Lean Cities - Low Carb Materials & the Role of Restorative Sustainability
David Baggs, CEO and Technical
Director
Summary
The current focus on energy supply sources in
relation to the greenhouse impacts of current cities is only the
tip of the iceberg in mitigating the societal impacts of climate
change and resource utilisation. Just as we count carbohydrates to
lose weight, our over-bloated cities and individual lifestyles need
to go on a different kind of 'low carb' diet. Instead of counting
carbohydrates, we need to count carbon outputs.
While this might smack of a single focus on energy once more, we
need to realise that consumption per se is a major factor
in itself. Just as we talk about the need for balanced lifestyles,
we need to re-double and quadruple our focus on creating and
utilising eco-balanced products, materials and technologies. This
involves not just energy and resource use but the whole process of
how we create and re-create the built environment.
This paper looks at what it will take to make eco-balanced
cities and eco-balanced products that are engineered with multiple
life-cycles considered before sale and how they can be re-use
enabled by information flow into design, construction and higher
levels of activity in physical re-sculpting at end of use. The
Concept of Restorative Sustainability and the
ecospecifier website as a tool is presented and
case study solutions provided.
1. Introduction
According to Global Footprint Network, as a global society, our
planetary impacts ceased to be able to accommodate sustainably
sometime around 1985. At current growth and consumption rates, if
all societies choose to develop in the same way as Australia, the
US and many other 'developed' nations' we will need up to the
equivalent of 2-3 planetary ecosystems to support our needs and
demands. 'Developed nations', our Cities, our lifestyles and
attitudes are the drivers of the biggest challenge humankind has
ever faced and it is entirely of our own doing.
The current attention being placed on global warming and the
need to reduce fossil fuel energy consumption is being turned into
a political, spin-managed, sound-bite driven issue that except for
Nature's constant reminders, whether by storm (Hurricane Katrina -
St Orleans 2005, Cyclone Larry - Australia, 2006),
Australia's 'worst drought in 1000 years' and recent flooding
in Australia, would become yet another over simplified media
message that soon becomes lost in the morass of self interested
lobby-group counter message and mis-information campaigns
only to be dropped when the public's attention wanes. As cynical as
this sounds, recent history has shown this to be only too true with
the secret funding of mis-information campaigns by oil companies
and the 'Carbon is Life' mass media advertising in the US launched
to attempt to counter the public influence of Al Gore's movie 'An
Inconvenient Truth' in late 2006.
While global warming and climate change have become big news now
and likely to become bigger with the likes of Rupert Murdoch and
News Limited's conversion to active support of mitigating climate
change by going 'Carbon Neutral', there is a real need to look
beyond the superficial sound bites and the politically driven
mantra that climate change is largely due to the obvious energy
consumption of electricity and transport.
Digging deeper we see that while the energy consumption of
electricity and transport in homes and businesses is obviously a
major issue there is significant carbon other resources embodied in
the actual buildings, infrastructure and lifestyles as well.
There are also more fundamental drivers underlying this energy
consumption that are not being addressed. The 'great unsaid' in the
debate to date is consumption in general i.e. the insatiable drive
to own more and more, bigger and better, newer and different, the
desire of developing nations to emulate our profligacy and more
fundamentally, our growth economic models that recognise all
economic activity as 'positive' (even if it is rebuilding from
natural disasters or cleaning up after toxic spills that have
devastating environmental consequences) and still more
fundamentally, population growth itself. There is a dire and
increasingly pressing need for us to look at the way we measure our
success.
"The economy is a wholly owned
subsidiary of the environment, not the reverse."
Herman Daly, The ex Chief Economist for the World Bank, Quoted in
'The Age' May 4 2007
As more and more global population drifts into cities to attempt
to find shelter, stability, and a more prosperous life, there is
also an increasingly strong, commercially driven, acquisitive,
'Home Beautiful-esqe lifestyle' behaviour that is seemingly fed by
an upward spiral of media goading.
While it takes massive amounts of energy to run cities, it also
takes vast amounts of energy to build cities, acquire the resources
to fit them out, move about in them, provide infrastructure,
resource, feed, clean, maintain, demolish and renew them. Whether
it be in building new or refurbishing homes, commercial or
industrial buildings, or our commitment to buying the 'latest and
greatest', there is a need for us to change our behaviour about
what we design, construct or buy, how we use, maintain and even
dispose of all personal and societal 'acquisitions'.
To date, when considering how we might reduce impacts, we have,
importantly tended to focus on reducing future impacts by the now
common '3Rs' catch phrase of actions, 'Reduce, Re-use, Recycle' and
a range of variants promoted by such pertinent books as Lovins et
al in 'Factor Four - Doing More with Less', William McDonough and
Michael Braungart's 'Cradle-to-Cradle', Paul Hawkins 'Natural
Capitalism' and Janine Benyus 'Biomimicry'. Focussing on how we
reduce past impacts has to an extent been left in the margins and
to nature. It has been assumed that 'if we reduce our impacts,
nature can look after herself and will recover in time'. While the
'Reductive Sustainability' most discussed in the above works
including initiatives like incorporating past waste into new
products or 'doing twice as much with half as much' (Factor
Four), have a critically important role in promoting sustainability
up to a point, how can we create a net positive impact to redress
the past if we only ever reduce a future negative impact?
