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THE 8TH LIFE CYCLE<br />

CONFERENCE<br />

Pathways to Greening<br />

Global Markets<br />

An LCA and carbon foot printing<br />

conference hosted by the <strong>Australian</strong><br />

<strong>Life</strong> <strong>Cycle</strong> <strong>Assessment</strong> Society<br />

<strong>Abstracts</strong><br />

Platform and Shortform Presenters<br />

Novotel Sydney, Manly Pacific<br />

15th - 18th July 2013


Platform<br />

Presenters<br />

PATHWAYS TO<br />

GREENING GLOBAL<br />

MARKETS<br />

<strong>ALCAS</strong>


Ms Lynda Amitrano<br />

Sustainable Built Environment Manager, BRANZ<br />

Co Author - Dr Dave Dowdell, Principal Scientist - Sustainability, BRANZ, Roman Jaques, Senior Sustainable<br />

Building Scientist, BRANZ.<br />

An Overview of Developments in use of LCA and EPD in Building Environmental Rating Schemes<br />

Materials credits in green building rating systems have traditionally evolved from a consensus based<br />

understanding of environmental issues, often resulting in evaluation of products based on proxy measures of<br />

environmental performance, such as transport distance and having an ISO 14001 environmental management<br />

system (for example).<br />

Workshops with the New Zealand construction industry in 2010 showed a desire for more robust, flexible<br />

whole of life based assessment to provide a better basis for comparisons. The outputs of <strong>Life</strong> <strong>Cycle</strong><br />

<strong>Assessment</strong>s (LCA) and Environmental Product Declarations (EPD) are currently barely referenced in<br />

GBCA’sand NZGBC’s suite of building rating tools such as GreenStar and Home Star, although increasing local<br />

interest is evident as shown by the GBCA’s consultation on LCA in GreenStar. Internationally, standards that<br />

address application of LCA to construction products and buildings have been or are in the process of<br />

development, providing an underpinning framework for application of LCA to the built environment. This is<br />

resulting in changes to EPD schemes that seek closer alignment and increasing examples of building<br />

environmental rating tools that utilise LCA, EPD and whole building whole of life assessments in their building<br />

rating processes.<br />

This paper sets the scene by providing an overview of key international standards and how they have been<br />

shaping EPD schemes, particularly with respect to the long recognised need for better alignment of detailed<br />

requirements contained in scheme product category rules (PCRs). Furthermore, it provides examples of how<br />

building environmental rating tools are increasingly utilising LCA and EPD derived data about building products<br />

as part of a broader building level assessment across the life cycle.<br />

Mr Jonas Bengtsson<br />

Director, Edge Environment<br />

Co Author - Mr Scott Grierson, Chief Technology Manager - Research & Development, MBD Energy Limited.<br />

<strong>Life</strong> cycle assessment of a microalgae biomass cultivation, bio-oil extraction and pyrolysis<br />

processing regime<br />

A clear message from the ‘Technology Roadmap’ published by the US Department of Energy’s (DOE) Biomass<br />

Program is that there are many possible parameters to investigate in relation to the commercialisation of<br />

microalgae biomass, spanning the full spectrum from ‘species selection’ and ‘cultivation systems’, to<br />

‘intermediate constituents’, ‘conversion processes’ and ‘end use fuels and products’. Standardisation and<br />

comparison of results is therefore challenging, as different product pathways may require unique assumptions,<br />

functional units and/or allocation decisions. At present, there is no known LCA study within the current body<br />

of published work that assesses the pyrolysis conversion of microalgae biomass into its various co-products.


This paper presents the use of LCA of a microalgae biomass cultivation, bio-oil extraction and pyrolysis<br />

processing regime to gauge the likely environmental impact of this prospective new development on an<br />

industrial scale. Coupled to thermal conversion via slow pyrolysis, the prospect of biologically ‘sequestering’<br />

carbon derived from microalgae biomass as biochar, added to soil, is considered. Results indicated that an<br />

intensive closed culturing photobioreactor (PBR) system coupled to a pyrolysis process incurs a net increase in<br />

global warming impact and overall life cycle impact, nowithstanding biochar application.<br />

Results indicate that up to 50% of environmental impact in certain categories stems from the upstream<br />

influence of fertiliser production. Energy used in flue gas delivery and pumping during cultivation is also<br />

considerable, suggesting that current practice in closed cultivation systems does not yet adequately trade-off<br />

biomass productivity against operating intensity. Drying of the harvested microalgae biomass for pyrolysis<br />

processing is potentially a major hurdle in terms of process viability also. Overall, utilisation of nutrients<br />

derived from waste streams, integrating renewable energy and capture of process heat for more efficient<br />

drying are essential levers for reducing the environmental impact of this proposition.<br />

Dr Wahidul Biswas<br />

Senior Lecturer, Curtin University<br />

Co Authors - Mr Ahsanul Kabir, Mechnical Engieer, Dr Nazrul Islam, Senior Lecturer, Curtin University.<br />

<strong>Life</strong> cycle environmental benefits from the use of retrofit electric vehicles in Western Australia<br />

Electric vehicles are being considered to replace conventional combustion engine vehicles in the near future,<br />

and the notion is gaining momentum and popularity worldwide, especially due to zero tailpipe emissions<br />

associated with its propulsion mechanism. The paper presents the life cycle emissions savings in the use of<br />

retrofit electric vehicles in Western Australia. The emissions associated with aftermarket conversion of a<br />

conventional gasoline vehicle have been compared to that of the original vehicle over a lifespan mileage of<br />

150,000 kilometres.<br />

The study presents a methodology to evaluate GHG savings from electric mobility over an assumed lifespan<br />

mileage. A detailed life cycle assessment of four main electric propulsion components has been carried out<br />

based on available data from the manufacturers and past literature.<br />

The main focus of the study lies only on the electric propulsion mechanism and thus the life cycle impacts of<br />

the glider have not been considered. Two scenarios for the electric vehicle components were considered<br />

under the investigation, one where the electric drivetrain components to be manufactured overseas, and the<br />

other where the components were to be manufactured locally. Total life cycle GHG emissions of the electric<br />

propulsion system manufacture overseas was found to be 6.67 tonnes of CO2 eq., whereas that for<br />

conventional gasoline was found to be substantially higher, 9.02 tonnes of CO2 eq. In comparison with<br />

conventional vehicles, the carbon footprint mitigation potential of using an electric drivetrain manufactured<br />

locally with Western <strong>Australian</strong> energy mix was found to be 2.35 tonnes of CO2 eq. over a course of 150,000<br />

km mileage. The amount of emission savings is comparable to that from electricity consumption of a<br />

household for about five months


Dr Wahidul Biswas<br />

Senior Lecturer, Curtin University<br />

Co Authors - Dr Waqar Ahmad, Principal Scientist, CSIRO, Mrs Deborah Engelbrecht, Ph.D Student and<br />

Research Assistant, Curtin University.<br />

Methodology development for the Integrated Spatial Technology<br />

The Clean Energy Act 2011 aims to drive the transformation of the <strong>Australian</strong> economy to a clean energy<br />

future by reducing greenhouse gas (GHG) emissions. To aid the land use sector to reduce GHG emissions, the<br />

Carbon Farming Initiative has been designed for landholders to generate and sell carbon credits. Currently<br />

limited methodologies have been developed which address these issues.<br />

This paper presents the application of Integrated Spatial Technology (IST) Framework that aims to reduce<br />

Greenhouse Gas (GHG) emissions from Western <strong>Australian</strong> grain industries by integrating <strong>Life</strong> <strong>Cycle</strong><br />

<strong>Assessment</strong> (LCA), Geographical Information Systems (GIS) and Remote Sensing (RS). The data for<br />

implementing into the project, were obtained from a current Department of Agriculture and Food Western<br />

Australia (DAFWA) project which focuses on crop sequencing in Western Australia.<br />

To delineate the project boundary and extract paddocks for this project, two satellite images were acquired<br />

and all paddock co-ordinates were registered on these. Secondly, the landholders from the paddocks which<br />

were within the satellite images were then interviewed to obtain input/output data for the LCA. Thirdly, the<br />

carbon footprints resulting from these inputs/outputs were calculated and thereafter incorporated into a GIS,<br />

giving a visual representation of the “hotspot” in the farm management practice used. Furthermore the IST<br />

aided with the identification of the maximum and minimum levels of GHG emissions across all the stages of<br />

farming from cradle-to-gate. Fourthly the farm management system, soil and climate variability and calculated<br />

GHG emissions allowed for the identification of mitigation measures that were introduced into the IST<br />

framework for future grain production across similar conditions. Finally, the IST was applied to predict the<br />

carbon footprint from paddocks surrounding those analysed.<br />

Miss Pornpimon Boonkum<br />

Doctoral student, Waseda Univeristy, Graduate School of Environment and Energy Engineering<br />

Co Authors - Dr Jitti Mungkalasiri, Researcher, National Metal and Materials Technology Center, A/Prof Hiroshi<br />

Oonoda, Assoc Prof, Waseda Univeristy, Graduate School of Environment and Energy Engineering.<br />

Impact of different farm management systems on Jatropha cultivation for biodiesel feedstock. A<br />

case study in Thailand<br />

Renewable energy has been promoted by the Thai government since 90’s, with the aim to solve and relieve<br />

the problem of fossil energy depletion. One of the key factors for the success of the promotion on bio-fuels is<br />

the potential of feedstock in terms of economic and environment. Nowadays, oil palm is a major feedstock for<br />

the biodiesel production in Thailand while Jatropha curcas L. (hear in after as Jatropha), potentially non-edible<br />

oil plant is considering as an alternative energy crop that can avoid the competition between food industries<br />

and energy sectors. Jatropha cultivation in Thailand has different agricultural practices due to the variety of


climate and soil condition. The disadvantage of JCL is the low seed yield and inconsistent of seed yield, while<br />

the advantage of JCL is the low investment and low energy for milling process.<br />

The objective of this study would like to evaluate the environmental impact of Jatropha crude oil (JCO) from 2<br />

different methods of JCL cultivation practices; conventional and managed plantation, by using the concept of<br />

<strong>Life</strong> <strong>Cycle</strong> <strong>Assessment</strong> (LCA). Data collection was done in JCL farm in the north of Thailand. The main<br />

environmental impact will be focused on Greenhouse Gas (GHG) emission and energy balance. Allocation<br />

method will be applied for allocate the impacts of the main product and co-products of JCO from this system.<br />

Dr Pip Brock<br />

Project Officer, Grain <strong>Life</strong> <strong>Cycle</strong> <strong>Assessment</strong>, NSW Department of Primary Industries<br />

Co Authors - Dr Sally Muir, NSW Department of Primary Industries, Dr Graeme Schwenke, Soil Scientist, NSW<br />

Department of Primary Industries.<br />

Identifying opportunities for reducing greenhouse gas emissions for climate change mitigation in<br />

grain production systems in NSW using <strong>Life</strong> <strong>Cycle</strong> <strong>Assessment</strong> (LCA).<br />

The Grains Research and Development Corporation has commissioned the NSW Department of Primary<br />

Industries to prepare greenhouse gas emissions profiles using LCA for specific grain production systems in New<br />

South Wales. Comparative regional studies developed during 2012 to 2015 will provide the <strong>Australian</strong> grains<br />

industry with information about emissions sources and provide data to support eco-labelling and product<br />

marketing. Potential emissions reduction strategies will be provided to the industry within the context of<br />

practical and economic opportunities. Previous LCA indicates the magnitude of possible emissions reductions<br />

in grain production systems in NSW. Nitrogen fertilisation is a major contributor to emissions. Calculated<br />

emissions from wheat in Central NSW were approximately 200 kg CO2-e/t grain comprising 30% from the<br />

production and transport of fertiliser and 26% from N2O emitted from soil after fertiliser application.<br />

Emissions from N-fertilised cereals in a field trial at Tamworth, NSW, were 251 and 242 kg CO2-e/t grain for<br />

two wheat crops in 2010 and 137 kg CO2-e/t grain for barley in 2011. Emissions from the production and<br />

transport of fertiliser and N2O emitted from soil in field trial were similar to those from wheat in Central NSW.<br />

A major opportunity exists to reduce emissions by moving towards systems which include substantial inputs of<br />

nitrogen from legume N2 fixation. At Tamworth, chickpeas provided some nitrogen for a following wheat crop<br />

grown without urea, with total emissions reduced to 98 kg CO2-e/t grain. Grain yield remained similar to ureafertilised<br />

crops but protein was reduced. Preliminary LCA comparisons will be presented of rotations involving<br />

winter cereals, sorghum and canola with added N-fertiliser or prior legume N2 fixation. Current economic<br />

data, field research on N2O emissions factors and LCA of irrigated cotton production will assist modelling of<br />

mitigation options which may be significant when implemented over large areas/volumes of production.


Dr Cecil Camilleri<br />

Manager, Sustainable Wine Programmes, The Yalumba Wine Company<br />

Growing and Making Wine in an Atmosphere of Increasing Risk - Mitigation and Adaptation to<br />

Climate Change at Yalumba<br />

The Yalumba Wine Company has developed an ethos of quality that is inclusive of environmental, economic<br />

and stakeholder stewardship. Yalumba’s sustainability story commence in 1999 when it became the first<br />

<strong>Australian</strong> wine company, and one of the first enterprises operating in the agricultural sector, to undertake a<br />

Greenhouse Challenge co-operative agreement. Since then, Yalumba has adopted a life cycle approach to<br />

continuous improvement in the management and conservation of the essential ‘elements’ that make up fine<br />

wine: earth, air, energy and water. These are the essential ‘elements’ of photosynthesis and fermentation.<br />

By adopting life cycle thinking, Yalumba is addressing mitigation and adaptation to climate change by<br />

strategically applying life cycle management and life cycle analysis to the development of business<br />

management practices that include setting aside land for conservation and carbon sequestration. Importantly,<br />

Yalumba and its people aspire to be recognised as a smart, knowledge-based, independent <strong>Australian</strong> wine<br />

company with the necessary adaptive capacity and resilience to succeed in a globalised competitive winemarket<br />

that is increasingly being impacted by the uncertainty of climate change, and where the consumer and<br />

other stakeholders are at the centre of business concern for sustainability.<br />

Therefore, Yalumba must engage its stakeholders in profit-making by allocating scarce resources amongst<br />

competing economic, environmental and social needs without compromising the life options of future<br />

generations. In the face of uncertain future scenarios, action research at Yalumba has highlighted that this can<br />

be achieved by establishing a coaching culture at the workplace that communicates and co-creates sustainable<br />

business practices that: 1. Maintains or improves economic viability; and 2. Maintains or enhances production;<br />

and 3. Minimises risk; and 4. Satisfies Yalumba’s stakeholders; and 5. Protects the biotic or abiotic<br />

environment; and 6. Makes the purchase experience a responsible activity, socially, ecologically and<br />

economically.<br />

Therefore, to deal with the vagaries of climate change, forward looking organisation mitigation should adopt<br />

workplace coaching which isa continuum based on a positive, affirmative approach that: 1. Builds on and<br />

extends the capacity of Yalumba and its People to develop skills and competencies as part of the wine firm’s<br />

commitment to sustainable winemaking. 2. Attains new knowledge and understanding as part of the process<br />

of sensemaking and sensegiving. 3. Builds and maintains effective workplace relationships.<br />

Dr Guangnan Chen<br />

Lecturer, National Centre for Engineering in Agriculture<br />

Co Author - Craig Baillie, University Southern Queensland, Sandra Eady, CSIRO.<br />

Developing farm energy inventory for life cycle assessment<br />

The sustainable development of modern industry and society has been identified as a significant national and<br />

international issue. To achieve sustainable development, the first step would be to understand and identify


where the environmental impacts and damages occur so that targeted remedy actions can be taken. <strong>Life</strong> <strong>Cycle</strong><br />

<strong>Assessment</strong> (LCA) is an ideal tool for such a purpose. It analyses and quantifies the environmental impacts of<br />

the whole process of making, using and disposing a product e.g. a cotton T-shirt. LCA has also the advantage of<br />

providing a rigorous, comprehensive, and multi-dimensional analysis of all relevant factors.<br />

A comprehensive LCA analysis would in particular have the advantage of being able to quantify the magnitude<br />

of potential environmental saving in each (environmental) category, and to avoid the pitfall of just shifting<br />

from one category to another category. In this paper, the importance of farm energy inputs and high quality<br />

data in LCA analyses is highlighted. Different approaches to building life cycle inventory, particularly the<br />

methods for allocating farm machinery inputs (on an ownership of a whole unit by the farm versus an hourly<br />

allocation based on average machine inputs) and recycling of machinery materials, are discussed. The impacts<br />

of these approaches on the accuracy of LCA models are also examined, using cotton production in Australia as<br />

an example.<br />

Mr Scott Clarkson<br />

Project Manager – CSR Innovations, CSR Building Products<br />

Co Author - Mr Jonas Bengtsson, Director, Edge Environment.<br />

Cradle to Grave <strong>Assessment</strong> and Benchmark of the CSR House<br />

CSR Building Products is investing to drive innovation within the built environment to deliver high performance<br />

building solutions to the mainstream market. The CSR House research centre, launched in November 2012 has<br />

been constructed to research building processes and perform ongoing operational research on building<br />

performance. Edge Environment was commissioned by CSR to conduct a LCA of the CSR House.<br />

This project is the first whole building assessment to use the BP LCI toolkit and to create “robust data” that will<br />

underpin CSR initiatives to communicate with, and educate industry stakeholders about the life cycle<br />

performance of CSR products. The CSR LCA tool includes 23 climate zones, selected by building activity. The<br />

environmental performance is benchmark against the Housing Industry Association reference building. The<br />

default scope of the LCA was 70 years building life, including production and transport of all major fixed<br />

building elements; construction site impacts; building products maintenance and replacement lives;<br />

operational energy and water use from fixed appliances over the life of the building; and end of life disposal.<br />

The following three functional units were used to benchmark the building impact: Cradle to end of life per<br />

whole dwelling; per m2 floor area; and per occupant. The LCI data was entered into the SimaPro LCA program<br />

and linked to the pre-existing data for the upstream feedstocks and services selected primarily from the BP LCI<br />

database and AusLCI. Energy modelling including fixed appliances was performed using AccuRate Sustainability<br />

algorithms.<br />

The life cycle inventory data was interpreted into key environmental impacts, including global warming<br />

potential and <strong>Australian</strong> ecopoint, in accordance with the BP LCI methodology. &#65532;The results and tool<br />

provided CSR with a comprehensive basis for evaluating life cycle performance during building design and<br />

construct, and going forward to underpin sustainable product development and building design<br />

communication nationwide.


