Environmental sustainability assessment of terrestrial ...

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oriented and affects the amount of natural stocks and funds and/or ... (e.g., forestry, agriculture, renewable energy). (4) ... Solar energy required to regenerate soil.
th SETAC Europe 26 Annual Meeting, Nantes, France, 22-26 May 2016

Environmental sustainability assessment of terrestrial land use in LCA overview and advanced methods Taelman, S.E., Schaubroeck, T., De Meester, S., Boone, L., Dewulf, J.

Background Competition for land among different uses is becoming acute

Several life cycle impact assessment (LCIA) methods try to evaluate environmental damages due to human activities on land

Consequences of an intensified land use include, amongst others, soil degradation, loss of biodiversity, erosion, etc.

BUT accounting for land use impacts in LCA is not straightforward! OBJECTIVES: • Identifying natural land-based processes and resources • Overview of available LCA land use impact indicators • Proposal of 2 enhanced LCIA methods to account for land use impacts on ecosystem health

Important to reduce the pressure on land resources and natural ecosystems to ensure land availability for future generations

Material and methods Anthropogenic land use is mainly socio-culturally or economically oriented and affects the amount of natural stocks and funds and/or disturbs certain ecosystem processes

Proxy used by the indicator to assess land use impacts on the AoP natural resources or the AoP ecosystem health Solar exergy metabolized within natural vegetation

Net primary production loss (1,2,3)

Soil Núñez et al. (2013)

Land area Number of plant species (+ rarity )

Genetic resources

Fossils

Metals Habitat suitability matrix (plant and animal species)

(1,4)

affects

Biodiversity Weidema & Lindeijer (2001) Koellner & Scholz (2007) Koellner & Scholz (2008) De Baan et al. (2013) Frischknecht et al. (2006) Frischknecht & Büsser Knöpfel (2013) Goedkoop & Spriensma (2001) Jolliet et al. (2003) Goedkoop et al. (2009) Vogtländer et al. (2014) Geyer et al. (2010) De Baan et al. (2015) Souza et al. (2013)

Solar energy required to regenerate soil

Fresh water

Maintenance of biodiversity

Primary production

Erosion regulation

Photosynthesis

Waste treatment

Natural hazard regulation

Overview of LCIA indicators that are considered to assess the impact of land use on: • AoP natural resources • AoP ecosystem health

Evapotranspiration of potential natural vegetation (PNV) Erosion regulation Núñez et al. (2013)

Tons of soil eroded ha-1 yr-1, cation exchange capacity, water flow rate and water recharge rate

Air quality and climate regulation

Water purification

Water cycling

Water regulation

Disease regulation

Water cycling Maes et al. (2009) Erosion and fresh water regulation, water purification Saad et al. (2011) Saad et al. (2013)

-1

Fossil-combustion-equivalent’ tonnes of C ha

Climate regulation Müller-Wenk and Brandão (2010)

Pollination

Nutrient cycling

Natural biomass Dewulf et al. (2007) Alvarenga et al. (2013) Taelman et al. (2014) Alvarenga et al. (2015) Brandão and Milà i Canals (2013)

Soil organic carbon change

Biomass

Soil formation

Natural ecosystem processes

Economically oriented -Transport (4) -Land based production (e.g., forestry, agriculture, renewable energy)(4) -Mining/extraction of metals, fossils, sediments, etc. (4) -Residential, industrial and commercial infrastructure (4)

affects

Sediments

AoP

ECOSYSTEM HEALTH

Socio-culturally oriented -Human health and human well-being (need for food, clean air, etc.)(4) -Provision of work (1) -Recreation and ecotourism (1) -Cultural diversity (1) -Spiritual and religious values (1) -Knowledge systems (1) -Educational values (1) -Inspiration (1) -Aesthetic values (1) -Social relations (1) -Sense of place (1) -Cultural heritage values (1)

Natural resources (stocks and funds)

Anthropogenic LAND USE

Minerals

LCIA Indicators that assess land use impacts on

NATURAL RESOURCES

Data source of indicator

Soil Quality (*) Milà i Canals et al. (2007a) Brandão et. al (2011)

(1)

MEA (2005) de Groot et al. (2002) (3) Dewulf et al. (2015) (4) Pérez-Soba et al. (2008) (2)

Supporting Supporting processes processes

Regulating Regulating processes processes

Net primary production (NPP) is a key process for life on earth  good starting point to determine the impact land use may have on ecosystem health HUMAN INTERVENTIONS

DIRECT IMPACTS

MIDPOINT level categories

ENDPOINT level categories AoP

Impacts on natural stocks and funds

Development of LCIA indicators that account for the actual loss of NPP • HANPP • Hemeroby (naturalness)

LAND USE (occupation & transformation)

Chemical inputs (fertilizers, pest control) (1,2) Drainage/irrigation (1,2) Soil compaction (1) Fragmentation (1,2) Vegetation cover modification (1,2) Surface sealing (2) (Over)exploitation

Loss of natural resources (e.g., fossil resources)

Damage to natural resources (resource depletion)

Natural resources

Damage to the natural environment

Ecosystem health

Damage to human health

Human health

(1,2)

Loss of supporting services (e.g., net primary production)

Impacts on natural ecosystem processes

Loss of regulating services (e.g., climate regulation)

Loss of biodiversity (e.g., reduction in amount of plant species) (1) (2)

Koellner et al. (2013) Souza et al. (2015)

Results and conclusions HANPP approach LADA (land use systems of the world) INTERSECTION

Countries of the world

Hemeroby approach World map (3680 zone, country and land use specific) INTERSECTION

Naturalness Degradation Potential (NDP) assigned to different land use types as described in the LCA database ecoinvent version 2.2, 3.0 and 3.1 Zone specific CFs (area-weighted averages of HANPP)

HANPP (MJex m-2 year-1)

Limitations • Based on LADA land use classes: not completely compatible with commonly used background databases (e.g., ecoinvent) • Low resolution of the zonal map may add to uncertainty of final results (CFs)

Multiplying the NDP of a specific land use with the country-specific potential NPP  exergy-based CF that represents the loss of NPP at that particular area Limitations • The naturalness assigned to a certain land use type is based on a qualitive (subjective) ecological framework

Reference: Taelman, S.E., Schaubroeck, T., De Meester, S., Boone, L., Dewulf, J., (2016) Accounting for land use in life cycle assessment: the value of NPP as a proxy indicator to assess land use impacts on ecosystems. Science of the Total Environment 550, 143-156. Taelman, S.E. (2016) Environmental Sustainability Assessment of Algae Production Systems. Methodological development and case studies. PhD thesis, Ghent University, Belgium. ISBN 978-90-5989-878-3 Contact: [email protected]