Along with all the necessary strategies dealt with in the above
works, there is a need for an additional 'enhancing nature' focus.
A focus on how we can begin to pro-actively support nature where
possible, to create initiatives that have a 'net positive' impact
that 'put back' more than they 'take out' of our 'Natural
Capital'. These are initiatives that can be described as
'Restorative Sustainability'.
This paper looks at the role of cities in our un-sustainability
and explores the full spectrum of strategies and solutions as to
how cities might become a pathway towards a 'Low Carb' future and
how, using carbon as a proxy, we can move towards a more
sustainable future with cities as part of a '5Rs' solution.
2. The 'Inconvenient Truth'
This paper will firstly analyse the major issues and actions
within cities generating impacts that are accelerating our
unsustainable demands on our Natural Capital, then look at
the important 'Reductive Sustainability' actions that can be
implemented to reduce future impacts. It will then investigate a
definition of what makes something 'restorative' then present some
examples of 'Restorative Sustainability' initiative and how cities
can be used as part of the solution.
2.1 The Issues
When we consider the impacts of cities and the societies that live
in them, it is useful to understand where the impacts are being
generated and more importantly, where the potential savings are.
Most studies, such as the Vatenfall study cited below and
illustrated in Figures 1 and 2, when reviewing these impacts, only
review recurrent operational impacts:
The buildings sector generates
8.2 GtCO2 or 21% of total global CO2e
emission; 8% through emissions from primary fuel types (coal, gas,
oil), 13% generated from power production to meet electricity
demand from residential and commercial buildings. The residential
subsector, while contributing 76% of consumption, contributes 63%
of emissions, while the commercial sector, while generating 24% of
consumption contributes to 37% of emissions; the difference in
emission intensity is driven by different energy mixes. The
developed world (EU + US/Canada) generated overall 63% of total
anthropogenic CO2 emissions in 2002. Energy consumption
by this sector is expected to grow 50% by 2030 with a 70% increase
in emissions to 14 GtCO2e driven partly by a fuel shift
towards electricity. (Vattenfall 2007).


Figure: 1 Global greenhouse emissions by sector
Figure 2: Global greenhouse by End Use
2002 (Vatenfall 2007) 2002 (in Vatenfall 2007)
Furthermore, seen from figure 3 below, the growth in this sector
has been astronomical over the last 50 or so years.

Figure 3: The growth in US materials consumption by sector
1900-1995 (Matos & Wagner, 1998)
A significant amount of energy is 'hidden' and largely ignored
within these materials used in the fabric of cities, buildings and
their infrastructure. The energy embodied within materials,
products and technologies is a key factor in the carbon footprint
of cities as a result of their raw materials procurement,
manufacturing and packaging, is being overlooked in the macro
studies of potential CO2e savings.
Buildings account for one sixth
of the world's fresh water withdrawals, one quarter of its wood
harvest, and two fifths of its material and energy flows… Building
and construction activities worldwide consume three billion tons of
raw materials each year or 40 per cent of total global use.
(Roodman & Lenssen 1995).
When we look at the relevant proportions of operational vs.
embodied energy in the residential sector, as exemplified by the
analysis of a typical household in Figure 4, and a 40 year
analysis of 40,000m2 office building in Figure 5, the
majority of energy is consumed in operational energy. However, we
also see a significant proportion of overall energy resulting from
embodied energy, not just of the buildings themselves but of also
of recurring consumption as part of the overall 'lifestyles' of
occupants.
In the residential sector this is seen as a personal or family
'lifestyle' and in the commercial sector the 'lifestyle' and
purchasing patterns of companies result in the second highest
embodied energy factor being the 'churn' of furniture, fittings and
finishes due to short leases, corporate image and fashion design
trends.
Figure 4: The proportion of energy
attributable to initial, recurring, and operational energy of
residential households (Treloar et al, 2000).
Figure 5: The proportion of energy attributable to
initial, recurring, and operational energy of a 47,000m2
commercial office building over 40 years. (Treloar et al,
1999).
What's more, as can be seen in Figure 6, in recent times we are
using less and less renewable sources of materials (which tend to
be low embodied energy) in favour of non-renewable materials.
Figure 6: The growth in non-renewable materials
1900-2000 (Wagner, 2002)
The real impacts of Electricity
There is also a need to look below the superficial media headlines
and stop sweeping 'inconvenient' and unpalatable truths under the
metaphorical carpet. The focus on global warming due to
carbon emissions is actually a little like the proverbial 'canary
in the cage'. As seen above, electricity emissions are a major
source of CO2, (and can be seen as proxy for the
following impacts) but we conveniently ignore its other major
environmental and human health impacts. Mercury is a highly toxic,
bio-accumulative heavy metal, yet nearly 45% of emissions of
mercury (66 tonnes) to the environment in the US alone are from
electricity generation (calculated from Wagner 2002, pg.12). Other
by-products emitted to air that create significant health impacts
include PM 10, PM 5 and PM 2.5 fine asthma and cancer-causing
particulates, photochemical smog producing, NOx and
SOx, sulphuric acid, chlorine, (Hunwick Consultants
2007), 43% of all mercury, 42% of all cadmium, 38% of all cobalt,
31% of all antimony (Environment Australia 2002) and vast volumes
of radioactive ash in Australia.