Monique Cornish<br />

Senoir Associate, Net Balance<br />

Co Author - Nicole Sullivan<br />

BlueScope Steel – a new era inspired by LCA<br />

Many <strong>Australian</strong> manufacturers are facing increasing market pressure due to domestic market conditions and<br />

the high <strong>Australian</strong> dollar. As a response, BlueScope Steel has developed technology to differentiate their<br />

steel products – like ZINCALUME® and COLORBOND® steel – with a new and compelling value proposition<br />

based on sustainability.<br />

In 2013 BlueScope will launch next generation ZINCALUME® steel. For the first time in BlueScope Steel’s<br />

history, this world-leading technology will be launched with a full LCA and EPD to demonstrate the improved<br />

environmental performance and overall sustainability credentials of the product.<br />

Data collection and life cycle modelling for a system as complicated and integrated as Port Kembla Steelworks<br />

presented a number of methodological challenges. We will share some of these challenges and solutions from<br />

a practitioner perspective. The results of the LCA show a significant improvement in the footprint of next<br />

generation ZINCALUME® steel compared to last generation ZINCALUME® steel across all 18 categories<br />

assessed. The study highlights the importance of dematerialisation and resilience in the determining the<br />

footprint of building materials, and the overall sustainability of Australia’s built environment.<br />

As a result of this initial LCA there is much greater cross-functional recognition of the value of LCI and LCA<br />

within BlueScope Steel. We will share how LCI and LCA are now emerging as drivers of innovation and market<br />

leadership, as well as how they are facilitating better operational understanding and research into further<br />

manufacturing developments, including another BlueScope Steel product launch supported by LCA planned for<br />

2013.<br />

The future for LCA in BlueScope Steel is bright: we are now able to identify and envision the opportunities that<br />

LCA presents to the business. The challenge is to translate these opportunities into actions that result in<br />

further improvements in our environmental credentials.<br />

Ms Annette Cowie<br />

Director, Rural Climate Solutions, University of New England<br />

Update on the ISO Carbon Footprint standard<br />

Recognising the desire of many stakeholders for better information about the climate change impacts of<br />

products, the International Standards Organisation (ISO) agreed to develop a standard to guide the<br />

quantification and communication of the carbon footprint of products. The quantification component is based<br />

on life cycle assessment, following closely ISO 14040 and ISO 14044. The communication guidance is based on<br />

the environmental labelling standards ISO 14020, ISO 14024 and ISO 14025.


The process has met hurdles, as is it seen to have potential implications for international trade, for example,<br />

disadvantaging developing countries that have little capacity to improve their GHG-intensive energy systems.<br />

There has also been uneasiness about communication based on a single impact category.<br />

Thus the development has been a protracted exercise, taking five years from inception.<br />

The final draft did not find agreement for release as an international standard, however, there was sufficient<br />

support to release it as a Technical Specification. Thus ISO/TS 14067 Greenhouse gases — Carbon footprint of<br />

products — Requirements and guidelines for quantification and communication has been approved, and is due<br />

for imminent release.<br />

The standard encourages use of Product Category Rules, in order to increase consistency in calculation of<br />

carbon footprints for similar products produced by different organisations.<br />

The GHG emissions and removals from some sources and sinks are reported separately in addition to being<br />

included in the calculation of the carbon footprint. This applies to fossil and biogenic carbon sources and sinks,<br />

emissions and removals due to direct land use change, aircraft emissions, and non-CO2 emissions from<br />

livestock, manure and soils. The standard does not require inclusion of emissions due to indirect land use<br />

change.<br />

The climate change impacts of timing of emissions and removals has been a particular point of debate, and is<br />

an issue which has been largely neglected in LCA to date. There was no consensus on whether delayed<br />

emissions and temporary sequestration do indeed deliver a benefit. Nevertheless this was recognised as a<br />

potentially important feature for some products, and therefore it was agreed that the timing of emissions<br />

across a product’s life cycle must be documented as part of the carbon footprint. No guidance is provided on<br />

how to quantify the impacts of timing of emissions and removals.<br />

The committee that developed ISO/TS 14067 is aware of limitations with this document, and there is strong<br />

desire from some members to reconvene the committee in the near future, in order to revise the TS and work<br />

towards approval of an International Standard.<br />

Miss Kelly Cox<br />

Researcher, Boeing Research and Technology Australia<br />

<strong>Life</strong> <strong>Cycle</strong> <strong>Assessment</strong> of Jetfuel Production in Queensland: A Comparison of Three Potential<br />

Feedstocks<br />

The aim of the Queensland Sustainable Aviation Fuel Initiative is to detail the potential costs and<br />

environmental impacts or benefits that might arise if a supply chain is established to produce a realistic<br />

amount of aviation fuel for use in a commercial aviation setting, from feedstocks that are capable of being<br />

grown in Queensland. The feedstocks considered for this project include molasses from sugarcane, the oilseed<br />

plant Pongamia and autotrophic algae.<br />

This information may be used to build support for financial commitments from government or private<br />

investors to implement the modeled supply chains. Two models were developed for each feedstock, a baseline<br />

model showing the potential process flow based on published and publicly available data which incorporates<br />

the use of a digestion and cogeneration system for disposal of waste and by-products, and a variation model<br />

which removes the use of the cogeneration system and relies on the protein value of any potential co-


products. Both allocation and system expansion modeling methodologies were applied for this LCA in order to<br />

show the variation of results for each method across the three feedstocks; and while both methods are<br />

correct, the disparity between method results causes a reasonable feedstock comparison to be quite difficult.<br />

The relevant impact categories identified for this model include cumulative energy demand, Global Warming<br />

Potential (GWP), eutrophication, land and water use, and human and eco- toxicity. A Monte Carlo uncertainty<br />

analysis was performed for all data as part of the LCIA in order to define a 95% confidence interval for the<br />

results of each impact category. Results for both the baseline and variation models will be presented, with a<br />

comparison of the outcomes of the three feedstocks. These results are specific to aviation fuel in Queensland.<br />

Helene Cruypenninck<br />

<strong>Life</strong> <strong>Cycle</strong> Strategies Pty Ltd<br />

Modelling pesticide flows in agricultural <strong>Life</strong> <strong>Cycle</strong> Inventories using PESTLCI<br />

A common current practice for assessing on-farm pesticides output flows in agricultural <strong>Life</strong> <strong>Cycle</strong> Inventories<br />

(LCI) is to assume that 100% of applied pesticide active ingredient is released into soil [Nemecek 2007]. The<br />

partitioning of the chemicals into different compartments (air, surface water, groundwater) is then left to the<br />

impact assessment methods (such as USEtox [Rosenbaum 2008]) which use non-farm specific partitioning<br />

factors. PestLCI 2.0 [Dijkman 2012] models the on-farm dynamics of active ingredients flows, from the time of<br />

application up to the time they leave the farm boundaries. Taking into account farm specific climate, soil and<br />

crop characteristics, this model estimates the output flows to surface water, ground water and air for a given<br />

active ingredient. Soil being part of the technosphere, there is no active ingredient output flow to this<br />

compartment.<br />

This paper will present the successive steps required to extend the current range of application of PestLCI 2.0<br />

from European to <strong>Australian</strong> conditions. These steps include: automation of PestLCI to allow for multiple<br />

calculations and interfacing with other <strong>Life</strong> <strong>Cycle</strong> Inventory tools; identification of the most sensitive user input<br />

parameters (amongst climate, month, crop type, etc.); accessing and defining these identified parameters for<br />

Australia by selecting the appropriate geographic scale; and identification of remaining data gaps and further<br />

research needs.<br />

The PestLCI model for partitioning on farm pesticides emissions will be applied to a selection of broad acre and<br />

horticulture crops. The effect of the use of PestLCI on on-farm ecotoxicity results compared to the traditional<br />

way of dealing with pesticides in agricultural cradle-to-gate <strong>Life</strong> <strong>Cycle</strong> <strong>Assessment</strong> will be presented and<br />

discussed.<br />

Dijkman, T.J., M. Birkved and M.Z. Hauschild 2012, PestLCI 2.0: A second generation model for estimating<br />

emissions of pesticides from arable land in LCA, International Journal of <strong>Life</strong> <strong>Cycle</strong> <strong>Assessment</strong> 17: 973-986.<br />

Nemecek, T. and T. Kagi 2007, ecoinvent data version 2.0, <strong>Life</strong> <strong>Cycle</strong> Inventrories of Agriculture Production<br />

Systems. Zurich, Ecoinvent Centre.<br />

Rosenbaum, R.K., T.M. Bachmann, L.S. Gold, M.A.J. Huijbregts, O. Jolliet, R. Juraske, A. Koehler, H.F. Larsen, M.<br />

MacLeod and M. Margni 2008, USEtox—the UNEP-SETAC toxicity model: recommended characterisation<br />

factors for human toxicity and freshwater ecotoxicity in life cycle impact assessment, The International Journal<br />

of <strong>Life</strong> <strong>Cycle</strong> <strong>Assessment</strong> 13(7): 532-546.


Dr Sandra Eady<br />

Research Scientist, CSIRO<br />

Co Authors - Mr Tim Grant, <strong>Life</strong> <strong>Cycle</strong> Strategies, Mr Simon Winter, RIRDC.<br />

The business case for investment in agricultural life cycle inventory to support sustainable industry<br />

development and competitiveness in a carbon constrained global economy<br />

Over the last decade there has been a significant focus on the environmental impact of products and services<br />

across the economy. This is beginning to play out in a variety of spheres: - environmental product declarations<br />

to inform consumer choice - delivery agreements where the supplier is required to demonstrate an on-going<br />

improvement program of environmental sustainability - the likely advent of trade agreements premised on<br />

climate change mitigation efforts - realignment of insurance risk and costs to the economy.<br />

A minority of environmental impacts have a clear and immediate cost to farmers and society. Hence, the<br />

financial signals for taking action to reduce environmental impacts are muted. However, once action is<br />

required (as imposed by a supplier or a pricing mechanism) primary producers need to be able to make an<br />

objective assessment of their environmental impact so that “hot spots” in their production system can be<br />

identified, and options to reduce these impacts can be investigated. Often it is not clear which inputs or<br />

processes in the production system are contributing the largest impact, and how these impacts will vary<br />

depending on the impact category of interest. <strong>Life</strong> <strong>Cycle</strong> <strong>Assessment</strong> (LCA) is the most commonly used tool to<br />

determine the environmental impact that a product or service has, by taking into account all of the impacts<br />

from resource extraction, production, use, through to end of life disposal.<br />

However, LCA is only as good as the underlying data or <strong>Life</strong> <strong>Cycle</strong> Inventory (LCI) that is used for modelling and<br />

analysis. Country specific LCI for agricultural products is essential for <strong>Australian</strong> agriculture to undertake<br />

environmental impact studies related to food and fibre, especially where differences in management systems<br />

and regional climate, soils and vegetation significantly affect LCA results. In addition, Australia exports a large<br />

proportion of production and provision of publicly available national LCI is essential to allow our trading<br />

partners to undertake LCAs with robust cradle-to-gate inventory that reflects the country of origin. CSIRO is<br />

partnering with RIRDC and a range of industry research and development corporations on a pilot initiative to<br />

produce LCI for <strong>Australian</strong> agriculture (AusAgLCI Project). Inventory being developed for AusAgLCI is based on<br />

publicly available data on farming systems as found in grower handbooks and gross margin publications.<br />

The goal of inventory collection for AusAgLCI is to provide the underlying data to ensure <strong>Australian</strong> primary<br />

producers can readily, and objectively, demonstrate that their products are being produced in a responsible<br />

manner, in a system where environmental assessment is used to aid and drive improvements. This will assist<br />

producers to meet marketing requirements and to benchmark their production in global markets.<br />

Dr Michael Faltenbacher<br />

Principle consultant, PE INTERNATIONAL<br />

Co Authors - Mr Michael Held, Scientist, Fraunhofer Institute for Building Physics, dept. <strong>Life</strong> <strong>Cycle</strong> Engineering,<br />

Mr Michael Baumann, Scientist, Fraunhofer Institute for Building Physics, dept. <strong>Life</strong> <strong>Cycle</strong> Engineering.<br />

<strong>Assessment</strong> of the environmental impacts of E-Mobility concepts


Under the impression of current discussions of depleting resources and environmental questions, the<br />

transportation sector is aware of its responsibility and in search of alternative concepts. Especially electric<br />

vehicles are expected to have a high potential, since they reduce the dependence from fossil fuels and reduce<br />

local noise and emissions during the vehicle operation. However, besides the environmental impacts of power<br />

generation, it is also required to investigate the production and end of life phase of electric vehicle concepts<br />

and power train specific components in an early stage. To do this, the method of life cycle assessment (LCA) is<br />

a suitable tool, since it evaluates the environmental impacts of products or services from a life cycle<br />

perspective. Main goal of this project is to give a first estimate of the environmental potential different of e-<br />

vehicle concepts and to identify significant parameter and indicators.<br />

The production and use phase of different electric vehicle concepts, like battery electric vehicles (BEVs) and<br />

plug-in hybrid electric vehicles (PHEVs) are evaluated in a screening LCA. In addition, as a broader market entry<br />

of electric vehicles is expected in the next years (e.g. the national roadmap for electric mobility of the German<br />

federal government expects around one million electric vehicles on German street until the year 2020) the<br />

study investigates future scenarios to estimate the environmental potential of future concepts and<br />

developments.<br />

In a first step the scenarios investigate the environmental profile of e-mobility due to further developments of<br />

battery systems as well as the future development of the national electricity grid mix. The presentation gives<br />

an overview of the main approach and outcomes of the study, identifies the significant indicators and<br />

parameters and discusses the relevant topics and questions for future research.<br />

Mr Sebastian Gollnow<br />

LCA and Sustainability Consultant, PE Australasia<br />

Co Authors - Dr. Sven Lundie, CSR & Sustainability Strategy Consultant, PE-INTERNATIONAL, Jake McLaren, <strong>Life</strong><br />

<strong>Cycle</strong> <strong>Assessment</strong> and Design for Environment Consultant, PE Australasia.<br />

Carbon footprint of dairy production in <strong>Australian</strong><br />

This paper explores the carbon footprint of dairy production in Australia and follows the approach of ISO<br />

14044 and the dairy industry specific carbon footprinting guidelines published by the International Dairy<br />

Federation (IDF 2010). This study is one of the first carbon footprinting studies for dairy production that has<br />

been conducted on a national level and is also one of the first to follow the IDF (2010) carbon footprinting<br />

guidelines. An industry cross section of primary data has been analysed from 139 farms across the country.<br />

The scope of the system covers all inputs and outputs cradle to farm gate for the year 2009/10. A web-based<br />

software platform has been developed as part of the project to enable auditable data collection and analysis.<br />

Results for production of average <strong>Australian</strong> raw milk at farm gate show the average carbon footprint for the<br />

year 2009/10 is 1.11 (-+0.22) kg CO2 e. / kg fat and protein corrected milk. More than half of the emissions are<br />

associated with enteric fermentation (57%), 8% are associated with manure management and 10% with<br />

manure excreted onto pasture. Fertiliser and energy inputs are each associated with 8% and purchased feed<br />

are associated with 9%.<br />

Further analysis of the feed systems, productivity, concentrate intake and individual farms indicated: GHG<br />

emissions differ substantially between farms, reduction potentials can best be derived at an individual farm


level. Each participating dairy farmer has received an interpretation of their own farm input with respect to the<br />

overall project results. Within the scope of the project an innovative software platform for data collection and<br />

analysis has been developed to overcome challenges associated with handling of extensive and complex<br />

primary data. Further methodological challenges associated with the allocation approaches between milk and<br />

meat at farm gate was assessed.<br />

Mr Tim Grant<br />

Director, <strong>Life</strong> <strong>Cycle</strong> Strategies<br />

New AUSLCI data – Making LCA easier<br />

Undertaking <strong>Life</strong> <strong>Cycle</strong> <strong>Assessment</strong> is a much a exercise in time management as it is a scientific investigation.<br />

Deciding what data to focus on, which impacts and flows to include in the assessment and how to interpret the<br />

robustness of results are all decision which a practitioner needs to make in the process of an LCA. Assessing<br />

the quality of the background data is time consuming and uncertainty in the background data can undermine<br />

the results of an LCA study.<br />

The new AusLCI data being developed by <strong>ALCAS</strong> will significantly reduce the time and uncertainty for LCA’s<br />

being undertaken in Australia and on <strong>Australian</strong> production systems. The guidelines for data collection provide<br />

a common framework for the collection and modelling fully connected life cycle inventory covering a broad<br />

range of flows which can support detail life cycle impact assessment and enable transparent interpretation of<br />

the source of impacts.<br />

For foreground data development in LCA many of the AusLCI modules are parameterised to allow the average<br />

or typical data in AusLCI to be easily customised specific situations. This includes electricity, transport, and<br />

agricultural inventories.<br />

The presentation will highlight the features of the new AusLCI data and how to get the most from using it.<br />

Mr Tim Grant<br />

Director, <strong>Life</strong> <strong>Cycle</strong> Strategies<br />

Economic and environmental analysis of Algae fuel systems<br />

According to market research organisations, algae biomass is poised for explosive growth in the next ten years.<br />

In particular there is interest in Algae providing alternative biomass source to traditional crop based biofuels<br />

which have caused a series of negative environmental outcomes due to land use and crop production impacts.<br />

Currently the environmental impacts of biomass from Algae production are highly variable depending on the<br />

location of production, source of inputs of land water carbon and nutrients and the technologies used for<br />

harvesting and conversion to an energy source.<br />

This paper explores the drivers of these impacts based on work undertaken in Australia looking at the use of<br />

Algae ponds within waste water treatment facilities and in saline and freshwater production systems.


