Environmental management
DPS reports annually on elements of environmental performance, in line with the
Environment Protection and Biodiversity Conservation Act 1999 (EPBC Act), for
the management of resources for which it is responsible.
DPS also reports under the:
- Energy Efficiency in Government Operations (EEGO) Policy, and
- National Environment Protection Measures (Implementation) Act 1998.
Ecologically Sustainable Development (ESD)
Ecologically Sustainable Development (ESD) is defined as ‘development that
improves the total quality of life, both now and in the future, in a way that
maintains the ecological processes on which life
depends’.
DPS reports annually on ESD throughout this report.
Identification, management and monitoring of
environmental impacts
DPS aims to ensure that the vital functions of Parliament House operate
effectively, while minimising resource consumption and waste production by:
- monitoring environmental performance
- implementing programs and projects to improve environmental outcomes, and
- developing plans to improve environmental sustainability.
Many activities at Parliament House—including maintenance, engineering,
landscaping, ICT, catering and office-based services—have the potential to
affect the environment through energy and water consumption, greenhouse gas
emissions and waste generation.
DPS incorporates environmental guidelines and checklists in the procurement of
products and services and in the planning and delivery of projects, including
consideration of:
- whole-of-life principles
- sustainable procurement principles
- reuse and recycling of materials, and
- energy, water and waste minimisation.
Communication and promotion
DPS provides information on its environmental performance and promotes
sustainability initiatives. This includes encouraging participation in annual
environmental events such as National Recycling Week and World Environment
Day.
Environmental performance
Water consumption
Figure 16: Annual water consumption 2007–08 to 2017–18
Total water consumption for 2017–18 was 199,797KL, representing an increase of one per cent on the 198,446KL consumed the previous year.
Landscape water consumption
increased from 101,721KL in 2016–17 to 106,542KL in 2017–18,
representing an increase of five per cent. Building water consumption in
2017–18 was 93,255KL, a decrease of four per cent on the 96,725KL
consumed the previous year. Annual water consumption for Parliament
House is shown in Figure 16. Figure 17
shows a breakdown of water use during 2017–18.
Figure 17: Breakdown of water consumption in 2017–18
Water saving initiatives
Kitchens upgrade project
From 2019, the Parliament House kitchens will be progressively updated to
incorporate more energy and water efficient equipment—new large
commercial dishwashers will use 40 per cent less water and 55 per cent
less energy. Preparation of procurement documentation for design and
construction is currently under way.
Energy consumption
In 2017–18, total energy consumed at Parliament House, DPS
tenancies, and by DPS vehicles was 141,330 GJ, representing a
decrease of 3.1 per cent from the previous year. Parliament House
electricity consumption decreased by 3.5 per cent, natural gas
consumption decreased by two per cent, diesel fuel energy
(non-transport) decreased by 19 per cent, and energy for DPS vehicles
(passenger and other transport) decreased by 20 per cent compared with
2016–17.
Table 42
shows energy consumption by Parliament House, DPS tenancies and
vehicles.
Parliament House building energy use comprises:
- natural gas for heating, general hot water and in kitchens
- electricity to power office lighting, mechanical services, lifts,
cooling and ICT equipment, and
- a small amount of diesel mainly used for testing the emergency
backup generators.
Table 42: Energy consumed at Parliament House, DPS
tenancies and by DPS vehicles
Indicator |
Energy consumption
(GJ) |
|
2015–16 |
2016–17 |
2017–18 |
Parliament House building
|
136,916 |
144,385 |
140,380 |
Minter Ellison building |
– |
614 |
603 |
Transport–passenger vehicles |
73 |
69 |
51 |
Other transport |
325 |
363 |
296 |
Total energy consumption |
137,314 |
145,431 |
141,330 |
Figure 18: Parliament House annual electricity and gas consumption from 2008–09 to 2017–18
Figure 18
shows total Parliament House electricity and gas usage has remained
stable over the past 10 years. In 2017–18, Parliament House’s
combined electricity and gas consumption was 139,900 GJ which was
consistent with the average consumption of 139,135 GJ observed over the
past decade—electricity consumption was two per cent lower than average
and gas consumption was five per cent higher than average.
Over the coming years DPS will undertake a number of building improvement
projects that will result in lower electricity and gas usage, including
replacement of the building’s heating equipment, which accounts for the
majority of gas usage.