Heat Islands: The Urban Negative Feedback Loop
A major negative global warming 'feedback loop' has
emerged in the way that our cities have now been shown to heat up
and retain heat compared to surrounding less densely settled
surrounding areas. This 'urban heat island' effect has been
identified around the world and most recently in Melbourne
Australia. Melbourne has been shown to be on average
3.5-4.5oC hotter during summer evenings and up to
10.0oC hotter on still summer evenings. Obviously with
more and more people moving into cities, as it gets hotter, more
air conditioning is installed and it will be run more often,
creating the 'negative feedback loop' that then generates even more
CO2. This effect has become so extreme in Tokyo, that
the city has, since 2000 mandated the use of green roofs on
public buildings over 250m2 and private buildings over
1000m2.


Figure 7: Isothermal net graph of Melbourne, Australia's urban
heat island effect by University of Melbourne. (Morris 2000)
Above: a diagramic profile of and urban heat island - (Rosenfeld
et al, 1997)
3. How we can 'ECOBALANCE' OUR
CITIES
In beginning to look at how we can ecobalance our cities much
has already been done to analyse what benefits can be found. In
Figure 8 below, it can be seen that of the 26.7 gigatonnes of
potential annual savings of carbon emissions costing under
€40/tonne, nearly 14% are in building alone and the influence of
the buildings, materials, infrastructure and consumption can be
seen throughout the rest (McKinsey 2007).
Figure 8: The abatement potential of greenhouse gas emissions
for carbon cost under €40/tonne
The recent Vatenfall study showed a total of 3.7
GtCO2e of low-cost abatement options have been
identified - 3.0 GtCO2e in the residential sector and
1.3 GtCO2e in the commercial sector - which would hold
emissions growth to 26% for the Construction sector by 2030.
Heating and ventilation including building envelope improvements,
water heating and air conditioning provide the largest potential
benefits for both residential and commercial buildings,
contributing a total of 2.3 GtCO2e (62%). Lighting is a potential
contributor mainly in residential building, potentially leading to
a 0.3 GtCO2e emission reduction. Improving other appliances and
reducing standby losses yields another 1.1 GtCO2of abatement
(Vattenfall 2007).
3.1 The Role of Materials & Design: 'Reductive
Sustainability' as Part of the Solution
If we are to reduce CO2 by 60% by 2050 to stop global
warming rising beyond 1oC to the 2-2.5oC that
current emissions rates would generate (Raupach 2007), further
economical savings need to identified. The role of materials has
been highlighted in the above data and provides ready evidence that
materials have a key role to play. Key issues identified to this
point are:
- Embodied Energy
- Energy Consumption
The key next question is now - how can cities and their
material's potential as part of the solution be realised? There are
a number of key strategies where materials selection and the ways
in which they are incorporated into buildings can provide benefits
with little, or often no cost, sometimes even with cost savings.
These focus on reducing impacts by design, cleaner production
strategies, materials selection and evaluation strategies. They can
all be categorised as falling within the concept described by this
author as 'Reductive Sustainability' as the following strategies
illustrate:
Materials choice: There is much to be gained
from identifying the 'best of class' within any materials
categories. As can be seen from the comparative embodied energy
data of different residential building assesmblages in Figure 9
above, there can be up to nearly a 1900% difference between the
best and worst performers in some categories

Figure 9: Mean value for global warming potential and the
highest and lowest value within the range for residential
assemblages (Walker Morison, 2007)
Industrial Ecology & 'Cradle to Cradle':
Since the early nineties, various authors including Frosch (1992),
Allenby (1992) and Ayres (1994) have introduced the concept of
industrial ecology where technical cycles are designed to mimic
natural organic cycles in nature, where there is no waste and all.
McDonough and Baungart (2002) coined the terms 'Waste equals Food'
and 'Cradle to Cradle' to describe how the carbon (and ecological)
footprint of materials products and technologies (and cities) need
to be re-designed to ensure that the materials inherent in them and
their production and manufacture systems will allow all elements or
sub-components of any product on deconstruction, to fit within one
(or possibly both) of these cyclic
production/consumption/remanufacture/consumption systems. To ensure
this approach works products need to be designed for
disassembly.
Design For Disassembly (DfD): Manufacturers and
all sectors of the built environment including designers,
engineers, specifiers, builders and developers need to design,
manufacturer and incorporate materials, products and technology in
cities (and the built environment generally) in ways that
facilitate DfD, or at the very least do not hinder it. Only in this
way can we be assured that once we have created a resource, that it
is not lost and can enter the 'Cradle to Cradle' re-cycling loops
and not need to be replaced with virgin resources at end of first
or subsequent use.