Unlike the economic factors which are dominated by capital equipment, the life cycle impacts are dominated<br />

by harvesting, thickening and processing stages due to chemical and energy use. The recycling of nutrients<br />

and production of co-products however lead to significant environmental gains. In particular energy coproducts<br />

are particularly valuable.<br />

Dr Anthony Halog<br />

Lecturer, University of Queensland<br />

Co Author - Mr. Nana Awuah Bortsie-Aryee, PhD student, School of Forest Resources, University of Maine, USA.<br />

Attributional <strong>Life</strong> <strong>Cycle</strong> <strong>Assessment</strong> of a Forest Derived “Drop-in” Biofuels<br />

The United States Department of Energy (DOE) has been championing efforts to ensure that the next<br />

generation of biofuels is regarded as “drop-in” biofuels. “Drop-in” biofuels are infrastructure-compatible –<br />

they can either be used directly or blended with their petroleum-derived fuels. This study initially evaluated<br />

the environmental life cycle impacts across the supply chain of a new drop-in biofuel, developed by the<br />

University of Maine (UMaine).<br />

The study made use of primary data for the biomass conversion stage and utilized Maine’s regional data as<br />

well as generic data developed in the United States. With respect to water use, it is clear from our analysis that<br />

the biomass production phase requires a significant amount of water intake to enable the biomass to grow to<br />

maturity. A water intake of 0.120 tonnes shows the importance of finding a suitable source of water to use in<br />

the first phase of the life cycle and not relying on potable water for the growth of the biomass. Though the<br />

global warming potential associated with carbon dioxide is very high, it should be understood that growing<br />

biomass actually helps reduce the atmospheric carbon dioxide in conjunction with photosynthesis.<br />

As compared to fossil fuel derived oils, the UMaine TDO oil could perform better in terms of GHG emissions.<br />

The internal physiological processes of the biomass during the biomass production phase reduce the carbon<br />

dioxide emitted during the complete life cycle phase by using it to further the growth of the trees.<br />

Mr Richard Haynes<br />

Engineer, eTool<br />

LCA of the built environment - the client’s perspective<br />

As LCA practitioners we’re all guilty of becoming so obsessed with the science that we’re embedded in at times<br />

that we forget about why and who we are doing the work for. One of the most important aspects of what we<br />

do is to encourage, influence and motivate the rest of the world to use LCA to improve how we create things.<br />

The best way to do this is to understand who the real client is (in construction it’s the developer, builder,<br />

architect or the actual end owner or occupant), what motivates them and how we can work to increase their<br />

motivation to get the best result for the project. The second most important thing is to ensure you have the<br />

tools and services that can deliver the best results. eTool has always started with the client and worked back<br />

from there. The following paper explores this process over a number of case studies ranging from residential


and commercial to infrastructure projects. It highlights how you can get the best results for the client and the<br />

environment.<br />

Mr Nigel Howard<br />

Principal, Clarity Environment<br />

Practical LCA for Building Design - ENVEST Au<br />

This paper presents the key features of the ENVEST LCA based building design tool and how it reconciles the<br />

complexity of whole building LCA, working from the limited information available at inception and<br />

communicating the complex and often perverse effects of design decisions for environmental impacts and<br />

financial costs. Building design teams may include Architects, Structural and Services Engineers, Cost<br />

Consultants, Landscape Architects, Environmental Consultants, each using specialist software to aid design<br />

development. Some tools share common data through the Building Information Modelling (BIM) protocol.<br />

ENVEST is unique because: • ENVESTworks from design inception where the biggest decisions are made. At<br />

inception, just 4 key pieces of information from the client brief dominate thinking – site location, size of<br />

building, mix of uses and budget and pencil are the main tools used.<br />

In about an hour of furious collective creative effort, massing and basic shape/dimensions, position on the site,<br />

orientation, glazing, rooflights/atria basic appearance i.e wall specification are all decided. Perhaps 90% of a<br />

buildings’ life cycle performance is locked in in this first design hour - the next weeks and months of design<br />

time will detail the building making relatively trivial improvements in performance. • ENVEST is a full LCA<br />

design tool that simultaneously and instantly reveals the complex and often perverse outcomes of decisions<br />

that affect materials and operational energy, water and waste. • ENVEST uses and complies with the BP LCI<br />

methodologies, data and Protocol. • ENVEST provides a starting point BIM file for all design team members •<br />

ENVEST simultaneously calculates financial cost to build and operate over the life, revealing cost trade-offs as<br />

well as environmental ones • Users can select from 12 environmental impact measures (include greenhouse<br />

gas emissions) and a composite <strong>Australian</strong> ecopoint indicator (based on the BP LCI 11 City weightings surveys).<br />

Ms Delwyn Jones<br />

Director Sustainability <strong>Assessment</strong>, The Evah Institute<br />

Deriving Negative and Net Positive LCA Metrics<br />

Making cities more liveable and sustainable is key to planning, analysis and reporting. Initiatives to visualize<br />

greener supply chains are constrained by current LCA philosophy and metrics. In practice LCA analysis typically<br />

focuses mostly or only on negative impacts. It begs many questions of how can we imagine or create<br />

restorative services, markets and cities if we do not measure net positive benefits needed for their<br />

development.<br />

While assessing greenhouse gas emissions why not report Oxygen generation? When assessing biodiversity<br />

loss why does LCA not typically asses growth in habitat richness? The paper seeks to answer these questions.


<strong>Life</strong> <strong>Cycle</strong> Benefit Analysis (LCBA) is designed to quantify e.g. habitat richness, oxygen generation and resource<br />

regeneration capacity of Eco-positive products, systems and urban and infrastructure development. The<br />

presentation proposes definitive algorithms to combine impacts and benefits at a local to global level on top of<br />

existing algorithms that address only negative metrics.<br />

Ms Yumi Kobayashi<br />

Student, University of New South Wales<br />

Co Authors - Greg M. Peters, Chalmers University of Technology, Gothenburg, Sweden & University of New<br />

South Wales, Stuart J. Khan, University of New South Wales<br />

Towards harmonised use of DALYs in <strong>Life</strong> <strong>Cycle</strong> <strong>Assessment</strong> and Quantitative Risk <strong>Assessment</strong><br />

The hybridisation of <strong>Life</strong> <strong>Cycle</strong> <strong>Assessment</strong> (LCA) and Quantitative Risk Analysis (QRA) has been recognised as a<br />

beneficial objective. The areas of their focus are quite distinct, but the common use of Disability Adjusted <strong>Life</strong><br />

Years (DALYs) for human burden of disease (BoD) impacts appears advantageous.<br />

However, since various assumptions are unavoidable in DALY value derivations, finding a consistent set of<br />

assumptions is essential for compatibility. The current state of use of DALYs in LCA was examined through a<br />

comprehensive literature review by contrasting three well established LCA methodologies to identify the<br />

assumptions involved. Further research is recommended to evaluate the feasibility of establishing a global<br />

consensus on the underlying assumptions for future LCA and QRA hybridisation.<br />

Dr Paul Koltun<br />

Senoir Research/Scientist, CSIRO<br />

Co Author - Dr. Ambavalar Tharumarajah, Principal Research/Scientist, CSIRO, Dr. Terry Norgate, Senior<br />

Research Ingineer, CSIRO.<br />

<strong>Life</strong> <strong>Cycle</strong> <strong>Assessment</strong> of the New Generation Nuclear power plant for <strong>Australian</strong> Conditions<br />

This study describes a life cycle assessment of a generation IV nuclear power plant based on a high<br />

temperature helium cooled reactor and gas turbine technology with modular design (GT-MHR) taking into<br />

account all phases of the nuclear power plant: pre-construction (design and equipment fabrication),<br />

construction, operation, decommissioning and waste disposal (spent fuel, radioactive and non-radioactive<br />

waste). The method adopted for the study was a desk-top hybrid LCA analysis.<br />

The analysis of each phase of the life cycle under consideration wherever possible was done on the basis of<br />

process chain analysis (PCA), using averaged available published data. Where detailed data were not available,<br />

the analysis of Input/Output (I/O) databases was employed. All inventory data used to calculate environmental<br />

impacts (greenhouse gas (GHG) emissions and energy intensity) as well as all assumptions made in the study<br />

are presented in the paper.<br />

The overall greenhouse gas footprint of nuclear power was estimated to be about 9.6g CO2 eq/kW with<br />

current uranium ore grade. The study also investigated other sustainability aspects of nuclear power in


addition to environmental impacts, namely, social impacts (biodiversity impact, health and safety,<br />

employment.) and economic impacts (cost of electricity), and these are discussed in the report. <strong>Australian</strong><br />

energy demands, which are largely met by fossil fuels, keep growing along with the associated greenhouse gas<br />

emissions. Electricity production from nuclear power could potentially be part of the solution to reduce these<br />

greenhouse gas emissions. This study provides valuable information which can contribute to the ongoing<br />

debate about the possible future deployment of nuclear power generation in Australia.<br />

Mr Joe Lane<br />

Research Scientist, University of Queensland<br />

Co Author - A/Prof Tommy Wiedmann, University of New South Wales, Prof Manfred Lenzen, Professor of<br />

Sustainability Research, University of Sydney.<br />

New capability for hybrid input-output life-cycle assessment – the Industrial Ecology Virtual<br />

Laboratory<br />

As pressure grows on Australia’s export industries to provide robust and comprehensive environmental<br />

information to support product evaluations, it is expected that life-cycle inventory data collection efforts in<br />

Australia will intensify. For LCA practitioners to meet this challenge, they will need access to robust and<br />

efficient databases and data estimation techniques. Hybrid input-output (IO) life cycle assessment (hybrid LCA)<br />

is an advanced technique for assessing the sustainability of processes, products or entities. Hybrid LCA utilises<br />

the strengths of both process- and IO-based inventory data; enabling the evaluation of multiple environmental<br />

impacts at both a high level of detail, and a high level of completeness.<br />

Doing so can improve the quality and reliability of information provided for applications such as supply chain<br />

analysis, eco-labelling of products, corporate reporting, policy formation, and infrastructure selection.<br />

Combining detailed process-specific data with an input-output (IO) framework is typically seen as a labour- and<br />

cost-intensive exercise. Disparate economic and environmental data need to be collated and aligned at a fine<br />

level of detail. In the <strong>Australian</strong> context, the difficulties are exaggerated by the lack of integrated collections of<br />

economy-wide environmental interventions, and the low sectoral and spatial resolution of ABS IO tables.<br />

The Industrial Ecology Virtual Laboratory (IE-VL) is a novel approach to overcoming the challenges of data<br />

compilation and analysis for hybrid LCA. The IE-VL will create and automatically update a multi-region inputoutput<br />

framework, linking environmental interventions with financial tables at a high level of spatial (substate)<br />

and industry (~500 sectors) disaggregation. It will be housed on the <strong>Australian</strong> National Research Cloud,<br />

making it easily accessible to the research community for hybrid LCA projects.<br />

This paper will outline the process, strengths and constraints in using the IO-VL system. We will demonstrate<br />

how the IO-VL maximises the use of automation and pre-defined data feeds, in order to minimise manual<br />

manipulation error, ensure repeatability, and provide a tool that can be updated over the long term. The<br />

output capabilities of the IO-VL will be demonstrated through application of a case study.


Dr Mark Lieffering<br />

Senior Scientist, AgResearch Ltd.<br />

Co Author – Dr Stewart Ledgard, Senior Scientist, AgResearch, Mr Mark Boyes, Research Associate, AgResearch.<br />

The GHG footprint of New Zealand manufacturing beef: the importance of allocation and other<br />

methodology factors<br />

A recent study calculated that the GHG footprint of generic beef exported from New Zealand was 2.2 kg CO2-e<br />

per 100 g meat portion; on-farm enteric methane production and nitrous oxide from excreta contributed<br />

about 80% of this total. The footprint was calculated using the weighted average on-farm emissions per kg<br />

live-weight for all cattle (i.e. animals from all the traditional beef systems, as well as cull dairy cows) and<br />

assumed a carcass contained a mix of prime and other cuts as well as the meat used for manufacturing grade<br />

beef. A large proportion of New Zealand exported beef is manufacturing grade beef, with the biggest volume<br />

going to the U.S.A. Manufacturing beef is made predominantly from culled dairy cows, with varying<br />

proportions of bull beef and other cattle types and cuts contributing to the mix.<br />

In this paper we calculate the GHG footprint of manufacturing beef made only from culled dairy cows; we<br />

assumed a live-weight meat yield of 30% and that the carcass produced no prime cuts. We first explored the<br />

effect that allocation between meat and milk had on on-farm GHG emissions: these ranged from 1.3 kg CO2-e<br />

per 100 g meat using biophysical allocation to between 1.0 and 0.6 kg CO2-e per 100 g meat for when<br />

economic allocation was used and the meat value was varied from 10 to 6% respectively. Adding in processing,<br />

transport and consumption emissions means that, depending on the allocation methodology used, the whole<br />

GHG footprint of manufacturing beef from New Zealand culled dairy cows consumed in the U.S.A. can range<br />

from 0.8 to 1.5 kg CO2-e per 100 g meat. These results are comparable to recently published GHG footprints of<br />

chicken and pork grown and consumed in the U.S.A. of 0.7 and 1.2 kg CO2-e per 100 g meat respectively.<br />

Mr Gonzalo Mata<br />

Scientist, CSIRO<br />

Co Authors - Ms Helene Cruypenninck, <strong>Life</strong>cycle Strategies Pty Ltd, Dr Sandra Eady, Research Scientist, CSIRO.<br />

Steps to Continuous Improvement Pathway to best practice LCA in developing the AusAgLCI<br />

Inventory<br />

National <strong>Life</strong> <strong>Cycle</strong> Inventory (LCI) for agricultural products is essential for enabling environmental impact<br />

studies related to food and fibre. This is particularly the case for agricultural products where differences in<br />

management systems and regional climate, soils and vegetation significantly affect <strong>Life</strong> <strong>Cycle</strong> <strong>Assessment</strong> (LCA)<br />

results. For counties like Australia, which export a large proportion of production, provision of national LCI<br />

with regional differentiation gives public access to inventory for cradle-to-farm gate, allowing LCAs to be<br />

completed with robust inventory that reflects the country and region of origin.<br />

This paper examines the process of moving from generic inventory found in common published LCI to more<br />

highly specified inventory that takes into account regional and production system specific inputs and<br />

environmental flows. The steps and tools to enable this transition are presented and discussed based on case<br />

studies from wheat production systems across Australia. These cover the use of agro-ecological classifications


to define production regions, land use maps to define spatial distribution of production systems within<br />

regions, product gross margins to define system inputs and timing of activities, and GIS data to populate<br />

models for pesticide and nutrient fate modelling and farm energy inputs.<br />

Mr Andrew D Moore<br />

Senior Consultant, PE International<br />

Co Authors - Dr Barbara Nebel, Managing Director, PE International, Ms Sheryl Chaffer, Development Manager,<br />

Cedar Woods Properties Limited.<br />

How sustainable are sustainability features on a residential building?<br />

A life cycle assessment (LCA) and life cycle costing (LCC) study of a typical Western <strong>Australian</strong> house was<br />

conducted for Cedar Woods and the WA Department of Housing by PE International in 2009. This original<br />

study provided baseline information to which the environmental performance of sustainability features could<br />

be compared.<br />

This study addresses the question: How sustainable are sustainability packages on a residential building, on the<br />

example of a Western <strong>Australian</strong> house? Four sustainability packages were investigated as part of the study;<br />

solar photovoltaic systems, rainwater tanks, solar hot water systems, and insulation. Each sustainability<br />

package was modelled to include the whole life cycle from raw material extraction, production, transport, use,<br />

and disposal at the end of life. Several variations of each sustainability package were investigated to ensure<br />

that the environmental benefits and impacts for each package were explored in detail (for example different<br />

sizes and types of solar system, types of rainwater tanks, efficiency of rainwater pumps, orientation aspect of<br />

solar hot water system, type of insulation). The results were presented in comparison with the baseline results<br />

that were established in the original study.<br />

The study demonstrated that the sustainability packages can lead to significant reductions in the<br />

environmental impacts of the house over its whole life cycle. The solar photovoltaic systems had the largest<br />

increase in environmental impact associated with their construction but also the greatest reduction in impacts<br />

during the use phase. The rainwater tank systems investigated can reduce the consumption of mains water<br />

without adding significantly to each of the impact categories investigated, depending on the specifications of<br />

the pump. Solar hot water systems can lead to reductions in environmental impact categories even in<br />

comparison to gas storage hot water systems. Insulation also reduces the contribution to all impact categories<br />

regardless of the type of insulation chosen.<br />

Mr Aidan Mullan<br />

Sustainability and Lean Manager, Interface<br />

Co Author - Ms Connie Hensler, Director Corporate LCA Programs, Interface, , .<br />

Effectively Communicating LCA Results Internally and Externally<br />

Effectively translating the complex results of a LCA into understandable and actionable information is<br />

challenging, and should be presented in a way that supports the overall decision making process. The balance


etween the presentation of detailed data and general conclusions can influence how the results are<br />

understood and used. For internal communications, choosing the right graphic is crucial to presenting detailed<br />

data and properly informing the audience. For example, radar graphs displaying multiple impacts can<br />

effectively show relative results between scenarios at a glance, but can also misrepresent the data if not<br />

carefully explained. A combination bubble graph can show normalized data while keeping raw data visible to<br />

give both detail and perspective. A traditional bar graph often thought of as old fashioned or boring, is<br />

sometimes still the most effective way to tell the story. This presentation will provide examples from actual<br />

