ref8">8</xref>
          ].
        </p>
        <p>Requirement and Outcome: Any activity in LCA has required inputs and resulting
outputs. These inputs and outputs are formalized as Requirement and Outcome in our
ontology. The provision of Requirements and the disposition of Outcomes depend on
the specific place and time that an activity takes place. Thus, we define
SpatiotemporalRequirement as a subclass of Requirement, and associate it to the SpatiotemporalScope
using the relation isAssociatedWith. Similarly, we define SpatiotemporalOutcome as a
subclass of Outcome, and use isInfluencedBy to link it with SpatiotemporalScope.</p>
        <sec id="sec-3-2-1">
          <title>SpatiotemporalRequirement v Requirement</title>
        </sec>
        <sec id="sec-3-2-2">
          <title>SpatiotemporalOutcome v Outcome SpatiotemporalRequirement v 9isAssociatedW ith:SpatiotemporalScope SpatiotemporalOutcome v 9isInf luencedBy:SpatiotemporalScope</title>
          <p>4</p>
          <p>Domain &amp; Range Restrictions and Class Disjointness: In addition to the above
axioms, the pattern also defines a set of guarded domain and range restrictions.
Specifically, for each object property P pointing from the class A to the class B in Figure
1, we define 9P:B v A as the guarded domain restriction and A v 8P:B as the
guarded range restriction, which also acts as a local closure of P . For example, for
occursAtP lace property, we have:</p>
        </sec>
      </sec>
      <sec id="sec-3-3">
        <title>9occursAtP lace:P lace v SpatioT emporalScope</title>
      </sec>
      <sec id="sec-3-4">
        <title>SpatioT emporalScope v 8occursAtP lace:P lace</title>
        <p>Specific for hasRole property, we have:</p>
      </sec>
      <sec id="sec-3-5">
        <title>9hasRole:Requirement t 9hasRole:Outcome v F low</title>
      </sec>
      <sec id="sec-3-6">
        <title>F low v 8hasRole:(Requirement t Outcome)</title>
        <p>Finally, we assert class disjointness for every pair of classes in Figure 1, except when
the pair of classes are connected via rdfs:subClassOf.
(5)
(6)
(7)
(8)
(9)
(10)
(11)
(12)
(13)</p>
      </sec>
    </sec>
    <sec id="sec-4">
      <title>Use Case</title>
      <p>
        A use case was created by selecting a unit process from the US Life Cycle Inventory
database, in this case “Conditioned log, at plywood plant, US SE,” [
        <xref ref-type="bibr" rid="ref10">10</xref>
        ] depicted in
Figure 2. The data set was obtained from OpenLCA software in ILCD format [
        <xref ref-type="bibr" rid="ref17 ref4">4, 17</xref>
        ].
Conditioning is an intermediate step in the preparation of logs for the production of
plywood [
        <xref ref-type="bibr" rid="ref16">16</xref>
        ]. The activity’s requirements are its input flows: hogfuel biomass, electricity
from the grid, heat from the combustion of liquefied petroleum gas (e.g. propane), water,
and the debarked wood itself. Its outcome is its sole output flow, the conditioned logs.
      </p>
      <p>The scope of the activity is a plywood plant in the southeastern United States during
the year 2000. The mix of process energy reported is an averaged result of several
facilities within the scope. To use the data for LCA, each requirement would need to be
linked with an exchange partner that produced it as an outcome. Similarly, this activity’s
outcome could be exchanged with another partner activity that requires the logs as input.</p>
      <p>
        The competency questions presented above can be addressed through the selection
of exchange partners. A database can be constructed that accepts an activity
specification and a spatiotemporal scope and returns a list of exchange partners. The logistical
requirements associated with performing the exchange are implicit in the
spatiotemporal scopes of the partners. Differences in emissions resulting from the same activity in
a different scopes can be inferred through the differences in exchange partners.
This paper proposed a compact ontology to capture the spatiotemporal scope of
activities referred to in LCA inventory models. The pattern enables key competency questions
to be addressed by querying a spatiotemporally-explicit data resource. The pattern can
be used as a bridge between sets of activity and flow definitions and spatial modeling
ontologies. Future work will focus on integrating this ontology with other LCA
ontologies and ontology design patterns (such as [
        <xref ref-type="bibr" rid="ref8">8</xref>
        ]) in order to further enhance semantic
interoperability in LCA and improve the reproducibility of published LCA studies.
      </p>
    </sec>
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