Design For Climate (DfC): Also known as
'passive solar' design, this term is not used as much recently as a
result of the erroneous perception that it does not relate to
warmer climates. DfC means designing buildings and incorporating
materials in such as way as to maximise the use of environmental
heat sinks and sources in the heating and cooling of the internal
spaces for thermal comfort and daylighting. The simple orientation
and appropriate use of windows, shading, insulation, ventilation
and thermal mass is sufficient in many climates to produce
buildings that require no heat or cooling and little artificial
lighting energy. DfC is the most powerful design strategy we have
to minimise the carbon footprint of operational energy consumption
in buildings. We are yet to see zero-carbon footprint buildings
mandated (although the UK is planning to) although they are
technically feasible in most climates.
Buy Recycled: One of the most important
initiatives to ensure that the carbon footprint of materials are
minimised is the make sure that products being purchased and
specified already contain recycled content. While being recyclable
is important, first priority should be given to those products that
already contain high levels of preferably, post consumer content
and have constituent componentry clearly identified to facilitate
the next recycling cycle.
Design for Durability: The single most
important issue in life-cycle impacts of buildings and materials is
durability, providing the carbon payback period is more or less,
short term. It is an unfortunate reality than many (not all) highly
durable materials are high in embodied energy. For this 'carbon
investment' an 'avoided energy' return needs to be calculated, i.e.
are the savings that accrue as a result of a material or product's
durability due to avoided maintenance or unnecessary replacement,
create more carbon savings than the initial investment, over a term
of preferably less than 10-40 years (given the 60% reduction target
by 2050 to contain global warming to rising beyond 1 degree or
less). The key action here is for designers to;
Start by designing with the
end of life in mind. If it's not reusable or
recyclable to a high value, it's not sustainable. This design
approach drives design re-thinking throughout the project,
requiring the design team to think 'up' from the construction of
building elements to the whole building. (Walker Morison,
2007)
Biomimicry: By using nature as a model we are
finding amazing ways to reduce the impacts of how products are made
and recycled. Janine Benyus in her 1997 book looks at case studies
of how products are being designed using natural criteria and
processes.
Nature as
Model. Biomimcry is a new science that studies
nature's models and then imitates or takes inspiration from these
designs and processes to solve human problems, e.g. a solar cell
inspired by a leaf.
Nature as
Measure. Biomimicry uses an ecological standard
to judge the "rightness" of our innovations. After 3.8
billion years of evolution, nature has learned: What works.
What is appropriate. What lasts e.g. high durability plastics
made like abalone lucre at room temperature.
Nature as
Mentor. Biomimicry is a new way of viewing and
valuing nature. It introduces an era based not on what we can
extract from the natural world, but on what we can learn from
it.e.g. natural reedbed waste treatment systems instead of chemical
dosed electro-mechanical systems.
Key lessons that can be drawn from this approach relate to how
products are evaluated, how to choose between alternatives and how
we integrate industrial ecology cycles, ensuring that the materials
and technology with the lowest carbon and toxic life-cycles and
biodiversity impacts prevail. Working with nature to restore
function is implicit in the concepts promoted by biomimicry,
however, there is no explicit focus on restorative solutions.
Dematerialisation & Factor
Four+:
Dematerialisation is about increasing the efficiency of
materials e.g. the Weisacker and Lovins' Factor Four: Doubling
wealth, Halving Resource Use' is about 'doing twice as much with
half as much'. It is essentially an economic concept wherein
technologies and processes are developed to use a lower amount of
resources to meet the human need for goods and services (increased
resource efficiency sometimes also known as eco-efficiency), it
enables technology and the economy to act as efficient driving
forces (market mechanisms, financial incentives). Dematerialisation
is also an issue in building design where efficient use of
resources can be influenced by structural design efficiencies,
detailing practices and the level of finish. As an extension of
this concept, The Factor Ten Institute believes that for planetary
sustainability, developed nations should be targeting Factor Ten
efficiencies in dematerialisation (Schmidt-Bleek).
Renewable Inputs: Subject to where and how
products are manufactured, transported and used and hence the
extent of the importance of durability, the use of renewably
sourced products can have a major impact on reducing overall
environmental and carbon impacts. Some renewable materials are
highly durable, e.g. Western Red Cedar. Renewable materials can
still be sourced in ecologically unsustainable ways, so care must
be exercised that resources are sourced sustainably e.g., by
recognised 3rd party sustainability assessment systems
such as the Forest Stewardship Council sustainable timber
certification scheme or other third party evaluation process.
Identify Carbon Sinks: Some products that bind
large amounts of carbon in the materials themselves during use are
called carbon 'sinks'. Provided the materials are long lived, there
are significant benefits in starting to increase the use of
products that are high density carbon sinks. As shown in figure 10,
even among the renewable materials field there are claims of
preferential carbon sink benefits beginning to emerge. How these
products are dealt with at end-of-life then becomes doubly
important if the embodied carbon is not to be released into the
atmosphere.