LCA studies, and will show how presenting detailed data using different graphics can drive various conclusions.<br />

Externally communicating LCAs to provide high-level data and general conclusions of the environmentally<br />

related impacts is a separate challenge.<br />

The publication of critically reviewed studies is the most thorough method for communications; however the<br />

audience for that level of detail is limited. This presentation will show examples of LCA results in marketing<br />

collateral, as well as how the incorporation of LCA results into an ISO 14025 Environmental Product<br />

Declaration (EPD) allows for external communication to a larger audience without sacrificing the rigor of third<br />

party verification.<br />

Mr Aidan Mullan<br />

Sustainability and Lean Manager, Interface<br />

Co Author - Ms Connie Hensler, Director corporate LCA Programs, Interface.<br />

Use of an LCA Study in the Development and registration of an EPD<br />

An Environmental Product Declaration (EPD) is an ISO type III ecolabel requiring life cycle assessment and third<br />

party verification. While EPDs are being adopted in Europe, so far they have little traction in Australia or the<br />

US. Interface is the first carpet manufacturer in Australia to have registered EPDs for its products. EPDs follow<br />

a credible, verifiable process in their development. Companies must have a commitment to full disclosure of<br />

what is usually confidential information about how products are made. In addition to this ingredient<br />

information, companies must perform a life cycle assessment pursuant to ISO 14040 standards with goal and<br />

scope defined by the Product Category Rules (PCR). From this information, an Environmental Product<br />

Declaration is developed, pursuant to ISO 14025 standards. Interface’s first verified and registered EPD (US<br />

market) was for a modular carpet. The PCR was adopted from the IBU (Institut fur Bauen and Umwelt) PCR –<br />

Floor Coverings, Environmental Product Declarations Harmonized Rules for Textile, Laminate and Resilient<br />

Floor coverings, 2008.<br />

The LCA study and the EPD were verified by Five Winds International and the EDP was subsequently registered<br />

with The Green Standard. The process of developing an EPD is extensive and the adoption of EPDs as a<br />

decision making tools in the US is uncertain. The first companies to invest in EPD take a risk in exposing<br />

proprietary information about their products, but hopefully will reap the rewards of the position of<br />

environmental leadership. The value of an EPD beyond demonstrated leadership will depend on the<br />

acceptance of EPDs as a common method for environmental disclosure and guidance for purchasing decisions.<br />

When there’s only one EPD out there, there’s nothing for comparison. When it is commonly available on<br />

products, comparisons can be made to guide purchasing decisions and to assist in understanding the<br />

environmental footprint of larger systems. A trend in Europe is use of EPDs for construction products to<br />

measure the environmental impact of entire buildings. While here in the US, there is less support, but the


transparency made possible with EPDs should make it the standard environmental comparisons between<br />

products<br />

Dr Barbara Nebel<br />

Managing Director, PE INTERNATIONAL<br />

Co Authors - Mr David Drysdale, Consultant, PE Australasia, Mr Ian McGill, Engineering Specialist, Fisher and<br />

Paykel Appliances.<br />

Comparative Analysis of the Use of LCA and Hot Spot Analysis to steer the design of sustainable<br />

refrigerators and sustainability standards for refrigerators<br />

This paper explores the recent use of LCA by Fisher and Paykel Appliances (FPA) and parallel industry activity to<br />

develop a sustainability standard for household refrigerators in a joint effort by the Association of Home<br />

Appliance Manufacturers (AHAM) in the United States, Canadian Standards Association (CSA) and<br />

Underwriters Laboratories Environment (ULe) for North America. During 2011-12 Fisher and Paykel Appliances<br />

conducted an LCA study of three kitchen appliances to inform and steer FPA’s environmental strategy and to<br />

provide an internal benchmark for future product improvement.<br />

The study was conducted by PE INTERNATIONAL. While FPA developed its LCA study, PE was involved in the<br />

development of the AHAM Sustainability Standard for Household Refrigeration Appliances (AHAM 7001-<br />

2012/CSA SPE 7001-2012/UL 7001) which was published in June 2012. The approach for the development of<br />

this standard was to use hot spot analysis as an effective initial step in elucidating the significant<br />

environmental life cycle impacts of refrigeration appliances, as well as a means to balance these impacts with<br />

stakeholder concerns.<br />

These life cycle impacts or “hot spots” – are the pre-cursor to the attributes within the standard. This paper<br />

reports the results of the FPA refrigerator LCA, an analysis of the hotspots identified from this study, and a<br />

comparison with the hot spot analysis conducted during the development of the AHAM refrigerator standard.<br />

The results of the refrigerator hot spots identified by the FPA LCA closely reflect the hotspots identified during<br />

the development of the AHAM standard. The refrigerator hotspots are not centred on a single attribute (e.g.<br />

energy efficiency) but instead include multiple attributes including: materials, energy consumption during use,<br />

manufacturing and operations, product performance, and end-of-life management.<br />

Dr Barbara Nebel<br />

Managing Director, PE INTERNATIONAL<br />

Co Author - Ms Carina Svensson, Programme manager, Swedish Standards Institute.<br />

Trade Promotion through Standardisation in the South and South East (SESA) regions based on the<br />

Carbon Footprinting Standard<br />

Today, many retailers and consumers on the global markets demand that products and services are produced<br />

according to international standards. International standards can therefore function as a supporting tool for<br />

trade, sustainable development and be a crucial factor in order to get access to global markets. During the


development of the ISO standard 14067 for product carbon footprinting it became very clear that developing<br />

countries are concerned about the standard being used as a barrier to trade.<br />

This project addresses this issue and aims to assist developing countries in South and South East Asia through<br />

increased access to markets by local and regional producers by implementing the standard as a tool to support<br />

trade. Another overall goal is to contribute to greenhouse gas mitigation activities within the exporting<br />

sectors.<br />

The project is managed by the Swedish Standards Institute (SIS) and funded through Swedish International<br />

Development Cooperation Agency (Sida). Pilot studies in the following countries on different products will be<br />

developed: Indonesia (hotel stay), Pakistan (electric fans), Bangladesh (plastic products), Nepal (tea), Vietnam<br />

(rubber), Cambodia (rice), Laos (coffee) and Sri Lanka (rubber). By involving local chambers of commerce,<br />

relevant associations, national standardisation bodies as well as companies, the pilot studies will be used to<br />

transfer knowledge in the region and sectors. Communication of the learning process as well as the<br />

development of guidelines will enable other companies in the sector to undertake carbon footprinting.<br />

This paper will present early findings and the approach of involving industry in the implementation of the<br />

standard as a tool to support trade.<br />

Dr Barbara Nebel<br />

Managing Director, PE INTERNATIONAL<br />

Co Author - Mr Alistair Robertson, Managing Director, WE-EF LIGHTING Pty Ltd.<br />

<strong>Life</strong> cycle assessment for street lighting, including an example of an Environmental Product<br />

Declaration<br />

The designer and manufacturer of luminaires and lighting systems ‘WE-EF LIGHTING’ is using <strong>Life</strong> <strong>Cycle</strong><br />

<strong>Assessment</strong> to develop its commitment to environmental and resource protection. Initiated by the <strong>Australian</strong><br />

arm of the business, a full LCA was undertaken, covering the manufacturing, installation, operation and<br />

recycling. The product in question, coded VFL540, sits within the LED area and street lighting family of<br />

luminaire’s. Energy use and emissions during the operation of the luminaires were assessed based on<br />

representative streets in a range of locations. This inclusion of the energy mix, allows WE-EF to use the results<br />

across a range of markets, in particular the United Sates, South East Asia and Australasia; clients across the<br />

globe can now be provided with meaningful data for their particular location. The full evaluation was<br />

completed with Environmental Product Declarations (EPD) pursuant to ISO 14025. The programme not only<br />

allows the direct and integrated comparison of lighting solutions in terms of the environmental cost, it also<br />

provides WE-EF with valuable data to effect environmentally appropriate improvements to the product design<br />

and the production process. The functional unit of the study was 1 kilometre of street lighting designed to the<br />

appropriate standards and with an operational life of twenty years.<br />

The LCA study used the ‘cradle to grave’ principle and made certain conservative assumptions, the life of the<br />

LED’s mounted on printed circuit boards and the electronic controllers for example was assumed to be 50,000<br />

hours meaning an operational life of 13.7 years. The findings highlight that installation and operation are the<br />

life cycle stages that most influence the results. This in turn points to the importance of high performance<br />

products capable of reducing the quantity employed and the energy consumed.


Dr Caroline Noller<br />

Chief executive officer, The footprint company<br />

Co Author - Ms Hilary Beckmann, Sustainability Manager Property, Macquarie University.<br />

Application of ecological footprint to building development and sustainability strategy.<br />

The Ecological Footprint is a simple and elegant method for quantifying the impact of human consumption of<br />

the planet's biological resources. Developed in the 1990's it has been applied to sustainability policy<br />

development at the country, region and personal level with reasonable success.<br />

This paper will describe the adaption of the Ecological Footprint to building development and planning and<br />

demonstrate through case study, the strengths and weaknesses in relation to building sustainability<br />

assessment.<br />

It will also highlight the gap which exists between current green rating best practice and sustainable built form<br />

in the context of resource constraint. The use of the method to improve cost benefit evaluation of<br />

sustainability features will also be discussed.<br />

Mr Chris Nunn<br />

Sustainability Leader, Norman Disney & Young<br />

Embodied carbon footprinting and life cycle assessment to inform materials selection for 6<br />

underground stations for the Crossrail project in London<br />

This presentation will outline the method used and results of embodied carbon footprinting calculations and<br />

life cycle assessment evaluations of approximately 30 key materials being considered for as architectural<br />

components of 6 new underground train stations in London as part of the Crossrail project. Crossrail is a major<br />

new £16 billion railway infrastructure project that will cross London. It will link towns to the east and west of<br />

London with Heathrow Airport, the West End in central London and the Canary Wharf business district in East<br />

London. Our sustainability consultancy work involved liaising with Crossrail to set priorities and agree a process<br />

for sustainability evaluation of the underground station design, communicating sustainability requirements to<br />

architects, engineers, cost planners and industrial designers, coordinating inputs toward BREEAM certification,<br />

producing and issuing supplier sustainability questionnaires, interviewing suppliers, evaluating supplier<br />

responses and component options using a scoring matrix, and making recommendations about the most<br />

sustainable architectural components for the: floor; walls; ceiling; fixtures; lifts & escalators; communication<br />

systems; signage; and lighting.<br />

This evaluation involved and life cycle evaluation to compare the products being considered, taking into<br />

account the following factors: BRE Green Guide to Specification score; materials intensity; operational carbon<br />

emissions; embodied carbon; recycled content; toxic or hazardous materials; wastage rate; volatile organic<br />

compounds; service life expectations; maintainability considerations; and end of life reuse or disposal options.<br />

The presentation will provide an overview of the method used and sources of data relied on to compare the<br />

products against one another, and highlight the results of the analysis.


Miss Aurélie Perrin<br />

PhD student, Cirad<br />

Co Authors - Dr Claudine Basset-Mens, Researcher, Cirad, Prof Benoit Gabrielle, Professor, AgroParisTech.<br />

The use of a mechanistic model to estimate the emissions of reactive Nitrogen for the <strong>Life</strong>-<strong>Cycle</strong><br />

<strong>Assessment</strong> of Tomato production in Benin, West Africa<br />

Field emissions and more specifically of reactive nitrogen (Nr) compounds bear a large contribution to the<br />

environmental impacts of agricultural products. In the life-cycle assessment (LCA) of horticultural products, the<br />

methods currently used to estimate Nr emissions appeared unsuitable due to inconsistencies between their<br />

validity domain (annual crops in temperate regions) and the diversity of cropping systems encountered.<br />

The use of mechanistic models represents a promising avenue for better estimating Nr emission in a context of<br />

data scarcity such as horticultural production systems in the Tropics. Here, we compared the LCA results of<br />

tomato production using first the usual methods (ex. IPCC) and then a mechanistic crop model to estimate Nr<br />

emissions. We assessed 12 tomato cropping systems in Benin involving a variety of soils and agricultural<br />

practices. The crop model STICS simulates the main processes underlying Nr emissions: ammonia volatilization,<br />

nitrification, denitrification, and nitrate leaching, as a function of fertilizer input rates and environmental<br />

conditions.<br />

The resulting Nr emissions varied across cropping systems, both in terms of quantity and Nr forms (NH4, N2O<br />

and NO3). Compared to the usual methods for Nr emissions, the model-based LCA results differed in terms of<br />

impacts and contributions of emissions. As measurements of Nr emissions are resource-consuming, this<br />

modeling approach provides a good understanding of key factors responsible for their variations. Future work<br />

involves the implementation of a statistical experiment to quantify the range of potential variations due to<br />

these factors and assess the uncertainties due to missing data.<br />

In addition, the nitrogen balance approach from the STICS model led to a consistent estimation of the three<br />

main Nr emissions. This lance approach already used in European contexts brought perspectives for a<br />

generalized method to set adapted Nr emission factors for horticultural products in the Tropics.<br />

Miss Hannele Pulkkinen<br />

Research Scientist, Agrifood Research Finland, MTT<br />

Co Authors - Miss Hanna Hhartikainen, Research Scientist, Agrifood Research Finland, MTT, Mr Juha-Matti<br />

Katajajuuri, Research Scientist, Agrifood Research Finland, MTT.<br />

Consumer attitudes and desires towards carbon footprints and labels of food products – A Finnish<br />

consumer study<br />

The climate impacts of production and consumption of food are significant. In Finland around 25 % of climate<br />

impacts of private consumption originate from the production and consumption of food, including household<br />

food preparation, food preservation, journeys to shops and meal services. Communication of climate impacts<br />

for food products is highlighted by there being no great reductions made solely by adapting low carbon<br />

technology. Carbon labeling of food products is one significant way of communicating the climate impacts of


food. In fact, thus far six Finnish food companies include carbon labels on their product packages. However,<br />

there is lack of knowledge about how consumers perceive carbon labelling. In the Climate Communication 2<br />

(2011-2013) project Finnish consumers perception about carbon footprinting and information needs were<br />

studied.<br />

The study consisted of 5 semi-structured focus groups and one online-survey with over 1000 respondents.<br />

Both the focus groups and online-survey showed that the product carbon footprint -term is familiar to many<br />

Finnish consumers. Nevertheless, the term is generally misunderstood. Finnish consumers describe product<br />

carbon footprint either too broadly (e.g. total environmental load) or too narrowly (e.g. energy use).<br />

Furthermore, terms “climate impact” and “global warming” are seldom spontaneously related to carbon<br />

footprint.<br />

There are positive attitudes towards communicating product carbon footprints, though, but the information<br />

on product carbon footprints can become important purchasing criteria only when other key criteria, such as<br />

price and taste, are satisfied. In other words, carbon label could have a positive impact on Finnish consumers’<br />

purchase decisions only when the choice is to be made between two otherwise equal food products.<br />

Additionally, there are divergent desires for type and form of the information on product carbon footprints<br />

e.g. on carbon label designs. These consumer information desires will be discussed further in the presentation.<br />

Miss Hannele Pulkkinen<br />

Research Scientist, MTT Agrifood Research Finland<br />

Co Authors - Mr Juha-Matti Katajajuuri, Research Area Manager, MTT Agrifood Research Finland, Miss Hanna<br />

Hartikainen, Research Scientist, MTT Agrifood Research Finland.<br />

Co-operation within food industry - disclosing carbon footprints in a meaningful way<br />

<strong>Life</strong> cycle thinking is spreading among companies around the world. Growing efforts to mitigate climate<br />

change and development of life cycle assessment methodologies have pushed and enabled also food sector to<br />

act. In Finland national carbon footprint methdology for food sector has been developed and the industry has<br />

been brought together to discuss on common communication of product carbon footprints. Despite the<br />

activities of the industry, more knowledge on LCA is still needed in the sector and among its stakeholders, and<br />

specially, active companies need to be engouraged to be more open of their activities. It has been<br />

acknowledged that when LCA is used for communication to third parties, it is critical to bring together different<br />

industries in order to develop harmonised methodology. The national methodology is based on the existing<br />

generic international standards and guidelines, as well as, best existing practises of LCA methodologies on<br />

food. The guidelines are more practical than other standards for food sector, offering clear rules to assessment<br />

makers in decision making situations they face when conducting LCA and aiming towards more comparable<br />

carbon footprinting. Workshops have been organised nearly twice a year for past three years.<br />

To create a commonly accepted guidelines, there were several workshops among stakeholders, and hearings<br />

of several LCA experts. In the workshops also different kind of carbon labels have been evaluated, latest<br />

international developments and new research results, problems in conducting product carbon footprint<br />

studies and common approach to communication has been discussed.<br />

The hopes are high that in future the active co-operation in the industry will lead to more reliable and<br />

harmonised product carbon footprint studies and which would be communicated to consumers in


understandable and meaningful way. For now, challenges, such as open discussion between food companies<br />

or creation of a common approach to communication, still remains.<br />

Miss Hannele Pulkkinen<br />

Research Scientist, MTT Agrifood Research Finland<br />

Co Author - Mr Juha-Matti Katajajuuri, Research Area Manager, MTT Agrifood Research Finland.<br />

Reducing environmental footprints in agriculture - a combined beef and dairy production<br />

The food sector, and especially the beef and dairy production, is responsible for a large share of environmental<br />

impacts of Finnish private consumption. System innovations in beef and dairy production have a large<br />

potential to reduce the environmental footprints also as it is a system which both requires and provides<br />

nutrients. The long supply chain will act as a challenging case study aiming at closed nutrient loop by optimal<br />

nutrient use throughout the entire production chain from fertilizer production through cultivation to animal<br />

production. This will require system analysis and inclusion of many experts along the chain and will give a<br />

holistic view for stakeholders of the importance of nutrient recycling in their business environment and will<br />

provide insights for policy makers on how to stimulate transition towards sustainable nutrient economy.<br />