Transport energy use
In 2017–18, there was a 20 per cent reduction in energy use
associated with all DPS transport vehicles, compared with 2016–17. The
energy reduction is mainly associated with a reduced requirement to
transport landscape waste offsite—instead making more frequent use of a
local skip service. Other transport energy consists of fuel used in
onsite maintenance and loading dock vehicles, many of which operate on
electric power to reduce emissions.
Energy saving initiatives
In 2017–18, DPS completed the upgrade of two large central chillers
and associated control systems, which concluded an extensive chiller
upgrade program of all five central chillers, commencing in 2010. The
new chillers are more energy efficient and use more environmentally
friendly refrigerants.
In 2017–18, DPS progressed with the upgrade of six large boilers
used to heat the building—all boiler installation work is expected to be
completed in 2018. The new heating equipment will provide significant
energy savings from better equipment and operating efficiency.
Further projects and energy saving initiatives progressed in 2017–18
include:
- upgrade of lifts—this project is upgrading all 42 lifts in the
building to more energy efficient types, which use 30 per cent less
energy. Four lifts were upgraded in 2017–18. Of the remaining
38 lifts, the next 10 are scheduled for completion in 2018–19; then
a further 14 in 2019–20; and the final 14 lifts will be completed in
2020–21, and
- fine-tuning of the Building Management System (BMS)—in 2017–18,
DPS completed a broad fine-tuning program of the BMS controls used
to automate the building’s heating and cooling equipment. BMS
control settings have been adjusted and optimised by BMS technical
staff to improve energy efficiency while maintaining building
comfort conditions.
Recycling and waste management
Parliament House waste is generated from a diverse range of activities
inside and outside the building. Quantities and types of waste fluctuate
throughout the year, depending on building occupancy, sitting patterns,
construction projects, office refurbishments, and election cycles.
DPS recycles paper, cardboard, printer cartridges, lamps, used oil,
grease, batteries, landscape material, metal, organic food waste and
co-mingled waste.
In 2017–18, the amount of general waste (excluding construction
waste) sent to landfill was 404 tonnes. This is an increase of 11 per
cent compared with the 364 tonnes sent in 2016–17. The increase is
predominantly due to furniture replacement projects in both the Senate
and House of Representatives, requiring disposal of old furniture that
could not be resold through auction. A thorough clean-out of all plant
rooms in the building also contributed to the increase in landfill
waste.
In 2017–18, a total of 165 tonnes of paper was recycled—a decrease
of 20 per cent compared with the 206 tonnes in 2016–17. In 2018, the
printer settings on all DPS fleet printers were reset to double-sided
printing and greyscale on all print jobs, to reduce paper consumption
and printing costs. The amount of paper and cardboard recycled varies
annually, depending on parliamentary business and other building
activity.
Figure 19
shows annual waste disposed to landfill and paper recycled.
Construction waste is managed under project contracts and where possible
and appropriate, construction materials are reused, recycled or disposed
of in an environmentally friendly manner.
Figure 19: Parliament House annual waste disposed to
landfill and paper recycled
The preferred method for disposing of green landscape waste at Parliament
House is to chip the material on-site and re-use it in the gardens. When
waste generated in the landscape cannot be chipped on-site the material
is taken off-site to be recycled or sent to landfill. During 2017–18,
107 tonnes of landscape waste was sent for recycling and no material was
sent to landfill. Figure 20 shows annual trends in
landscape waste and recycling rates.
Figure 20: Annual quantity of landscape waste (tonnes)
Co–mingled and organic waste recycling
Co-mingled waste includes metal cans, glass bottles, milk cartons and
plastic, collected in a common bin. During 2017–18, a total of 38
tonnes of co-mingled waste was collected and recycled, a six per cent
decrease compared to the amount collected and recycled in 2016–17.
DPS collects organic food waste from catering operations in the building
for recycling at a local worm farm. Since being introduced in 2012, the
initiative has helped reduce the burden on ACT landfill sites and reduce
emissions (methane) caused by the breakdown of food waste.
During 2017–18, a total of 77 tonnes of organic waste was diverted
from landfill and converted into garden compost material at the local
worm farm—a 20 per cent increase compared to the amount collected the
previous year. The increase is mostly due to additional excess food
waste collected from functions, events and catering operations at
Parliament House. Figure 21
illustrates annual co-mingled and organic recycling rates.