Figure 10: Showing the claimed carbon sink benefits of a natural
rubber based flooring over other natural and synthetic floor
coverings (source: Dalsouple International)
Embodied Water: Another emerging issue due to
both lack of the resource as a result of global warming and
the negative global warming impacts of the embodied energy of water
is the embodied water content of products. The impacts of water
consumption in both manufacture and maintenance will become
increasingly important as the focus on water availability
increases. Crawford and Treloar (2005) showed that the embodied
energy content of a 11,200m2 office building ranges from
6.3 kL/m2 using process analysis, to 54.1
kL/m2 using Input-Output-based hybrid analysis (that
includes National Account data including financial and
infrastructure system inputs). As occurs using the same comparison
process for embodied energy, this difference in values can be
attributed to the truncation typically associated with process
analysis.
3.2 Materials & Design: 'Restorative Sustainability'
completing the solution
As discussed in the Introduction, the 'Reductive Sustainability'
initiatives discussed above have a critically important role in
promoting sustainability up to a point. If we reduce our demands on
nature's systems and living resources, there is no doubt that
regeneration will occur to some extent.
The key question is 'can nature replenish herself in the context
of explosive consumption, ongoing population growth and the
inexorable growth of cities where impacts are concentrated and
populations insulated from their impacts?' The current
collapse in the integrity of ecosystems globally is indicative that
this is highly unlikely. The plain likelihood remains that we will
be unable to create enough relaxation in the societal demands we
place on natural capital to allow adequate natural recovery in
currently highly stressed, damaged or destroyed ecosystems to
ensure sustainability in the long term if we only ever reduce
future negative impacts without redressing past impacts.
Along with all the necessary strategies dealt with above, there
is a dire need for an additional 'enhancing nature' focus. This
focus on pro-actively supporting nature requires us to where
possible, create initiatives that have a 'net positive' impact that
'put back' more than they 'take out' of our natural capital.
If we are to restore natural capital pro-actively, then as part of
every possible project we need to integrate initiatives that
'Repair and Restore', such initiatives are described by this author
as 'Restorative Sustainability'. However, before we can define what
constitutes 'net positive' repairing and 'restorative' solutions,
we firstly need to identify what actually constitutes
sustainability from a scientific viewpoint.
3.3 Defining Sustainability
While there are numerous literary definitions of sustainability
per se, such as the Brundtland Commission's and
Australia's National ESD Policy, that focus on mitigating impacts,
maintaining intergenerational equity and working with the
'Precautionary Principle', these are very broad overarching
principles that do not really help us actually identify and
implement actual strategies. In fact, we do not really have a clear
idea what a truly sustainable city actually looks like or how it
can operate given the extent of existing development infrastructure
and systems. There is no doubt that a truly sustainable city will
of necessity be radically different to what we are doing now - not
just from a physical standpoint, but from a systems (transport,
services, energy etc) and societal standpoint as well. According to
the Australian CSIRO, the 3 'Sustainability Wedge' strategies
required to deliver sustainability are, as seen in Figure 11:
- A values based decline in consumerism
- A dematerialisation of product and services; and
- Closing the loop in industrial ecology.


Figure 11: CSIRO vision of unsustainability and its impacts
(top) and 3 proposed interventions necessary to deliver
sustainability.
These strategies provide some general guidance on the directions
we need to move to redress unsustainability. However the Natural
Step Institute has developed 4 System Conditions for Sustainability
that define sustainability from a scientific standpoint:
- Substances from the lithosphere (within the earth) must not
systematically increase in the ecosphere;
- Substances produced by society must not systematically increase
in the ecosphere;
- The physical basis for the productivity and diversity of nature
must not be systematically deteriorated;
- Fair and efficient use of resources with respect to meeting
human needs.
These system conditions need to form the underpin to our
assessment of products, services and strategies on the broadest
scale possible.
3.4 Defining 'Restorative Sustainability'
If we are to solve the looming global warming crisis, we need
all the tools in our armoury to be fully primed and must be ready
to actively implement them.

Figure 12: The full complement of 'Sustainability Wedge'
Initiatives required to deliver sustainable, lean, ecobalanced
cities (adapted from Heij 2002)
In addition to the 3 sustainability wedges adapted by Heij
(2002) from Raskin (2002) a fourth needs to be added;
- A values based decline in consumerism;
- A dematerialisation of product and services;
- Closing the loop in industrial ecology; and
- Identifying and incorporating 'Restorative
Sustainability';
Figure 12 above shows the 4 sustainability wedges that are
actually needed for cities to begin the major process of
holistically moving toward real sustainability, towards the goal of
being lean and eco-balanced.
So what is 'Restorative Sustainability' and what constitutes a
restorative solution? To be restorative a strategy, process or
product would meet all TNS System Conditions for Sustainability
plus involve one or more of the following ;
- Reduce past concentrations substances from within the
earth;
- Reduce past concentrations substances produced by society in
the ecosphere;
- Repair and restore ecosystems and increase the diversity of
nature;
- be long lived perpetual or self perpetuating;
- be non maintenance or low maintenance;
- likely to be biological or biomimicking.