The case study starts with a holistic, detailed carbon footprint and nutrient balance and nutrient footprint<br />

evaluation of the current different beef and milk production systems. In addition, utilizing scenario techniques<br />

and expert assessments, other footprint reduction methods are investigated, such as concentrate feed protein<br />

modifications and manure handling methods. Then the study goes further by investigating those desirable<br />

system changes which have the largest potential to improve efficient nutrient use and reduce nutrient and<br />

other environmental footprints. The potential of optimizing nutrient use, fertilization in feed production using<br />

manure and/or synthetic fertilizers, feeding intensity and composition to mitigate environmental footprints<br />

will be given a special focus.<br />

To avoid -optimization, this will be done by assessing nutrient footprints and also others environmental<br />

footprints such as carbon and acidification of current feeding and entire beef and dairy production systems. A<br />

holistic view will be used for the assessment of the nutrient footprint and its improvements and different<br />

improvement options, and also assessment of other footprints and their improvements towards sustainability.<br />

Mrs Catherine Rae<br />

Sustainability Analyst, Amcor Limited<br />

Supporting Flexible Packaging Conversion using LCA<br />

There is a growing trend for the conversion of rigid packaging to flexible formats across a range of products<br />

and for a variety of reasons. Flexible packaging can offer advantages in terms of cost, enables packaging<br />

companies to help their customers to meet packaging reduction goals, and provides increasing functionality to<br />

consumers with features such as easy open, microwavable, and refill packs, amongst many other innovative<br />

developments. However, recycling of flexible packaging from consumer products is limited, and the typical


need to landfill these materials in Australia creates a perception of a poorer environmental outcome to<br />

consumers well versed in recycling.<br />

<strong>Life</strong> cycle assessment is a critical tool to show the environmental benefit of conversion to flexible packaging,<br />

which is counter-intuitive to those focussed on recycling. Packaging companies then have a role to play in<br />

communicating the results, not just to the customer but also to the consumer through the medium of the<br />

packaging itself. There are opportunities to influence the outcome further by ensuring that end of life<br />

instructions are clearly communicated, removing confusion for consumers.<br />

At Amcor, our proprietary LCA tool, ASSET, is used to quantify the benefits of packaging development projects.<br />

ASSET uses respected international databases and company information to enable quick comparison of<br />

multiple packaging formats. ASSET covers all stages of the packaging life cycle, and is certified by the Carbon<br />

Trust to PAS 2050:2008 for cradle to gate greenhouse gas calculations. Three LCA studies are presented as<br />

examples of the benefits of flexible packaging and the output of ASSET, comparing the environmental impacts<br />

of rigid containers with flexible packs for coffee, drinking yoghurt and detergent.<br />

Dr Marguerite Renouf<br />

Adjunct Lecturer, The University of Queensland<br />

Co Author - Mr Carlos Fujita-Dimas, Post-graduate student, The University of Queensland.<br />

Application of LCA in agriculture and food in Australia – a review<br />

LCA studies conducted on <strong>Australian</strong> agriculture and food production systems and products have been<br />

reviewed to understand the status of LCA work in the agri-food sector. Around 30 published studies<br />

undertaken between 2000 and 2012 underwent a structured review to identify the scope of products /<br />

processes assessed, the purpose of the studies, the scope of the assessments (system boundaries, impact<br />

categories), and the approaches taken in inventory development and impact assessment. Observations were<br />

then made about the intent and coverage of work to date and trends in methodological approaches, leading to<br />

a critique of gaps in knowledge and opportunities for improving the value of agriculture LCA in Australia.<br />

The review found that many important <strong>Australian</strong> agricultural products (livestock for meat, dairy and wool,<br />

wheat, canola, sugarcane, some horticulture products and cotton) have been examined to various extents. The<br />

intent of most has been exploratory to identify environmental hotspots, and studies of meat products have<br />

also aimed at allowing meaningful comparisons between competing products. Studies have predominantly<br />

been partial LCAs, representing generic processes, with scopes limited to agricultural processes up to the farm<br />

gate, and focusing on global warming potential using default greenhouse gas emission factors.<br />

Few studies have assessed the broad spectrum of impact categories, or evaluated the full supply chain of<br />

agricultural products. Products found to be under-represented in published work to date are fruit, vegetables,<br />

nuts, grains other than wheat and canola, and aquaculture products.<br />

While past studies have allowed the global warming impacts of <strong>Australian</strong> agricultural processes to be well<br />

understood, there is still a considerable gap in our understanding of other impact categories (eutrophication,<br />

eco-toxicity, water use, land transformation), which may be more significant for this sector. The significance of<br />

<strong>Australian</strong> agriculture in the context of the full supply chain has also not been well assessed to date.


Dr Marguerite Renouf<br />

Adjunct Lecturer, The University of Queensland<br />

Co Authors - Dr Peter Allsopp, Manager, Cropping Systems & Technology Support, BSES Limited, Ms Nicole<br />

Price, Research Officer, The University of Queensland.<br />

CaneLCA tool to support practice change decision making in sugarcane growing<br />

CaneLCA is a customised LCA tool for <strong>Australian</strong> sugarcane growing that aims to make LCA more accessible to<br />

the sugar industry. It was developed in response to expectations that the industry adopt sustainable<br />

sugarcane-growing practices, driven by government water quality protection measures for the Great Barrier<br />

Reef, but also by opportunities to benefit from greenhouse gas abatement through the Carbon Farming<br />

Initiative. CaneLCA can be used by sugar industry extension advisors to help sugarcane famers understand the<br />

eco-efficiency of different cane growing practices and make informed decisions about practice changes. It<br />

differs from existing LCA-based tools for agriculture because it caters for the complexities of sugarcane<br />

cropping, assesses a range of impacts (not just carbon footprint), and allows users to extensively alter and<br />

compare operations.<br />

In this paper we demonstrate the use of CaneLCA for assessing practice change, by applying it to some typical<br />

practice change scenarios, and generating indicators for non-renewable energy use, carbon footprint, water<br />

use, eutrophication and eco-toxicity. The results show the potential for environmental benefits from many of<br />

the practice changes being adopted in the industry, but with possible downsides for others. It shows how<br />

CaneLCA can identify and communicate sources of, and changes in, environmental impacts so that practice<br />

change can be optimised.<br />

We also discuss feedback received from users, which has guided the tool’s development. Industry input has<br />

been crucial for ensuring the effectiveness of the tool. It has led us to present the LCA results as eco-efficiency<br />

indicators rather than absolute impact values, use more meaningful terminology to name the eco-efficiency<br />

indicators, include a single eco-efficiency score, and match data entry requirements to industry protocols. It<br />

has also identified possible future enhancements, such as integration with farm profitability calculators to<br />

better inform practice change decisions, and to enable automatic data feed from farm data management<br />

systems (if used) to avoid duplication of data collection.<br />

Dr Bradley Ridoutt<br />

Principal Research Scientist, CSIRO<br />

Co Authors - Dr Marlies Zonderland-Thomassen, AgResearch, New Zealand, Dr Stewart Ledgard, AgResearch,<br />

New Zealand.<br />

Water footprint: Application of a new single-indicator calculation method to New Zealand milk<br />

production<br />

The development of impact assessment models for water use in LCA has been an active research topic in<br />

recent years, supported by a project group working under the auspices of the UNEP-SETAC <strong>Life</strong> <strong>Cycle</strong> Initiative<br />

(Kounina et al. 2012 International Journal of <strong>Life</strong> <strong>Cycle</strong> <strong>Assessment</strong> DOI 10.1007/s11367-012-0519-3). These<br />

new methods are filling an important gap in LCA. Water is a critical resource supporting human and ecosystem


health and water use is an important environmental burden in many product systems, especially in the<br />

agriculture, food and energy sectors. Also important is a new international standard for water footprint (ISO<br />

14046) which is at an advanced stage of development. This new standard, coherent with the ISO 14040 series<br />

and environmental metrics such as carbon footprint, will support water use assessment in LCA generally and<br />

have particular relevance where LCA studies are used for environmental reporting and labeling purposes.<br />

According to ISO 14046, impacts related to both consumptive and degradative water use (pollution) need to<br />

be assessed. Due to the range of environmental mechanisms involved and the absence of a single midpoint<br />

indicator that is relevant to all the many potential impact pathways, the reporting of results as a profile of<br />

impact category indicators has been common, and meeting the market demand for a single stand-alone water<br />

footprint indicator (comparable to the carbon footprint) has been problematic.<br />

We present a new water footprint calculation method integrating consumptive and degradative water use into<br />

a single score (Ridoutt and Pfister 2012 International Journal of <strong>Life</strong> <strong>Cycle</strong> <strong>Assessment</strong> DOI 10.1007/s11367-<br />

012-0458-z) and demonstrate its use with case study dairy systems in Waikato and Canterbury, New Zealand<br />

(Zonderland-Thomassen and Ledgard SF 2012 Agricultural Systems 110, 30-40). The results highlight the need<br />

for improved nutrient management to reduce water footprints in these systems.<br />

Ms Alison Rothwell<br />

PhD Student, University of Western Sydney<br />

Application of Consequential LCA to a “Wicked” Peri-Urban Problem<br />

The <strong>Australian</strong> Public Service (APS) has stated that they are increasingly being tasked with what have been<br />

termed ‘wicked’ problems requiring policy responses (APSC 2007). Wicked problems involve complex issues<br />

where there is disagreement on the nature, scope and solution (for example, climate change). The decision to<br />

displace horticulture through urbanisation of peri-urban land in the Sydney basin can be seen as a wicked<br />

problem: it is the result of multiple causal factors; involves high levels of disagreement between stakeholders;<br />

is socially complex; and has no verifiably right solution. The stakes are high as once urbanised, land is not<br />

typically reclaimed. Linear thinking is not suitable to solve such problems. Instead, the solution lies in how to<br />

best manage the decision to urbanise. According to the APS, holistic responses utilising high level systems<br />

thinking are required in order to generate sustainable policy responses. The decision to extract land for<br />

urbanisation is typically based on economics. With natural capital providing a limited flow of goods that<br />

support civilization, it is vitally important to make optimal land use decisions that best support an increasingly<br />

uncertain future. However the environmental consequences of the decision to urbanise are not typically<br />

measured. A consequential LCA (CLCA) approach enables a method that provides quantifiable evidence of<br />

environmental impacts associated with land use decision consequences.<br />

This presentation illustrates how a consequential LCA method was used to compare scenarios: different<br />

housing systems (greenfield versus infill) were combined with different horticultural land use options (local<br />

versus interstate production) for peri-urban Sydney, using lettuce production in a case study approach.<br />

Environmental impacts including greenhouse gas emissions and cumulative energy demand were compared.<br />

Results per hectare of land indicate that environmental impacts are dominated by housing system, rather than<br />

horticultural system.


This CLCA case study provides an example of how land use options in the Sydney basin can provide both<br />

housing and food, at lower relative emissions and energy requirements. Using CLCA provides an innovative<br />

systems-based solution to inform a complex decision, providing environmental data that may balance<br />

economic growth as a sustainable policy objective. (Reference APSC 2007, Tackling Wicked Problems A Public<br />

Policy perspective, <strong>Australian</strong> Public Service Commission (APSC) viewed 28 November 2011,<br />

http://www.apsc.gov.au/publications-and-media/archive/publications-archive/tackling-wicked-problems,<br />

Commonwealth of Australia, Canberra.)<br />

Mr Rob Rouwette<br />

Director, start2see<br />

Co Author - Mr Brian Au, Director, RESET Carbon Limited, Mr Byford Tsang, Consultant, RESET Carbon Limited.<br />

LCA: supercharged<br />

This paper presents a case study where LCA is being used in a fast, practical manner to inform the client's<br />

product design and marketing strategy. The client, a starting primary battery manufacturer in Hong Kong,<br />

intended to create a new type of battery with the lowest possible environmental impact. The initial battery<br />

design was based on functionality and a high level understanding of environmental impacts. The key focus was<br />

on retrieving the highest possible percentage of materials during a typical battery recycling process. A<br />

streamlined LCA quickly showed that there were some "hidden" issues in the raw material supply chain that<br />

would have significant effects for the battery's environmental performance. The client used this information to<br />

make critical changes to the design and research various alternatives.<br />

During a follow up meeting we assessed the possibilities in real time and a decision on the changes of the final<br />

design was locked in. By dealing directly with the CEO ecause the client contact was the key decision maker we<br />

were able to implement changes at great speed. Using a life cycle approach has saved the client significant<br />

costs (marketing as well as raw material costs), has improved their chances of gaining a positive reputation,<br />

reduced the weight of their product by half and reduced environmental impacts. We are currently preparing<br />

an ISO compliant LCA that will be independently reviewed and is scheduled for completion around March/April<br />

2013.<br />

Dr Fabian Sack<br />

Principal, Fabian Sack & Associates<br />

Co Authors - Dr Maartje Sevenster, Principal, Sevenster Environmental Consultancy, Ms Louise Pastro,<br />

Manager, Sustainability and Stakeholder Engagement, Focus Press.<br />

The story behind the page – social–<strong>Life</strong> <strong>Cycle</strong> <strong>Assessment</strong> of Focus Press<br />

As part of a move toward “<strong>Life</strong> <strong>Cycle</strong> Sustainability <strong>Assessment</strong>”, social LCA (S-LCA) is a necessary extension of<br />

traditional, environmental LCA. Since the release of the Unep/Setac LCI guidelines for S-LCA in 2009 only a<br />

handful of those assessments have been performed (e.g. Ekener and Finnveden, IJLCA, 2012) despite the fact<br />

that social sustainability attracts a lot of interest. One of the complexities lies in the lack of data for the level of


disaggregation normally required for process LCA. Quantitative data for social indicators are typically available<br />

at the level of nations.<br />

Thus issues such as relating inventory data to the reference flow for the functional unit and determining<br />

materiality are complicated. Economic Input/Output tables may provide some of the background data. We will<br />

present results of a innovative <strong>Australian</strong> print industry case study, covering both social and environmental<br />

impacts, with international production chains involving countries with different social issues.<br />

We will discuss benefits and limitations of the process from perspective both of the practitioners and of the<br />

client. Interpretation of results and suitability for decision support will receive specific attention.<br />

Ms Julie Sandilands<br />

Solution Manager, PE INTERNATIONAL<br />

Co Author - Miss Oy Cheng Phang, Principal Consultant, PE INTERNATIONAL Malaysia<br />

Challenges, Opportunities and Success Factors in conducting the Carbon Footprint Study in<br />

Malaysian Port<br />

During COP15, Malaysia’s Prime Minister restated Malaysia’s commitment to reduce national carbon intensity<br />

by up to 40% by 2020 from 2005 levels. This statement was restated during the 3rd International Green<br />

Technology <strong>Conference</strong> (IGEM) in October 2012 to call for a greater concerted and pragmatic move from the<br />

industries towards a lower carbon development. However, the low response rate (13.33% in 2011, 11.43% in<br />

2012) from the Malaysia industries towards the annual survey conducted by Carbon Disclosure Project (CDP),<br />

suggests that more awareness are required for meeting the 40% carbon reduction target. As part of this<br />

initiative and commitment, Bintulu Port has committed to becoming the first Green Port in Malaysia. Arising<br />

from this commitment, Bintulu Port embarked on a carbon footprinting exercise to determine their baseline<br />

carbon emissions and to identify opportunities for reduction. PE INTERNATIOAL Malaysia was called in to<br />

provide assistance in this endeavour.<br />

This study present the challenges, limitations and opportunities from conducting a carbon footprint exercise<br />

for a Malaysian port. The methodology undertaken for this exercise was in accordance to the GHG Protocol<br />

(March 2004). Due to uncertainties regarding the methodological aspects (especially the Scope 3 emissions),<br />

data quality, lack of awareness and understanding from the departments were associated with several<br />

challenges. Outcome of the study showed that the vessels activities within the Port (vessels manuvering and<br />

berthing), which also the Scope 3 emissions were the largest source of carbon footprint.<br />

This coincides well with typical a service sector. Moreover, the method of how PE INTERNATIONAL works with<br />

Bintulu Port in developing the carbon reduction plan will be discussed in this paper. Finally, the success factors<br />

and the potentials in using carbon footprint in business communication for a port will be presented in this<br />

paper.


Miss Julia Seddon<br />

Group Environment Manager, Inghams Enterprises Pty Limited<br />

Co Author - Mr Jonas Bengtsson, Director, Edge Environment.<br />

Environmental impact of Inghams chicken products and options for product facing labelling<br />

This paper presents the results of the LCA of chicken production by Inghams Enterprises, a major poultry<br />

producer in Australia. This study was funded by a grant from Woolworths to explore environmental impact of<br />

Inghams chicken products and options for product facing labelling. Of specific interest was the comparative<br />

environmental impact of conventional and free-range chicken production, as well as fresh produce versus<br />

further processed products such as chicken schnitzel.<br />

The scope of the study was cradle to and including retail handling. Foreground data were obtained from<br />

Inghams’ internal and external reports; background data were modelled in the SimaPro software. The life cycle<br />

impact assessment includes 12 environmental impact categories, characterized at midpoint, normalised per<br />

capita Australia and weighted into <strong>Australian</strong> ecopoints. Allocation of impact between co-products were based<br />

the associated economic wholesale price of roaster chicken and breast fillet in relation to the average overall<br />

production output value.<br />

The results confirm previous research in that upstream feed production is the largest impact area of the<br />

chicken meat supply chain, contributing approximately half of the overall impact and two thirds of the overall<br />

water consumed for chicken meat. This highlights the importance of productivity measures, such as feed<br />

conversion ratio, on the environmental performance of chicken meat. Poultry farm operation contributes<br />

approximately one third of the overall impact, primarily from manure emissions and energy used in chicken<br />

housing, and over half of non-renewable energy consumption. Meat processing is the third largest impact<br />

source with approximately 10% of the overall impact.<br />

All other life cycle stages combine to less than 10% of the overall impact. Attempts to benchmark the results<br />

with the <strong>Australian</strong> RIRDC chicken meat LCA and international studies highlighted the need for a consistent<br />

and level playing field methodology for the food sector in order for LCA to provide meaningful and reliable<br />

input into businesses decision-making and for product comparisons.<br />

Dr Maartje Sevenster<br />

Director, Sevenster Environmental<br />

Delayed GHG emissions : limitations of the ILCD approach<br />

In life-cycle assessment (LCA) and carbon foot printing (CFP), climate neutrality of so-called short-cycle carbon<br />

dioxide emissions has always been accepted as a given. The inevitable question that arises from this practice is<br />

for what time separation of uptake and emission the carbon cycle can no longer be called 'short'. To avoid an<br />

arbitrary cut off, current methodology development focuses on delayed emissions (see Brandao et al., January<br />

2013), e.g. the recommendations of the ILCD Handbook.


