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Environmental footprinting in health care: a primer

医療における環境フットプリント:入門 (AI 翻訳)

Jacob Fry, Angie Bone, Keiichiro Kanemoto, Carolynn L. Smith, Nick Watts

The Medical Journal of Australia📚 査読済 / ジャーナル2024-10-17#炭素会計Origin: Global経営インパクト: 調達リスク対象セクター: healthcare
DOI: 10.5694/mja2.52481
原典: https://doi.org/10.5694/mja2.52481
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🤖 gxceed AI 要約

日本語

医療システムは世界のGHG排出の4-5%を占め、その多くはサプライチェーン由来です。本稿は、医療の環境影響を評価するためのLCAとEE-IOAの手法を初心者向けに解説し、ハイブリッド手法の利点やシステム境界の重要性を説明します。医療従事者に環境持続可能性を品質の一部として考慮するよう提言します。

English

Healthcare systems contribute 4-5% of global GHG emissions, largely from supply chains. This primer introduces environmental footprinting methods (LCA, EE-IOA, hybrid) for healthcare, emphasizing system boundaries and indirect emissions. It calls for integrating environmental sustainability into healthcare quality and governance.

Unofficial AI-generated summary based on the public title and abstract. Not an official translation.

📝 gxceed 編集解説 — Why this matters

日本のGX文脈において

日本では、医療分野の脱炭素化はまだ初期段階ですが、SSBJ開示やサプライチェーン排出量算定の要請が強まる中、医療機関も間接排出の把握が求められる可能性があります。本稿は、医療特有のフットプリント手法の基礎を提供し、今後の日本での医療GX推進に役立ちます。

In the global GX context

Globally, healthcare decarbonization is gaining attention, with initiatives like the NHS net-zero commitment. This primer aligns with ISSB/CSRD trends by explaining how to measure Scope 3 emissions in healthcare, supporting organizations in meeting disclosure requirements and reducing environmental impact.

👥 読者別の含意

🔬研究者:Provides a clear overview of LCA and EE-IOA methods applicable to healthcare, useful for researchers studying healthcare sustainability.

🏢実務担当者:Offers practical guidance for healthcare organizations to start measuring their environmental footprint, especially indirect emissions.

🏛政策担当者:Highlights the need for standardized environmental data collection and reporting in healthcare, informing policy development.

📄 Abstract(原文)