So far as outcomes are concerned, they create:
- net positive environmental and health outcomes;
- multiple ecological benefits;
- long lasting effects.
3.5 'Restorative Sustainability' Solutions in
Practice
A range of initiatives that have been identified as currently
available and meeting the above criteria are presented below. There
may well be others not yet identified and this author would welcome
suggestions as to others or comments on the above proposed
criteria.
Climate Positive: An Australian carbon offset
organisation that focuses on tree-planting offsets that are
equivalent to 1.3 times the actual carbon footprint of the offsets
as calculated by their online calculator. For every tonne of
CO2 subscribers produce, 1.3 tonnes is offset - 1 tonne
with verified emission reduction projects, and an additional 0.3
tonne over time through ecologically diverse forest restoration
projects. All or part of an individual, family or company's annual
CO2 emissions including travel, food, buildings and
lifestyle can be offset. Biodiverse forests are grown in the
Strzelecki Ranges where some of world's most carbon-rich forests
once stood. (ClimatePositive)
Green Roofs and Earth Integrated Buildings:
Green roofs, earth integrated and earth covered buildings provide a
diverse set of benefits including potential:
- energy savings - provided insulation, soil cover, and
vegetation are properly considered;
- air pollution and CO2 sink - absorbing and binding
airborne pollutants including CO2 into biological matter
resulting from the interaction between soil, micro
(micro-organisms) and macro fauna and flora;
- nutrient & pollutant sink - cleansing water and
minimising downstream pollution;
- stormwater volume reduction;
- biodiversity restoration - based on soil cover, and vegetation
properly considered for locally indigenous plants etc.;
- reduced urban heat island impacts;
- higher levels of visual amenity;
- Lower maintenance and longer life of roof surfaces;
- Dual land use including recreation and productive urban garden
potential (Baggs et al 2007).
As a word of caution, it is important to consider the
whole-of-life-cycle greenhouse impacts of green roofs and earth
covered building. The deeper soil profiles associated with better
energy returns tend to require more structural resources and hence
higher greenhouse intensity (due to higher embodied energy). So
analysis should be undertaken to ensure that greenhouse benefits
return a less than 10-30 year carbon payback, i.e. the operational
energy savings and environmental benefits of the development need
to offset the whole embodied energy of the construction within this
period (as well as having a neutral ecological footprint) to avoid
exacerbating global warming.
Green Walls: The benefits of plantscaped walls
depends to some extent whether the soil in which the plants are
growing is in contact with the building's walls or not. If so,
higher thermal benefits will result (with likely increased embodied
energy as in green roofs above).
Plantscaping in general provides numerous benefits similar to
green roofs, but to a slightly lesser extend depending on the
volume of soil present:
- energy savings - providing shade and insulation effects;
- glare control - depending on design and prominence;
- air pollution and CO2 sink - absorbing and binding
airborne pollutants including CO2 into biological matter
resulting from the interaction between soil, micro and macro fauna
and flora;
- nutrient sink - cleansing water and minimising downstream
pollution;
- biodiversity restoration - based on soil cover, and vegetation
properly considered for locally indigenous plants etc.;
- reduced urban heat island impacts;
- higher levels of visual amenity;
- Lower maintenance and longer life of roof surfaces;
- Dual use including privacy (e.g. CH2 Building, Melbourne City
Council) and productive urban garden potential.
Plantscaped Interiors: Have been shown by
research to reduce air pollution and provide CO2
absorption. They absorb and bind indoor volatile organic compounds
(VOCs) and airborne pollutants including CO2 into
biological matter. This ability results from the interaction
between soil and micro organisms. Plants also provide additional
psychological benefits resulting in a contribution to increased
worker satisfaction and potentially productivity.
For EARTH Probiotic Water Treatments: Are non-toxic,
biodegradable, and self perpetuating, probiotic treatments which
digest solid waste, transforming effluent ponds into usable water.
They are suitable for any organic waste removal and organic odour
control and sanitation in industrial, commercial and residential
applications. For EARTH products assist in the treatment of waste
and wastewater by eliminating organic odours and accelerating the
breakdown of solids. They contain beneficial bacteria to
effectively reduce Biological Oxygen Demand (BOD), ammonia,
nitrates, nitrites and other pollutants including TSS (Total
Suspended Solids) E-Coli and pathogens including faecal coliforms
in effluent ponds and sewage systems. The product is suitable for
organic waste removal applications such as piggeries, and septic
systems. The use of these probiotics in waste-water treatment
plants has the effect of multiplying the efficiency of the plants
significantly - up to several times. This could potentially save
some large scale industrial or municipal waste water treatment
plants tens or even hundreds of millions of dollars in avoided
upgrade requirements or at the very least significantly delay the
expenditure. The microorganisms continue to assist even out into
the broader environment maintaining their beneficial conversion of
nutrients and reduction of pathogens provided aerobic conditions
exist.