The ILCD Handbook has considerable standing in providing guidance to best practice LCA, with practitioners as<br />

well as industry bodies, that refer to the Handbook in e.g. product category rules. The current draft ISO<br />

standard 14067 states that the effect of delaying emissions (by more than ten years) may be included in<br />

inventory and reported as a separate item. As practitioners will have to make a – well founded – choice on<br />

how to calculate those effects (no recommendation is given in the draft ISO standard), it is important to be<br />

aware of the limitations of fully linear approaches such as ILCD (and similarly PAS2050). We assess the<br />

influence of the profile of emissions as a function of time and propose some limited-linear approaches that<br />

more closely follow results of dynamic modeling.<br />

Dr Maartje Sevenster<br />

Director, Sevenster Environmental<br />

Natural land transformation in comparative LCA.<br />

Natural land transformation is not only a major cause of biodiversity loss but also one of the large contributors<br />

to global greenhouse gas emissions. A complex issue in LCA and foot printing is how to attribute this land<br />

transformation to particular products. While foot printing standards typically apply a 'worst case' direct<br />

attribution, there is a move towards averaged, indirect attribution (Cranfield report). While there is no doubt<br />

that agricommodity markets are very much intertwined, this approach does not leave a lot of perspective for<br />

producer responsibility as on of the solutions.<br />

In a recent study for a Dutch NGO, we looked into the issue of replacing South American soy by alternative<br />

ingredients in cattle feed. We will report on the findings regarding minimum conditions that need to be<br />

satisfied in order to limit the pressure on South American ecosystems with some certainty, both via direct and<br />

indirect mechanisms. The approach provides a step forward in the discussion on environmental consequences<br />

of replacing South American soy. We will apply the findings to the <strong>Australian</strong> context.<br />

Dr Maartje Sevenster<br />

Director, Sevenster Environmental<br />

QuestionMark: LCA made easy - consumer app providing full life cycle information<br />

Mid 2012, a new smartphone App was launched in the Netherlands.<br />

It provides people in supermarkets with information on life-cycle impacts of a product when they<br />

scan the barcode.<br />

The App uses impacts from an extensive life cycle inventory database containing more than 100<br />

production chains of meat, dairy and alternative meat products. Next to typical LCA endpoint<br />

indicators, a quantitative evaluation of animal welfare as well as several other issues is made. The<br />

App has been very popular in the first year of its existence and recently 7 million Euro was granted<br />

for extending the concept to include more product groups as well as additional impact categories.


Miss Helene Sterzik<br />

PhD Student, Massey University<br />

Co Author - A/Prof Sarah McLaren, Associate Professor, Massey University, Dr Anthony Hume, Senior Advisor,<br />

Landcare Research.<br />

Challenges and Enablers for Successful LCM Uptake in the New Zealand Kiwifruit Industry<br />

New Zealand relies heavily on agricultural production of primary products which is intimately connected with<br />

the natural environment. Therefore, proactive integration of sustainability into business practices is<br />

particularly important for primary industries to reinforce the country’s ‘clean and green’ image and strengthen<br />

competitiveness in the global market place [1-3]. One approach to incorporate environmental sustainability<br />

into company operations, management and strategies is the implementation of <strong>Life</strong> <strong>Cycle</strong> Management (LCM)<br />

initiatives.<br />

However, research focusing on individual organisations has shown that the majority of them, particularly small<br />

and medium sized enterprises (SMEs), still struggle to effectively manage and mitigate environmental impacts<br />

[4, 5]. An alternative approach is to focus on overcoming the LCM implementation challenges through<br />

activities initiated at the level of an industry sector. That will potentially allow cost and time effective LCM<br />

implementation in any industry sector.<br />

For this research a framework has been developed that visualises and assesses the various drivers and<br />

enablers to successful LCM uptake within an industry sector. It is based on a literature review on<br />

environmental management in SMEs, supply chain management and technology transfer. The latter two are<br />

closely related to the concept of LCM since knowledge about LCM needs to be communicated effectively to<br />

and between the organisations that are linked in a product life cycle. The main criteria in the framework<br />

include structure of the sector, resources, culture, recognition of environmental issues, market requirements,<br />

distance to markets, communication and networks. The framework has been tested in the New Zealand<br />

kiwifruit industry using a combination of quantitative and qualitative research methods. The findings from the<br />

face-to-face interviews with growers, packhouses and the industry board show that the New Zealand kiwifruit<br />

industry sees limited financial resources and the long distance to markets as major barriers. However, the<br />

industry benefits from its unique structure characterised by almost all growers using the single kiwifruit<br />

marketing desk and its proactive stance on environmental issues. References 1. Green Growth Advisory Group,<br />

Greening New Zealand's Growth. 2011. 2. McLaren, S., Defining a Role for Sustainable Consumption Initiatives<br />

In New Zealand. 3. Pure Advantage, New Zealand's Position in the Green Race, 2012. p. 58. 4. Hillary, R., Small<br />

and medium-sized enterprises and the environment: business imperatives2000: Greenleaf Publishing. 5.<br />

Seidel, M., et al., Overcoming Barriers to Implementing Environmentally Benign Manufacturing Practices:<br />

Strategic Tools for SMEs. Environmental Quality Management, 2009: p. 37-55.


Mr Wymond Symes<br />

Consultant, Catalyst Ltd<br />

The impact of methodology and data on calculating enteric fermentation emissions for the New<br />

Zealand dairy goat industry<br />

In agricultural LCA studies involving livestock there are two methods for determining GHG emissions from<br />

enteric fermentation. A Tier 1 approach applies a default annual methane value, sourced from IPCC guidelines<br />

or local studies, to each animal species. A Tier 2 approach is country specific and calculates emissions from<br />

feed intake data, either measured or estimated based on energy requirements and dietary composition. New<br />

Zealand has a growing dairy goat industry which is actively investigating its environmental impact. In 2012 a<br />

scoping study on the life cycle carbon footprint of on farm production was performed on case study farms in<br />

the Waikato.<br />

Like most livestock agricultural systems, the biggest contributor to GHG emissions was found to be enteric<br />

fermentation. Using the Tier 1 approach we determined enteric fermentation emissions to range between 8.6<br />

and 12.0 tonne methane (CH4) for a single farm over 3 consecutive seasons. Applying Tier 2 methodology to<br />

the same farm emissions ranged between 16.0 and 21.9 tonne CH4. For the Tier 1 approach the emission<br />

factors (EF) used in New Zealand’s national GHG inventory (8.6 kg CH4/head/annum) was applied. For the Tier<br />

2 approach methane emissions were based on estimated dry matter (DM) intake values and an EF of 20.9g<br />

CH4/kg DM (OVERSEER® Technical Bulletin).<br />

The difference, nearly 2-fold, has been attributed to some of the assumptions made in estimating DM intake<br />

and highlights the uncertainty associated with currently available data. This paper will discuss how DM intake<br />

values were calculated and compare this approach to that taken for the Tier 1 emission factor used, identify<br />

what data is missing for a comprehensive Tier 2 method, and discuss the challenges a relatively small industry<br />

may have in meeting the requirements for Tier 2 data.<br />

Mrs Katie Symons<br />

Senior Engineer, Ramboll<br />

Co Authors - Dr Alice Moncaster, Senior Research Associate, University of Cambridge, Dr Digby Symons,<br />

University Lecturer, University of Cambridge.<br />

An application of the CEN/TC350 standards to an Energy and Carbon LCA of timber used in<br />

construction, and the effect of end-of-life scenarios.<br />

The use of timber products in construction in Europe is increasing; this is coinciding with an increasing<br />

awareness of the energy and carbon impacts of the construction, maintenance and demolition of buildings<br />

(known as embodied energy and carbon), in addition to the more commonly assessed and well-regulated<br />

operational impacts. Businesses are keen to be able to present reliable and robust figures for embodied energy<br />

and carbon to inform design and procurement decisions, but are currently struggling, as agreement on <strong>Life</strong><br />

<strong>Cycle</strong> <strong>Assessment</strong> (LCA) methodologies to apply in these situations is not finalised.


This paper describes the LCA approach presented in the European Standards suite CEN/TC350, and assesses<br />

the results when it is applied to timber, particularly innovative heavyweight construction products and<br />

techniques, such as cross laminated timber. Comparisons of the energy and carbon impacts of timber with<br />

different end-of-life scenarios (such as incineration with energy recovery and landfill disposal) and the<br />

treatment of the carbon ‘sequestered’ within timber products is discussed. Availability and quality of data for<br />

energy and carbon LCA of timber in construction is examined. Results from an energy and carbon LCA tool<br />

developed in the UK at the University of Cambridge are presented, and the relative impact of each life cycle<br />

phase, as well as timber and other construction materials used in a traditional UK domestic building is<br />

analysed.<br />

A sensitivity analysis of these results to the end-of-life scenario adopted and different timber construction<br />

systems is presented. Finally, the energy and carbon impacts of a larger home-grown timber construction<br />

industry in the Australasia region is assessed, including quantifying the energy and carbon savings that could<br />

be made by using local (rather than Austrian) sources for the timber used in the Forte building in Melbourne,<br />

and potential energy and carbon implications to the post-earthquake rebuilding of Christchurch.<br />

Dr Mark Tatam<br />

Technical Manager, Kingspan Insulated Panels Pty Ltd<br />

Co Author - Mr Jonas Bengtsson, Director, Edge Environment Pty Ltd.<br />

Environmental Product Declarations : A Building Industry Experience for Kingspan Insulated Panels<br />

Kingspan have been publicly publishing its global sustainability performance for the last six years as part of a<br />

Global Reporting Initiative (GRI) to promote economic, environmental and social sustainability. A key part of<br />

this has been the development of environmental product declarations (EPDs) and labels for their insulated<br />

panels range.<br />

The overall goal of publishing EPDs and labels is to encourage the demand for, and supply of, those products<br />

that cause less impact on the environment, through communication of verifiable and accurate information<br />

that is not misleading, thereby stimulating the potential for market-driven continuous environmental<br />

improvement. In 2011 Kingspan commissioned Edge Environment to conduct a LCA study of their range of<br />

insulated panel products for roof, wall and controlled environment applications produced in Australia, in order<br />

to establish rigorous environmental credentials for external communications. The study was conducted in<br />

accordance with the Building Products <strong>Life</strong> <strong>Cycle</strong> Inventory (BP LCI) methodology developed by <strong>Australian</strong><br />

building product manufacturers under the auspices of the Building Products Innovation Council (BPIC).<br />

The study was peer-reviewed by PE International in the UK and the results published as a self-declaration<br />

following the ISO 14025 format for Type III EPDs, in the absence of an <strong>Australian</strong> or New Zealand EPD<br />

programme. The EPD of embodied performance in combination with extensive energy modelling of whole<br />

building operational performance was first published and presented at the GBCA Green Cities <strong>Conference</strong> in<br />

2012.<br />

This paper presents the <strong>Australian</strong> Kingspan business and its staff’s learnings and experiences from developing<br />

EPDs. It also describes the new challenges for Kingspan – for example how EPDs are effectively communicated<br />

by Kingspan, and how they are interpreted and used in the marketplace by green product leaders.


Mr Bill Thompson<br />

Boral Plasterboard<br />

Industry Update - Gyspum Board Manufacturer's of Australasia<br />

The GBMA was a leader in commissioning an industry based LCI on a cradle to grave basis encompassing all<br />

plasterboard manufacturers in Australia and New Zealand. The resulting industry average life cycle assessment<br />

data is publicly available and forms the basis of the GBMA’s entry in the BPIC database. An update of activities<br />

since then, including amendments required for inclusion in the AusLCI database will be presented.<br />

Dr Pep Turner<br />

Ecologist, School of Geography and Environmental Studies, University of Tasmania<br />

Co Authors: Fabiano Ximenes, SW Dept. of Primary Industries, Dr. Trent Penman, University of Wollongong,<br />

Dr Brad Law, NSW Dept of Primary Industries, Dr Cathy Waters, NSW Dept of Primary Industries, Matthew Mo,<br />

NSW Dept. of Primary Industries, Dr Pip Brock, Port Stephens Fisheries Centre<br />

Accounting for biodiversity in <strong>Life</strong> <strong>Cycle</strong> Impact <strong>Assessment</strong>s of forestry and agricultural systems<br />

There are currently no globally appropriate means of assessing biodiversity within the LCA framework. A new<br />

project is under way to test a new method proposed to address the issue of accounting for biodiversity<br />

impacts in LCA. The approach relies on literature review and expert opinions through a series of questions<br />

which aim to encapsulate the main issues relating to biodiversity within a disturbance impact framework. This<br />

project will test the applicability of this model using two forest industry case studies (native and plantation<br />

forestry) and a case study from the agricultural sector (cropping). Using a series of quantitative questions,<br />

biodiversity impacts are estimated for each taxonomic group (e.g. flora, mammals, diurnal birds, frogs and<br />

invertebrates) and then scaled to an overall biodiversity measure.<br />

In this talk we will provide some background on the proposed method, outline the current project and some<br />

preliminary results based on an initial literature review and a survey of ecologists to refine proposed questions<br />

to be addressed by the method.<br />

Mr Stephen Wiedemann<br />

Agricultural Scientist, FSA Consulting<br />

Co Authors - Ms Caoilinn Murphy, Project engineer, FSA Consulting, Mr Eugene McGahan, Senior Engineer, FSA<br />

Consulting.<br />

Greenhouse gas mitigation strategies for livestock production: what are the impacts on resource<br />

use?<br />

Reducing greenhouse gas emissions (GHGs) is an important objective for <strong>Australian</strong> farmers supported by<br />

government legislation (i.e. the Carbon Farming Initiative – CFI). However, there has been little investigation of<br />

changes to other environmental impacts when targeting GHG mitigation.


This study investigated two farm-gate GHG mitigation strategies for beef and pork production and examined<br />

the impact on energy, water and cultivated land use. The emission profile of both beef and pork is dominated<br />

by one major source; enteric methane (beef) and manure management methane (conventional pork). For beef<br />

cattle, mitigation strategies for grower cattle included i) feedlot finishing, and ii) grazing on irrigated Leucaena.<br />

Both strategies worked by improving growth rates and via diet modification to reduce enteric methane.<br />

The pig GHG mitigation strategies focussed on changed housing systems to remove manure management<br />

conditions favourable to methane production. Both beef mitigation strategies reduced emissions per kilogram<br />

of live-weight (25% for feedlot finishing, 29% for finishing on Leucaena) compared to the baseline scenario<br />

(grass finished 600 kg LW steer). However, energy use increased more than two-fold for feedlot beef and<br />

water use increased markedly for grazing on irrigated Leucaena. Both scenarios required more cultivated land<br />

use. For pigs, outdoor housing during breeding reduced GHG emissions and water use by 21% and 24%<br />

respectively compared to the baseline. However, energy and grain use were both higher because of the<br />

system’s poorer breeding efficiency. Deep litter growing-finishing resulted in 44% lower GHG and a<br />

concomitant reduction in both water (36% decrease) and energy (8% decrease) compared to conventional<br />

housing. However, both systems tend to provide poorer growing conditions for pigs, resulting in inferior<br />

performance compared to conventional housing. The results highlight the importance of a broader impact<br />

assessment process to determine where GHG mitigation can be achieved without ‘burden shifting’ to other<br />

impact categories.