Health care systems are responsible for 4–5% of global greenhouse gas (GHG) emissions.1, 2 There is increasing pressure to reduce the environmental effects of health care as more health professionals recognise its contribution to climate change.3, 4 However, measuring environmental effects and assessing progress towards decarbonisation are not trivial processes because the mechanisms driving environmental burdens are often hidden. Although much of the early focus in health has been on decarbonisation of building and transport assets, most of health care's GHG emissions occur within the supply chains that provision the health care system before the final delivery of services.5 This article is intended to serve as a beginner's introduction to the environmental footprinting techniques that can be applied to uncover health care's environmental impacts, including impacts occurring along supply chains. This article focuses on GHG emissions, but many other pollutants and environmental stressors can be assessed using these methods. Environmental impacts can be separated into “direct” and “indirect” impacts. Direct impacts occur within an organisation's physical boundary, for example hospital grounds. Indirect impacts occur outside this immediate boundary, for example impacts from purchased products. Direct impacts are relatively easy to estimate using fossil fuel consumption and utility bills. In contrast, estimating indirect emissions is more challenging for health care organisations and requires detailed data on the quantity or cost of procured products and services and the application of environmental footprinting techniques. An organisation's indirect emissions form part of their suppliers’ direct emissions and likely occur in other regions and jurisdictions, rendering them more abstract and intangible. Quantifying indirect environmental impacts requires consideration of the supply chains delivering goods and services to final consumption. Supply chains link production layers together, where at each stage numerous inputs and components are combined to make intermediate products. This can be depicted as a tree branching upwards and outwards from the consumer, with each node representing a production stage (Box 1). Here, “upstream” refers to layers occurring before the product reaches a consumer, and “downstream” refers to layers after final consumption, including disposal of the product. Environmental effects can occur at each layer and accumulate along the supply chain as more layers are included.6 Eventually, supply chains reach consumers as final products. Accounting for all upstream environmental impacts associated with a product or service is onerous because of the large number of production layers and the many inputs into each layer. An illustrative example of supply chain is “fossil fuel combustion > petrochemical refining > plastic sample jars > pathology services”, which is just one of the many supply chains contributing to “pathology services”.7 The “system boundary” is a conceptual limit within which environmental effects are captured by an assessment method.8 The boundary is considered “incomplete” when all important activities are not within the boundary, resulting in some fraction of environmental effects being uncounted.9 An awareness of the defined system boundary is important when calculating the full environmental footprint of a product or process and when making comparisons. The extent to which unaccounted impacts are significant depends on the process and activity and may include, for example, impacts arising from capital works, infrastructure and the services sector. Box 2 depicts the system boundary in relation to final consumption and intermediate production stages. Although in common use, these scopes are a simplification and do not always neatly align with organisation structure or function. For example, emissions from ambulatory patient transport may be attributed to a health system's scope 1 emissions; however, patient self-transport emissions remain uncounted. In addition, the scope framework does not consider shared responsibility of emissions between upstream and downstream actors in the supply chain. These difficulties reflect wider societal complexities in attributing responsibility for emissions reductions.11 Two main environmental footprinting methods can be distinguished: life cycle assessment (LCA) and environmentally extended input–output analysis (EE-IOA). Process-based LCA is a technique for assessing environmental impacts of specific products or processes. LCA maps each life cycle stage of a product or activity, such as raw materials extraction, manufacturing, product use, and waste treatment and disposal, and accounts for the environmental impacts occurring at each stage.12 There are two main types of LCA: attributional (ALCA) and consequential (CLCA) life cycle assessment.13, 14 ALCA accounts for environmental burdens associated with a product's life cycle, including production, use and disposal. CLCA describes how these flows change in response to decisions or changes, for example material design changes. An LCA analyst selects the processes and inputs to include in a particular assessment, which requires judgement and may result in truncated accounting of environmental impacts.6, 8 Many health care LCAs have been done, for example, assessing the impacts of surgical and anaesthetic care,15 magnetic resonance imaging machines,16 and health care building construction.17 Repositories such as HealthcareLCA18 and other literature reviews provide useful compilations of LCA studies relevant to health care.19 Input–output analysis (IOA) is a well established method for tracing environmental impacts along supply chains.20, 21 An environmental footprint calculated using IOA represents a retrospective allocation of impacts among products and services delivered to final consumption. This technique allocates all economy-wide production impacts to final products, leaving no impacts unallocated. The technique also avoids double counting, as all production environmental effects are attributed only once to final products. EE-IOA methods have been used to perform global assessments of health care1, 2 as well as national level assessments.5, 22 The sector detail of IO models is constrained by the underlying national accounting data, which limits IOA from analysing very specific activities or sectors. For example, IO models may distinguish hospitals from other health care services; however, specific activities such as oncology are likely beyond the model resolution. Similarly, issues of price can also distort the footprint calculation, for example in the case of low cost versus high cost pharmaceuticals. Hybrid approaches can be employed to overcome the limitations inherent in both LCA and IOA methods. LCA and EE-IOA methods can be seen as complementary:23 LCA performs a bottom-up attribution of environmental effects to specific processes, and EE-IOA performs a top-down allocation of economy-wide environmental effects to final products. Hybrid approaches augment IOA-based footprinting methods with process-specific LCA data, which has the effect of mitigating the sectoral specificity issues of IOA. In addition, the use of IOA guarantees system boundary completeness.24 Hybrid methods were used to do carbon footprinting of England's National Health Service (NHS).25 Which assessment technique should be used depends on the health care context and research question. In general, questions involving diagnostic methods and treatments are best answered using LCA techniques, whereas assessing overall progress at the health system level is more suited to EE-IOA. International Organization for Standardization (ISO) 14040:2006 and 14044:2006 provide guidelines to practitioners doing life cycle assessments. The European Union is introducing new regulations to combat greenwashing26 and has its own guidelines on how LCAs should be done.27 IOA and its extensions are also governed by global standards.28 Adherence to these standards and guidelines can provide an indication of the quality and trustworthiness of sustainability assessments and enables comparison between studies. Environmental impacts will increasingly need to be assessed and considered as part of health sector decision making at every level. However, systems for environmental data collection, storage and analysis are often limited in many health systems and usually not standardised or linked to clinical and population outcomes.29 Information about product environmental performance is rarely provided by manufacturers, and the underlying data are often inaccessible.30 Health care professionals have an important role in normalising consideration of the environmental impact of health care and advocating for availability of evidence and the supporting infrastructure to evaluate and reduce that impact. We are not suggesting that environmental footprinting is the primary role of health care workers, nor are we suggesting that considerations of environmental impact should take precedence over clinical outcomes. Rather, environmental sustainability should be considered as a dimension of quality, safety and good governance alongside patient and population health outcomes. We thank Anthony Capon, Richard Wood and Michael Frommer for their comments on an earlier version of this manuscript. No relevant disclosures. Not commissioned; externally peer reviewed. * This tree grows rapidly with production layer depth to encompass many inputs and distinct supply chains.

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