Desert Cube Waterless Urinal
Conversion: Desert Cube Waterless Urinal System also
contains naturally occurring microbes to turn existing trough or
bowl facilities into touch-free waterless urinals. The embedded
microorganisms naturally breakdown the organic matter inside the
drain and interfere with the bacterial digestion that produces
unpleasant odours. They also reduce the ability of faecal bacteria
to latch onto urine solids as a source of food. Reduces drain clogs
and stains by converting uric scale deposits into more soluble
compounds and reduces pathogens. Cubes are placed in the base of
the urinal and the water supply is turned off. Beneficial microbes
are released as the cubes slowly dissolve over several weeks. Cubes
are 100% biodegradable and safe for septic and sewerage. An all
purpose Washroom Cleaner is also available with scale inhibitor and
naturally occurring microbial strains to reduce washroom
odours. Reduces water use by up to 98% as only a single daily
cleaner flush is required. Reduces use of chemicals and is suitable
for use during development or in existing buildings any type of
urinal, as the system is installed after construction. As above,
the microorganisms continue down the pipe to assist in the sewage
treatment plant and even out into the broader environment to
continue their beneficial conversion of nutrients and reduction of
pathogens provided aerobic conditions exist.
Net Positive Renewable Energy: Renewable Energy
sources are greenhouse emission free except for their embodied
energy. Different types of systems have differing rates of embodied
energy payback:
Crystalline Silicon Systems: e.g. BP Solar,
Origin Energy
Energy Payback period - 4 years.
Thin-film Photovoltaic Systems
Amorphos Silicon Systems: Energy Payback period
of thin-film technologies is similar approx. 2-3 years (with
frame).
Cadmium Telluride (CaTe) Polycrystalline Systems. Energy Payback
period - 0.9 year (1.9 yrs with frame)
Dye Solar Cell (DSC, 3rd Generation PV Systems). Energy Payback
period - 0.31 years. (Baggs & Haines 2006)
While the size of a PV or other renewable energy system is
designed to replace only the emissions of a particular load, it is
a 'reductive sustainability' solution. However, as soon as the
embodied energy is paid back and the energy generated exceeds the
annual load of the site providing net positive energy into the grid
it can be said to be a 'restorative solution'.
Peak metal: A word of warning relating to the
rarity of some metals being incorporated into photovoltaic systems
- some of the rarest metals on the planet are being incorporated
into PVs, e.g. indium (gallium indium arsenide amorphous),
telluride (CaTe PV) and ruthenium (DSC PV). Some of these metals
are so rare some researchers are already discussing peak metal
availability approaching within a few years with the cost of indium
rising nearly 17 times between 2003-2006 ($60/kg-$1000/kg) and only
five years of known resources left (Cohen, 2007).
Restitution of Indigenous Plant Associations and
Ecological Values: While not relevant to every site, some
sites and roofs tops may be suitable for the re-establishing of
areas of plantings using locally indigenous plants and soil
profiles. While this not an inherently easy process, if enough
patches of restored ecosystem started to be installed, it is likely
to provide additional biodiversity benefits by allowing and
encouraging the repopulation of areas with indigenous native
insects, birds and other animals. When grown on roofs, the benefits
of green roofs (see above) would also apply.
Offsite Tree Planting: This strategy is being
used widely as an emissions offset tool already. The benefits that
accrue will actually depend on a variety of issues such as the area
being planted, the planting style (monoculture or diverse),
adjoining ecosystem integrity (better if diverse communities
planted adjoining high quality forest with similar locally derive
seed stock to allow more holistic re-colonisation of the ecosystem
over time) and forestry practices (use of baits, genetically
modified seed stock or not etc). Systems such as ClimatePositive
mentioned above use at least partial diverse plantings in relative
proximity to intact ecosystems.
Landfill Mining: The extraction of landfill gas
could be seen to be a restorative process in as much as it, in
effect, reduces past impacts.
Tools for Implementation: One of the factors
limiting the implementation of sustainability is the difficulty
design and construction professionals find in locating products
with bona fide preferential environmental and health
features.
Ecospecifier.org is an online knowledgebase and database of over
3200 ecologically and health preferred products, materials and
technologies which provides verified information to built
environment professionals and homeowners alike delivered at the
level of detail needed by each market.
The information provided is both quantitative and qualitative,
life-cycle assessment based and focuses on all aspects of
restorative sustainability including closed loop product cycles.
Products have to meet specific entry criteria and all claims are
verified by experienced professionals with enhanced listings
product manufacturers required to submit third party test data to
back all key environmental and health claims. Ecospecifier also
reviews products against major international Green Building Rating
tools such as Green Star. It is likely also in the near future to
be integrating LEED and Green Globe systems into product
verification and search processes.
4. Conclusions
Policymakers, designers, engineers and constructors responsible
for urban outcomes need to refocus their policy, design and built
outcome towards eco-balanced, lean, low carb cities materials
and strategies. The past 'Reductive Sustainability' mantra of the
'3Rs' ('Reduce, Re-use, Recycle) needs to be expanded to
include concepts of industrial ecology and 'Restorative
Sustainability' and replaced by the '5Rs' 'Reduce, Re-use, Recycle,
Repair + Restore'.