Shortform<br />

Presenters<br />

PATHWAYS TO<br />

GREENING GLOBAL<br />

MARKETS<br />

<strong>ALCAS</strong>


Dr Wahidul Biswas<br />

Senior Lecturer, Curtin University<br />

Co Author - Mrs Deborah Engelbrecht, PhD Candidate and Research Assistant, Curtin University.<br />

A life cycle assessment of annual, fertilised perennial and unfertilised perennial pastures<br />

The livestock industry contributes significantly to Australia’s greenhouse gas (GHG) emissions profile. Perennial<br />

pastures are considered to be more economically and environmentally sustainable system than annual<br />

pastures. Despite these facts, GHG emissions from the production of beef are considerably higher than other<br />

products. Therefore, this research aims to assess the GHG from beef production from three different pasture<br />

systems in Western Australia.<br />

A life cycle assessment (LCA) has been carried out to determine the greenhouse gas emissions from the<br />

production of one kilogram of carcass beef from annual, fertilised perennial and unfertilised perennial<br />

pastures. The system boundary of the LCA life cycle assessment mainly considers two stages: pre-farm and onfarm.<br />

Beef production from the fertilised perennial pasture produce more GHG emissions than that from the<br />

annual and unfertilised perennial pastures. Enteric emissions accounted for a significant portion of GHG<br />

emissions from both types of pastures considered.<br />

Dr Philippa Brock<br />

Leader, <strong>Life</strong> <strong>Cycle</strong> <strong>Assessment</strong>, Department of Primary Industries<br />

Co Authors - Mr Douglas Alcock, Livestock Officer, Department of Primary Industries, Mr Patrick Madden,<br />

Senior Economist, Department of Primary Industries.<br />

Overcoming methodological dilemmas when calculating greenhouse gas emissions for wool<br />

production: the application of LCA.<br />

A single-issue LCA was conducted to determine the greenhouse gas emissions profile and carbon footprint of<br />

19 micron wool produced in the Yass Region (NSW). Total emissions were found to be 24.9 kg CO2-e per kg of<br />

greasy wool at the farm gate, based on a 4941 breeding ewe enterprise on 1000 ha, with a total greasy wool<br />

yield of 65.32 tonnes per annum. The co-products included 1474 tonnes sheep meat as liveweight from<br />

wethers and cull ewes plus 978 maiden ewes sold off-farm.<br />

The relative contribution of different components of the production system was determined. Direct emissions<br />

of methane on-farm (86% of total) was the dominant emission, followed by nitrous oxide emitted from animal<br />

wastes directly (5%) and indirectly (5%), and decomposition of pasture residue (1%). Only 2% of total<br />

emissions were embodied in farm inputs, including fertiliser. Enteric methane production was calculated using<br />

five recognised methods and results were found to vary by 27%. As these differences are primarily driven by<br />

feed intake, we are exploring opportunities to obtain field data for this attribute. Calculated emissions for wool<br />

production changed substantially, under an economic allocation method, by changing the enterprise emphasis<br />

from wool to meat production (41% decrease) and by changing wool price (29% variability), fibre diameter<br />

(23% variability) and fleece weight (11% variability).


Given the dramatic difference in allocated emissions between wool and meat focussed enterprises, simple<br />

subtraction of emissions determined for a meat-dominant enterprise as with a systems expansion allocation<br />

method, effectively reduces emissions allocated to wool to that of a meat-dominant enterprise. As enterprise<br />

profitability is heavily reliant on co-production, reduced demand for wool will result in substitution of meat<br />

with that from other sources, with uncertain market connections. Therefore, we undertake economic<br />

allocation. We present data about variability and discuss assumptions, to enable ongoing development of<br />

robust livestock LCAs.<br />

Annette Cowie<br />

Director, Rural Climate Solutions, University of New England<br />

Co Author - Brendan George, Lukas Van Zwieten.<br />

Biomass for bioenergy or biochar: USING LCA to assess which delivers greater climate benefits<br />

Pyrolysis produces renewable energy products (syngas and bio-oil) and a solid that can be used as a soil<br />

amendment - known as biochar. Biochar can improve plant growth and reduce fertiliser requirements. It can<br />

contribute to climate change mitigation through delayed decomposition of biomass: biochar is estimated to<br />

remain in soil for centuries to millennia. Furthermore, biochar can reduce nitrous oxide emissions from soil.<br />

To determine the net climate change impact of converting biomass to biochar, and contrast this with<br />

alternative uses for biomass, the whole life cycle of the alternative systems must be considered.<br />

A <strong>Life</strong> cycle assessment (LCA) approach was used to assess the GHG emissions and sequestration across the<br />

biochar life cycle, including fossil fuel use in harvesting, processing, transport and application of biochar;<br />

indirect emissions such as from fertilizer manufacture; changes in soil and biomass carbon stocks; emissions of<br />

N2O and CH4 as well as CO2. The net impact of biochar was determined by comparison with the applicable<br />

reference system, representing the conventional soil amendment, use of the biomass, and energy system. The<br />

greatest emissions reduction was estimated as 3.2 kg CO2-e per kg biochar, for poultry litter biochar made at<br />

550°C applied to maize. Use of greenwaste for biochar had lower net benefit compared with other biochars,<br />

and may increase emissions if the biomass would otherwise have been deposited in landfill, where little<br />

decomposition occurs, and if the methane generated was captured and used for electricity generation.<br />

However, if the landfill had no methane capture, then use for biochar was preferable. If the alternative fate of<br />

greenwaste was mulch or burning, then utilisation for biochar gave a strong advantage. Biochars made at<br />

higher temperature gave greater benefit than lower temperature biochars, due to their greater stability and<br />

higher syngas yield during pyrolysis.<br />

The wide variation in results between biochars and target crops, and the great sensitivity to the assumptions<br />

for the reference case, mean that LCA studies should be conducted for each situation in which biochar is being<br />

considered.


Ms Felicity Denham<br />

PhD student, Centre of Excellence Science Seafood Health<br />

Co Authors - Dr Janet Howieson, Senior Research Fellow, Centre of Excellence Science Seafood Health,<br />

Dr Wahidul Biswas, Postgraduate Programme Coordinator and Senior Lecturer, Sustainable Engineering Group.<br />

Environmental Impact of a finfish supply chain in Western Australia: analysis, interventions and<br />

opportunities<br />

<strong>Australian</strong> seafood supply chains (from harvest through to retail outlets) are under pressure from consumers<br />

and other groups to improve their environmental impact. <strong>Life</strong> cycle assessment (LCA) is a useful tool to<br />

measure the environmental impacts of seafood supply chains and identify potential areas of improvement.<br />

The current research which applied LCA to assess the carbon footprint of wild caught Saddletail Snapper trawl<br />

harvested in an isolated area in Western Australia will be discussed. The research involved product either<br />

filleted locally for a regional retail store and nearby mining towns, or as whole fish transported to a Perth retail<br />

outlet. Although LCA research has been done, tropical fish trawled in Western Australia differ from existing<br />

trawling operations LCAs (e.g. Spain and Norway) as the warmer waters require stringent temperature control<br />

and harvesting in remote locations entail long transport chains from harvest to port and through to Perth. The<br />

supply chain of the current research consisted of three main stages: harvesting, sorting and processing. The<br />

harvest stage includes the on-boat and trawling processes, sorting the catch into species, cooling and storing<br />

the fish, and unloading. The processing stage includes packing and filleting before the wholesale and retail<br />

stage. LCA identified “hotspots” from the aforementioned stages of the seafood supply chain.<br />

Diesel combustion has the greatest impact in the harvesting stage whereas processing and retail both emit<br />

refrigeration gases and require a large quantity of electricity for ice manufacturing to keep the fish at a<br />

constant temperature. Mitigation strategies were identified and modelled for potential improvements in the<br />

environmental impact of the chain measured. Aligned with the LCA were quality and economic analyses to<br />

ensure the proposed mitigation strategies are also analysed for the potential impact on product quality,<br />

profitability and supply.<br />

Mr Tim Edwards<br />

CEO, <strong>Australian</strong> Refrigeration Association<br />

The Need For LCA / EPD Use In The HVAC&R industry<br />

It is well recognised that HVAC&R plays a key role in the environmental impact of the built environment. This<br />

understanding does not give rise to sufficient understanding or action. We will show how HVAC&R is<br />

responsible for about 11% of national emissions, how this could be reduced by 50% within ten years and the<br />

barriers to making it happen.<br />

We will canvass the progress being made in Australia and world wide to offer solution. We will discuss the<br />

many issues that cause the HVAC&R industry to fail to address the opportunities for improvement. We will<br />

recommend the use of LCA / EPD in then HVAC&R industry and we will recommend the development of a<br />

product stewardship structure of the industry.


Dr Andréa Franco Pereira<br />

Professor, Department of Architectural and Urban Technology, School of Architecture,<br />

Universidade Federal de Minas Gerais – UFMG<br />

Co Author - Dr Alfredo Jefferson Oliveira, Professor, Department of Arts, Pontifícia Universidade Católica - PUC-<br />

Rio.<br />

<strong>Life</strong> <strong>Cycle</strong> <strong>Assessment</strong> (LCA) of lychee crop in Sul de Minas, Brazil<br />

This study provides results of the <strong>Life</strong> <strong>Cycle</strong> <strong>Assessment</strong> (LCA) of the lychee (Litchi chinesis) crop in production<br />

in Sul de Minas, Brazil. Currently, litchi cultivation in Brazil covers an estimated area of 1000-2000 hectares.<br />

The State of São Paulo is the largest producer accounting for about 70% of production, followed by Minas<br />

Gerais and Paraná.<br />

The results presented herein were obtained from the LCA, using GaBi 4.0 software from the inventory which<br />

includes production of lychee and its distribution logistics, with reference to the period of a crop, i.e. one year.<br />

The scope of the analysis includes the step of obtaining the fruit in the orchard (fungicide and herbicide<br />

application, mowing, fertilization and irrigation), as well as the stages of harvesting, packaging, distribution<br />

and consumption. The data input and output were calculated from the functional unit corresponding to a<br />

production of 970 trees in one year.<br />

This analysis is part of research conducted by the producer, whose main objective is to understand the limits<br />

and possibilities of obtaining indicators of social impact in order to allow assessment of the socioenvironmental<br />

consequences, gains and losses of lychee culture during its life cycle. The research intends to<br />

identify critical points in the process during which action can be taken that seeks to mitigate negative impacts,<br />

so that the environmental gains achieved can be disseminated to consumers, and demonstrate the importance<br />

of sustainable market action deployed into production.<br />

Dr Anthony Halog<br />

Lecturer, University of Queensland<br />

<strong>Life</strong> <strong>Cycle</strong> Sustainability Analysis of Biofuel Supply Chains<br />

Towards developing an integrated decision support system (DSS) suite of tools that accounts for multistakeholders’<br />

interests in assessing biofuel system’s sustainability, this paper proposes how to address the<br />

grand challenges in evaluating the sustainability of biofuels via life cycle and integrated sustainability modeling<br />

and analysis with consideration to temporal and spatial dimensions.<br />

This work suggests approaches, frameworks, methods and tools that can be used to respond to the challenges<br />

of analyzing the sustainability implications of biomass-based products. Specific grand challenges related to<br />

biofuels have already been addressed in disaggregated and piecemeal fashion in several papers in various<br />

disciplines. However, there is a need to integrate the methodologies systematically and computationally to<br />

obtain comprehensive results (i.e. critical indicators and metrics) that are useful to different stakeholders and<br />

can support decisions and policies in public and private sectors.


Thus, our one grand challenge is to effectively integrate our existing methods and synthesize our results with<br />

regard to the triple dimensions of sustainability and to infer relevant and critical information either to support<br />

or not the bioeconomy development (i.e. whether or not to invest in biofuels, bioenergy and bioproducts). <strong>Life</strong><br />

cycle sustainability analysis contributes to an ongoing process that organizes both information and the process<br />

of prioritizing information needs.<br />

Dr Nawshad Haque<br />

Scientist, CSIRO<br />

Co Author - Mr Terry Norgate, Principal Research Engineer, CSIRO.<br />

<strong>Life</strong> cycle based greenhouse gas emission estimation of various mining methods<br />

Mining is an important economic activity in Australia. However, detailed assessments of greenhouse gas<br />

emissions from various types of mining methods such as open-cut, underground, heap leaching and in-situ<br />

leaching are limited in the literature. For this reason, CSIRO is undertaking LCA of mining methods in greater<br />

detail than previously considered. The major metallic mineral commodities of interest in Australia are iron ore,<br />

bauxite, copper, gold and nickel. The greenhouse gas emissions for the extraction of these metals using various<br />

mining methods have been estimated using life cycle assessment methodology and are presented in this<br />

paper. Specific case study results will be presented, particularly for the newer mining methods. For example,<br />

in-situ leaching (ISL) is a chemical method of recovering useful minerals directly from underground ore bodies<br />

which is referred to as ‘solution mining’. ISL is commonly used for uranium mining, accounting about 36% of<br />

global production.<br />

The main benefits are claimed as to be a lower impact in terms of visual disturbances and lower energy use,<br />

cost, environmental emissions compared with conventional open-cut or underground mining methods and<br />

potential utilisation of lower grade resources. However, there is a lack of reported studies on the assessment<br />

of environmental impacts of ISL, particularly the life cycle-based greenhouse gas (GHG) emissions. The SimaPro<br />

LCA software was used to estimate the GHG footprint of the ISL of uranium, gold and copper. The total GHG<br />

emission from uranium ISL was estimated to be 38 kg CO2e/kg uranium U3O8 concentrate (yellowcake), 902<br />

kg CO2e/troy oz gold, and 4.8 t CO2e/t Cu for the ore grades assumed in the study. These results are compared<br />

with conventional mining methods where applicable.<br />

Mr Richard Hamber<br />

<strong>Australian</strong> Window Association<br />

Building Products <strong>Life</strong> <strong>Cycle</strong> Inventory (BP LCI) - Progress and Next Steps<br />

LCA data available internationally is typically not based on consistent methodology – each sector adopting an<br />

approach that plays to the industry’s strengths. When selecting between competing specifications for building<br />

design, incompatible base data may lead to erroneous conclusions. The Building Products Innovation Council<br />

(BPIC) is the peak body for the producers of building materials in Australia. Assisted by joint funding from<br />

AusIndustry, BPIC developed the BP LCI as its contribution to AusLCI. BP LCI provides a robust, “level playing<br />

field” basis for conducting LCA for construction in Australia including: • Cross-sector consensus agreed


methodology, for data collection and impact assessment • 121 generic average <strong>Australian</strong> building product<br />

unit processes • Multi-stakeholder environmental impact weightings from 11 different cities providing a<br />

consistent way of interpreting LCA’s • A Protocol for the correct and appropriate use of BP LCI Since<br />

publication in June 2010, BP LCI data has been used: • For LCA based materials credits in the <strong>Australian</strong> Green<br />

Infrastructure Council’s (AGIC) Infrastructure Sustainability (IS) rating tool. • For the ANZ Transport Authorities<br />

Greenhouse Group (TAGG) greenhouse footprint assessment of alternative road constructions (Carbon<br />

Gauge). • To benchmark National Standards for <strong>Australian</strong> ecolabels and EPD’s – Masonry Products, Windows<br />

and Roofing Systems in progress; Pipework, Carpet and Flooring systems coming soon • For ENVEST Au LCA<br />

design tool developments Next steps for BP LCI may include: • Further refinement and update of the BP LCI<br />

website and the published datasets • Development of fully modeled ILCD and Ecospold compatible datasets<br />

for sale to LCA practitioners • Advocacy for the adoption of BP LCI compliant credits within Green Star, NABERS<br />

and regulation • Workshops to assist practitioners to use BP LCI compliant with the methodologies and<br />

Protocol • Additional datasets, especially for fit-out • Coordination with <strong>ALCAS</strong> (LCANZ) and National<br />

Standards<br />

Mr Richard Haynes<br />

Systems Development and Operations Manager, eTool<br />

The eTool Product Roadmap<br />

Building rating systems are proliferating as more people inform themselves and demand sustainability. Much<br />

debate ensues over the relative merits of the many different approaches being employed to measure<br />

sustainability. Similarly, the definition of “sustainable” is now being scrutinised by the public who are on the<br />

lookout for greenwashing.<br />

Within this environment, the integrity and power of LCA to enable truly sustainable outcomes is being<br />

recognised. Indeed, the well-established building rating bodies are implementing LCA into their methods<br />

rapidly whilst the European Committee for Standardisation is specifying LCA as the method for measuring the<br />

sustainability of buildings. Investigation into how LCA may be integrated into building codes is being<br />

conducted, whilst environmental footprint labelling trials are occurring in numerous countries for consumer<br />

goods. The pathways to large scale implementation of LCA in building design have been laid. Meeting this<br />

demand and ensuring the users of LCA tools enjoy the experience now becomes the challenge for LCA tool<br />

developers.<br />

Mrs Mahsa Karimpour<br />

phD Student, University of South Australia<br />

Co Authors - Dr Frank Bruno, Senior Research Fellow, Barbara Hardy Institute, Dr Martin Belusko, Research<br />

Fellow, Barbara Hardy Institute.<br />

Minimisation of life cycle energy of <strong>Australian</strong> homes<br />

Each year residential buildings make up a large percentage (20-40%) of total energy consumption in developed<br />

countries. This is why lot of studies focusing on decreasing energy consumptions in buildings. This research


aims to develop a life cycle energy model for residential houses in Australia and then optimise it to minimize<br />

whole life cycle energy.<br />

There are many studies about methods to reduce operational energy in the literature. However, not enough<br />

work about embodied energy has been done. Regarding to climate conditions in Australia embodied energy<br />

has larger proportion from total life cycle energy in residential buildings compare to dwellings in Europe. Cold<br />

winters in Europe have a strong effect on operational energy in houses in that area which is not happening in<br />

Australia.<br />

Therefore, in this study along with focusing on operational energy there will be a particular emphasis on<br />

embodied energy and techniques to minimize this energy in houses in Australia. For developing this model,<br />

different climate zones in Australia as well as a number of typical residential buildings will be examined. Also,<br />

different sources of building materials are considered in studying embodied energy of local and imported<br />

building products. AusLCI and BPIC LCI will be used for the datasets of <strong>Australian</strong> building products. In addition,<br />

Ecoinvent and other data from literature will be used for imported materials. Different heating and cooling<br />

systems and passive designs regarding to their impact on energy payback period and embodied and<br />

operational energy in buildings will be studied as well to achieve a feasible design for minimum life cycle<br />

energy buildings.<br />

Dr Paul Koltun<br />

Senior/Research Scientist, CSIRO<br />

Co Author - Prof. Miron Bekker, Prof .of Mathematics, University of Pittsburgh at Johnstown.<br />

Optimisation of forest rotation cycles<br />

An approach to optimise duration of the forest rotation cycle on established forest plantation is proposed.<br />

Such approach allows mathematically accurate evaluation of the cycle duration depending on defined goal:<br />

maximisation of CO2 uptake by the forest or maximisation of the forest growers gains taking into account tax<br />

on carbon emissions, quantity of grown wood, interest rate for selling wood biomass, selling price, etc. It is<br />

shown that estimation of the optimal duration of the forest rotation cycle can be done on the basis of a few<br />

known empirical parameters.<br />

Developed approach is illustrated on few examples for pine forest growth in Australia. The optimal duration of<br />

the forest rotation cycles have been estimated for some defined goals. The length of rotations cycles are 7 and<br />

15 years if the goal is maximisation of CO2 sequestration from the atmosphere without and with taking into<br />

account GHG emissions from one per cycle forest management operations, respectively. The same example<br />

leads to the optimal cycle of 17 years if goal is maximisation of the gain for forest growers. If an interest rate<br />

for selling wood biomass or quality of wood is also taken into account then the optimal duration of the forest<br />

rotation cycle is changed to approximately 14 or 10 years, respectively.


Mr Joe Lane<br />

Research Scientist, University of Queensland<br />

Co Authors - Prof Paul Lant, Head of School, Chemical Engineering, University of Queensland, Prof Mark<br />

Huijbregts, Professor of Integrated Environmental <strong>Assessment</strong>, Radboud Universty Nijmegen, Netherlands.<br />

<strong>Life</strong>-cycle toxicity modelling in the <strong>Australian</strong> context<br />

Toxicity modelling has long been a high profile component of the <strong>Life</strong>-cycle <strong>Assessment</strong> methodology.<br />

Research efforts in recent years have identified a number of substantial improvements that will increase the<br />

fidelity of available LCA toxicity models. The majority of these support the ongoing regionalisation of LCA<br />

impact assessment, and are therefore of particular relevance in the <strong>Australian</strong> context. Australia’s unique<br />

combination of geo-physical, climatic and demographic factors make it difficult for globally-generic impact<br />

models to provide results that hold much relevance for <strong>Australian</strong> decision makers.<br />

The USES-LCA toxicity model has been disaggregated into distinct urban, regional and remote compartments;<br />

so as to better represent the highly heterogeneous population distribution on the <strong>Australian</strong> continent. This<br />

has a significant effect on the calculation of human exposure to airshed emissions, demonstrating the<br />

importance of choosing an appropriate level of spatial resolution when using simplified box models for this<br />

purpose. The modified fate and exposure factors were combined with an estimate of Australia-wide airshed<br />

emissions, identifying a number of industry sectors that might be responsible for particularly high levels of<br />

human health hazard as a result of chemical pollution. Additional modifications were made to improve the<br />

modelling of freshwater and terrestrial ecotoxicity in the <strong>Australian</strong> version of USES-LCA - incorporating the<br />

most recent science on metals speciation, and providing the flexibility to take different methodological<br />

approaches to pesticide effect modelling. The model was then applied to estimates of chemical emissions to<br />

terrestrial and aquatic landscapes across the country, generated using the best available data from a wide<br />

variety of sources. The results illustrate the importance of both these methodological developments, and<br />

highlight the need for more robust and consistent data collection on emissions to land and water.<br />

Ms Sue McAvoy<br />

PhD Student, University of Queensland<br />

Working Title: Using LCA to assess the impact of climate change policy on Red Meat Processing<br />

This paper presents work in progress on a thesis that uses partial life cycle assessment (LCA) as part of an<br />

investigation to assess the effectiveness of the federal government's climate change policy. It focuses on red<br />

meat processing (RMP), which is a trade-exposed industry falling outside of the emissions intensive cut-offs for<br />

direct assistance. Australia’s largest RMP Company will be used as a case study.<br />

It will test whether the <strong>Australian</strong> carbon accounting framework, legislation and associated regulations, which<br />

collectively underpin the carbon tax policy, will enable the “activity” of red meat processing to lower its carbon<br />

footprint and remain competitive. The research responds to a concern that Australia’s Red Meat Processors<br />

are price takers of a world commodity price that is non-carbon inclusive and must compete globally with<br />

international processors who are either not subject to a carbon tax or are adequately shielded. Two<br />

methodologies will support this research – LCA and systems dynamics. Firstly, the partial LCA will measure the


carbon footprint of the abattoir process (with a functional unit of 1 tonne of HSCW), “before” and “after” the<br />

company’s response to climate change policy.<br />

This will test the success of the Clean Energy Legislation as a policy mechanism promoting the adoption of<br />

mitigation strategies that lower the company’s overall carbon footprints and transition them to low carbon<br />

technologies. It will also provide a reliable carbon footprint to potentially assist the processor in making<br />

informed decisions about practice changes and proposed mitigation projects. Secondly, the systems dynamics<br />

approach will complement the LCA by simulating the potential impacts of the government’s choice of policy on<br />

the competitiveness of red meat processing. This paper will describe a novel application of LCA for assessing<br />

the implications of government policy on business activities. While the work presented focuses on the<br />

<strong>Australian</strong> meat industry, the approach could also be applied to other business activities.<br />

Miss Caoilinn Murphy<br />

Project Engineer, FSA Consulting<br />

Co Authors - Mr Stephen Wiedemann, Senior Agricultural Scientist, FSA Consulting, Mr Eugene McGahan,<br />

Principle Consultant, FSA Consulting.<br />

Consumptive and stress weighted water use in <strong>Australian</strong> conventional and alternative breeder<br />

and grower/finisher pork systems<br />

Worldwide, there is increasing concern about the sustainability of water use in agriculture. At present, there is<br />

a distinct lack of robust studies focussing on water consumption and scarcity in <strong>Australian</strong> agriculture.<br />

This “cradle to farm gate” study is the first analysis of consumptive and stress weighted water use for<br />

<strong>Australian</strong> pork using a LCA approach. Five supply chains were investigated, consisting of a single large piggery<br />

(>5000 sows) or a cluster of smaller piggeries (100-1000 sows) in a given location. The supply chains were<br />

located in south-eastern Queensland, southern NSW and Western Australia. Three housing systems with<br />

different levels of water use for manure management were investigated: conventional housing with effluent<br />

flushing, housing on deep litter and outdoor housing. Consumptive water use ranged from 34.5 L / kg LW (WA<br />

outdoor-deep litter) to 150.5 L / kg LW (QLD large conventional). This was primarily influenced by housing<br />

type, the inclusion of irrigated feed products in the diet and losses associated with the water supply system.<br />

The QLD large conventional piggery combined all three factors, with evaporation from the water supply<br />

contributing 33% of overall water use. To compare differences in water use by housing type, the effect of<br />

water supply system and irrigated feed products were removed. Outdoor breeding compared to conventional<br />

breeding showed that water consumption decreased by 24% using the outdoor system. Compared to deep<br />

litter, conventional growing-finishing required 64% more water, which was attributed to differences in<br />

cleaning water requirements. Stress weighted water use was analysed for conventional breeding and ranged<br />

between 3.1 (WA) and 148.7 (NSW) L H2O-e / LW. For all piggeries except NSW, water use expressed on a<br />

stress-weighted basis was considerably lower than consumptive water use, with the most noticeable change<br />

for the QLD supply chain, highlighting the importance of region for assessing the impact of water use.


Miss Aurelie Perrin<br />

CIRAD, UPR Hortsys, Elsa team<br />

Co Authors - Mitchell Burns, UPR Hortsys, Elsa team Cirad, Philippe Roux, UMR ITAP, Elsa team, Irstea,<br />

Claudine Basset-Mens, Elsa team Cirad<br />

Do the current life cycle inventory (LCI) methods adequately account for the life of a pesticide in<br />

horticultural production systems? A review.<br />

Two concerns arise from the use of pesticides in horticulture: the occurrence of their residues in fresh produce<br />

and the potential for the contamination of non-target ecosystems. Pesticides therefore require special<br />

attention in horticultural <strong>Life</strong> <strong>Cycle</strong> <strong>Assessment</strong>s (LCAs). Through a conceptual assessment of the life of a<br />

pesticide, we present critical analyses of the horticultural LCA case studies and emission estimation methods.<br />

These critical analyses identified that the system boundaries of the reviewed case studies were typically not<br />

clearly defined with respect to classical LCA definitions. Unclear boundary definitions were identified to also<br />

have implications for the methods used for estimating the emissions of pesticides or impacts (LCIA), which is<br />

consistent with a previous review. The methods that are available for estimating the emissions of pesticides<br />

showed the PestLCI model (Birkved and Hauschild 2006; Dijkman et al. 2012) to be the most comprehensive in<br />

theory.<br />

However, though this model exhibited the greatest complexity, it requires a large dataset and lacked scope for<br />

application in horticultural greenhouses. The latter was an important consideration when selecting a relevant<br />

pesticide emissions model for harmonised comparisons in LCA for horticultural products. We present the<br />

results from this critical review and propose further steps to improving the transparency and feasibility in<br />

applying relevant pesticide emission techniques in contrasted horticultural cropping situations.<br />

Birkved M, Hauschild MZ (2006) PestLCI - A model for estimating field emissions of pesticides in agricultural<br />

LCA. Ecological Modelling 198 (3-4):433-451. doi:10.1016/j.ecolmodel.2006.05.035<br />

Dijkman TJ, Birkved M, Hauschild MZ (2012) PestLCI 2.0: a second generation model for estimating emissions<br />

of pesticides from arable land in LCA. The International Journal of <strong>Life</strong> <strong>Cycle</strong> <strong>Assessment</strong> 17 (8):973-986.<br />

doi:10.1007/s11367-012-0439-2<br />

Ms Julie Sandilands<br />

Solution Manager, PE INTERNATIONAL<br />

Co Authors - Dr Markus Reuter, Director - Technology Management, Outotec Oyj, Dr Antti Roine, Senior<br />

Research Metallurgist, Outotec Oyj.<br />

Metals production sustainability and lifecycle evaluations<br />

For new designs of metallurgical plants and processes it is very important to get a “real time” sustainability<br />

assessment and life cycle evaluation during the design phase to avoid arising cost at a later stage because of<br />

not considered environmental impacts during production. Outotec and PE INTERNATIONAL AG developed a<br />

new software interface for this purpose, based on extensive research in this field. In the presentation the


advantages and benefits of such a “real time” LCA for the design of a selected copper plant will be shown in<br />

comparison to the world average LCA dataset developed from the industry association.<br />

The integration of LCA and plant and process design allows users to develop product and process modelling<br />

simulations and scenarios using a life cycle perspective. In addition, Original Equipment Manufacturers (OEM)<br />

and businesses will be able to plan their operations and make material decisions based on the sustainability<br />

and life cycle information of current and future metal manufacturing scenarios and their environmental<br />

impacts. This will help to lower the environmental footprint of these products and production facilities.<br />

Outotec’s HSC Chemistry software is designed for various process simulation and modelling applications. HSC<br />

consist of 24 calculation modules and 12 extensive databases.<br />

These tools help to design technically viable and effective processes. These process models give the initial data<br />

for the process design, engineering and automation. The new solution will make possible to develop industrial<br />

ecosystems, which are based on sustainable recycling and fruitful symbiosis between the processes, plants and<br />

whole society.<br />

Miss Helene Sterzik<br />

PhD Student, Massey University<br />

Co Authors - Associate Professor Sarah McLaren, Associate Professor, Massey University, Professor Jim Jones,<br />

Professor, Massey University.<br />

The Carbon Footprint of Biochar Systems: an Absolute Contribution to Climate-Change Mitigation<br />

Biochar is charcoal used for application into soils to store carbon and to improve soil functions. Since the<br />

carbon in biochar can take hundreds or thousands of years to decompose, the incorporation of biochar into<br />

soils is being promoted as a climate-change mitigation strategy. Furthermore, the recovery of by-products,<br />

syngas and bio-oil, for fossil fuel substitution offers additional opportunities to reduce greenhouse gas<br />

emissions. Since biomass resources are limited, the trade-offs associated with alternative end uses of biomass<br />

need to be explored using a system expansion perspective, particularly when considering policy options to<br />

encourage or discourage the production and use of biochar.<br />

The goals of this carbon footprint study are: 1) to compare reference scenarios with future alternative<br />

management scenarios for three biomass feedstocks selected as case studies (prunings from apple orchards,<br />

logging residues, and cereal straw); and 2) to inform policymakers on the best use of biomass to mitigate<br />

climate change. The functional unit is ‘the management of one tonne of fresh biomass’. The alternative<br />

scenarios considered in each case study, however, deliver additional functions (e.g. energy production and soil<br />

quality).<br />

Therefore, system boundaries have been expanded for each reference scenario to include background<br />

processes required to achieve the functions provided by each scenario under analysis. The results of the<br />

carbon footprint of three biochar systems will be presented in relation to alternative biomass management<br />

options.<br />

This comparative assessment is different from the approach taken in existing carbon footprint studies of<br />

biochar as the climate-change mitigation potential of biochar is recognised as one alternative use amongst<br />

others, and with consequences for other activities in the economy.


Dr Daniel Tan<br />

Senior Lecturer, University of Sydney<br />

Co Authors - Dr Philippa Brock, Leader, <strong>Life</strong> <strong>Cycle</strong> <strong>Assessment</strong>, Department of Primary Industries, Dr Nilantha<br />

Hulugalle, Principal Research Scientist, Department of Primary Industries.<br />

<strong>Life</strong> cycle assessment of cotton-corn farming systems in the Namoi Valley<br />

LCA is an approach which is commonly applied to identify the process through which greenhouse gas<br />

emissions arise from agricultural production systems. It has been applied to determine pre-field and in-field<br />

emissions associated with individual practices and inputs. Greenhouse emissions were determined for the<br />

lifecycle of different cotton and corn production systems in the Namoi Valley, Australia.<br />

A “cradle-to-gate” analysis was conducted which considered all the impacts from growing a crop (e.g.,<br />

fertiliser, crop establishment and maintenance) based on data from four co-operating growers in the lower<br />

Namoi (two dryland, two irrigated) and a long term experiment at the <strong>Australian</strong> Cotton Research Institute<br />

(ACRI) at Myall Vale. Actual crop history records were obtained by interviewing farmers face-to-face with a<br />

pre-developed questionnaire to gather the necessary crop information such as crop rotations, machinery use<br />

for the crop, products and rates used for the crop in selected fields.<br />

These data formed the basis for introducing upstream data about the production of inputs and calculated data<br />

about in-field emissions to enable analysis using the computer software Simapro. Greenhouse gas emissions<br />

averaged 0.34 kg CO2-e for the production of 1 kg of cotton lint and seed for both irrigated and dryland cotton<br />

and 0.33 kg CO2-e for the production of 1 kg of corn. The emissions profile for irrigated cotton and corn grown<br />

in rotation included N2O directly from fertilisers (35.3%), production of fertilisers (14%), CO2 emissions from<br />

the use of nitrogenous fertilisers (11.6%), N2O emissions indirectly via leaching (7.2%), N2O emissions via<br />

volatilisation and indirectly from fertiliser re-deposition (3.8%), CO2 emissions from on-farm combustion<br />

(7.8%) and irrigation (9.2%). The emissions are dominated by the production and use of nitrogenous fertilisers,<br />

at 72% for cotton and 65% for corn. Replacing these fertilisers with biologically fixed N using a legume-based<br />

system may reduce these emissions.<br />

Dr Pep Turner<br />

Ecologist, School of Geography and Environmental Studies, University of Tasmania<br />

Co Authors -<br />

Accounting for biodiversity in <strong>Life</strong> <strong>Cycle</strong> Impact <strong>Assessment</strong>s of forestry and agricultural systems<br />

There are currently no globally appropriate means of assessing biodiversity within the LCA framework. A new<br />

project is under way to test a new method proposed to address the issue of accounting for biodiversity<br />

impacts in LCA. The approach relies on literature review and expert opinions through a series of questions<br />

which aim to encapsulate the main issues relating to biodiversity within a disturbance impact framework.<br />

This project will test the applicability of this model using two forest industry case studies (native and<br />

plantation forestry) and a case study from the agricultural sector (cropping). Using a series of quantitative


questions, biodiversity impacts are estimated for each taxonomic group (e.g. flora, mammals, diurnal birds,<br />

frogs and invertebrates) and then scaled to an overall biodiversity measure.<br />

In this talk we will provide some background on the proposed method, outline the current project and some<br />

preliminary results based on an initial literature review and a survey of ecologists to refine proposed questions<br />

to be addressed by the method.<br />

Dr Mingjia Yan<br />

Project Engineer, FSA Consulting<br />

Co Authors - Prof Nick Holden, University College Dublin, Mr Stephen Wiedemann, Agricultural scientist, FSA<br />

Consulting.<br />

<strong>Life</strong> <strong>Cycle</strong> <strong>Assessment</strong> of Irish milk production<br />

<strong>Life</strong> <strong>Cycle</strong> <strong>Assessment</strong> (LCA) is an assessment tool for evaluating the environmental performance of products<br />

through their whole life cycle (i.e. production, use, disposal or recycling). In recent years, LCA has been applied<br />

to milk production worldwide, with the LCA interpretation of greenhouse gas (GHG) emissions also being<br />

referred to as carbon footprinting.<br />

The objective of this paper was to summarize the results of a PhD study on (1) evaluating existing LCAs of milk<br />

production in Europe and finding the mainstream approaches, major contributors to impacts, and suggestion<br />

of mitigations; (2) analysing the effect of sward management tactics on the CF of Irish milk production at a<br />

research farmlet and (3) analysing the effect of farm management strategies on carbon footprint and land use<br />

for milk production in commercial farms with a twelve-month farm survey. It was found that direct comparison<br />

of milk LCAs was difficult due to technical issues, arbitrary choices and inconsistent assumptions. At the<br />

research farmlet scale, the clover based sward had 11 to 26% lower carbon footprint compared with the<br />

fertilizer based sward.<br />

At commercial farms, milk output per cow, allocation between milk and live weight export were found to be<br />

important factors for carbon footprint. Fertilizer N rate, milk output per cow and allocation between milk and<br />

live weight export were influential on land use, and effective sward management of clover appeared to lower<br />

the carbon footprint but increased direct (on-farm) land use. The experience gained through the above<br />

research is expected to provide useful knowledge to agricultural LCAs in Australia.

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