REFERENCES
Allenby B.R., (1992) Achieving Sustainable Development Through
Industrial Ecology, International Environmental Affairs 4,
no. 1 (1992): 56-68.
Aust Uranium Association, (2007), Naturally-Occurring
Radioactive Materials (NORM), UIC Nuclear Issues Briefing Paper #
59, 11/5/12 accessed at http://www.tbc.school.nz/elearning/localsites/uic/nip59.htm.
Ayres R (1994) Industrial Metabolism: Theory and Policy,
In The Greening of Industrial Ecosystems, edited by
Allenby B, and Richards D, p. 23-27, National Academy Press,
Washington
Baggs D, & Haines B, Technical Guide 3: Photovoltaic
Technology & Installation, ecospecifier.org, Brisbane Australia
accessed 11/5/12 at /knowledge-green/technical-guides/technical-guide-3-photovoltaic-technology-installation.aspx
Baggs S, J & D, (2007) Australian Green Roof and Earth
Covered Buildings 3rd ed. Dual Harmony Publishers
Brisbane Australia
Benyus J, (1997), Biomimicry: Innovation Inspired by
Nature, Harper Collins New York.
ClimatePostitive accessed 11/5/12 at www.climatepositive.com.au
Cohen, D. (2007), Earth's Natural Wealth: An Audit, New
Scientist, 23 May 2007, issue 2605, page 34-41 accessed
11/5/12 at http://environment.newscientist.com/channel/earth/mg19426051.200-earths-natural-
wealth-an-audit.html
Crawford R, and Treloar G, (2005), An Assessment of the Energy
and Water Embodied in Commercial Building Construction, 4th
Australian LCA Conference, February 2005, Sydney
Enkvist P, Nauclér T, and Rosander J, (2007), A cost
curve for greenhouse gas reduction, McKinsey & Company,
Stockholm.
Environment Australia, (2002) Review of data on heavy
metals in ambient air in Australia, Technical Report No. 3, May
2002 accessed 11/5/12 at http://www.environment.gov.au/atmosphere/airquality/publications/report3/chapter2.html
Frosch R, (1992) Industrial Ecology: A Philosophical
Introduction." Proceedings of the National Academy of Sciences,
USA 89 (February 1992): p. 800-803
Heijj E., (2002) Sustainability Network Newsletter # 11,
CSIRO , Melbourne, based on p. 48 Raskin P, et al, The Great
Transition:The Promise and Lure of the Times Ahead, Global Scenario
Group, Stockholm Environment Institute - Boston
McDonough W, & Braungart M, (2002), Cradle to
Cradle, North Point Press, New York.
Matos GR., and Wagner L.A., (1998), Consumption of materials in
the United States, 1900-1995: Annual Review of Energy and the
Environment 1998, v. 23, p. 107-122.
Morris CJG, (2000), Urban Heat Islands and Climate Change - The
University of Melbourne, Melbourne, Australia accessed
11/5/12 at http://www.earthsci.unimelb.edu.au/~jon//WWW/uhi-melb.html
Raupach D, (2007), CSIRO Marine and
Atmospheric Research and the Global Carbon Project accessed
11/5/12 at http://www.itwire.com.au/content/view/12347/1066/
Roodman, DM & Lenssen, N (1995), A Building Revolution:
How Ecology and Health Concerns are Transforming Construction,
Worldwatch Institute, Washington, DC: Worldwatch Institute.
Schmidt-Bleek F, Factor 10 Institute accessed 11/5/12 at http://www.factor10-institute.org/
Treloar G, Fay R, Love PED, and Iyer-Raniga U, (2000), Analysing
the life-cycle energy of an Australian residential building and its
householders, in Building Research & Information
(2000) v. 28 (3), p.184-195.
Treloar, GJ, McCoubrie, A, Love, PED, Iyer-Raniga U, (1999),
'Embodied energy analysis of fixtures, fittings and furniture in
office buildings', Facilities, vol. 17, no. 11, pp.
403-9.
Vattenfall AB, (2007) Global Mapping of Greenhouse Gas Abatement
Opportunities up to 2030. available from http://www.schoonschakelen.nl/library_files/1_1253885146_Power%20Sector_Global_Mapping_of_Greenhouse_Gas_Abatement_Opportunities_up_to_2030-Vattenfall-2007%5B1%5D.pdf
Wagner L, Materials in the Economy, (2002), U.S.
Geological Survey Circular 1221, U.S. Department of the Interior
U.S. Geological Survey, Denver accessed 11/5/12, at http://geology.cr.usgs.gov/pub/circulars/c1221
Walker-Morison A, Grant T, & McAlister S, (2007), Using
Materials Sustainably, BDP Environment Design Guide, No
50, Melbourne
Weizsäcker, v. EU, Lovins A, Lovins H, (1997), Factor
Four: Doubling Wealth, Halving Resource Use, Earthscan Publications
Ltd., London.