Figure 21: Parliament House annual co-mingled and organic
waste recycled (tonnes)
Emissions and effluents
Greenhouse
gas emissions
During 2017–18, a total of 27,097 tonnes of carbon dioxide
equivalent (CO2e) was generated from Parliament House operations and DPS
tenancies,
representing a four per cent decrease from 2016–17. In 2017–18,
DPS reduced CO2 emissions by 57 tonnes from renewable electricity
generated by roof-top solar panels at Parliament House. Table 43
shows the breakdown of emissions within various categories.
Table 43: Annual greenhouse gas emissions (direct and
indirect, including passenger and operational vehicle fleets)
Emission category |
Comment |
2015–16
(tonnes
CO2e) |
2016–17
(tonnes
CO2e) |
2017–18
(tonnes
CO2e) |
Scope 1 |
Emissions at the source of the activity (for
example, emitted from gas and fuels used at Parliament House and
by vehicles)
|
2,350 |
2,702 |
2,635 |
Scope 2 |
Emissions generated elsewhere (for example,
by the power plants that produce the electricity used at
Parliament House and DPS tenancies)
|
19,283 |
21,736 |
20,810 |
Scope 3 |
Indirect emissions, meaning emissions
generated during the delivery of electricity, gas and fuel to
Parliament House, over which DPS has little control
|
3,326 |
3,762 |
3,652 |
Scopes 1 and 2 total |
DPS has direct responsibility for these
emissions
|
21,633 |
24,438 |
23,445 |
Total net emissions (Scopes 1, 2
and 3)
|
Direct and indirect emissions
including offsets |
24,959 |
28,200 |
27,097 |
Figure 22: Parliament House greenhouse gas emissions from electricity and gas usage,
and carbon savings from renewable sources
Carbon savings include accredited green power purchased under the
whole-of-government (WoG) electricity contract and a small amount of
solar power generated from Parliament House roof-top solar panels. From
1 July 2016, accredited green power was not available under the WoG
contract.
Emission reductions from
recycling
In 2017–18, DPS diverted 77 tonnes of organic food waste from
landfill to a local recycling facility—equivalent to reducing lifetime
landfill CO2 emissions by 146 tonnes.
Ozone–depleting substances
Parliament House relies on refrigerants that contain Ozone-Depleting
Substances (ODS). These are used for chillers, air-conditioning units,
cool rooms and refrigerators. DPS is reducing the requirement for
ozone-depleting gases through timely replacement of older equipment with
equipment that uses environmentally safer refrigerants.
In 2017–18, DPS completed an upgrade replacement of two large
chillers containing ODS with new chillers free of ODS. The upgrade work
completes an extensive chiller replacement program of all five chillers
used to cool the building, which commenced in 2010.
Many cool rooms at Parliament House operate on a ‘glycol’ fluid which is
an environmentally safer refrigerant. Over the coming years, DPS will
upgrade many of the building’s smaller air-conditioning units to
ODS-free cooling units.
Air
pollutants
The combustion of natural gas at Parliament House for heating, hot water
and cooking purposes generates oxides of nitrogen (NOx), oxides of
sulphur (SOx) and other air pollutants.
DPS reports annually on these emissions to the National Pollution
Inventory (www.npi.gov.au).
Discharges to water
Sewage from Parliament House is required, under a trade waste agreement,
to be equivalent to domestic strength (a domestic equivalent is a
concentration or level the same as would be found in household waste
water). To ensure these requirements are met, the following facilities
are in place:
- a grease trap on each kitchen drain
- a coalescing plate filter on the vehicle wash-down bay (to prevent
oil from entering the sewer), and
- a system to remove paint solids from paint brush washing facilities
before waste enters the sewer.
Significant spills of chemicals, oils and
fuels
In 2017–18, there were no significant spills of chemicals, oils or
fuels from Parliament House.
Footnotes:
National
Strategy for Ecologically Sustainable Development 1992
Landscape
water consumption includes irrigation, water features and ponds,
gardens taps,
and outside toilets.
Includes
electricity, natural gas and diesel (non-transport).
‘Parliament
House building’ energy in 2016–17 was 144,807 GJ, not 144,385 GJ.
The difference
is due to a correction in electricity data provided by the energy
retailer ActewAGL.
Energy use
(electricity only) related to DPS tenancy at Minter Ellison
building.
Includes
LPG, diesel and petrol used for maintenance and loading dock
vehicles.
‘Total
energy consumption’ in 2016–17 was 145,853 GJ, not 145,431 GJ. The
difference is due
to a correction in electricity data provided by the energy retailer
ActewAGL.
Electricity
use from DPS tenancy at Minter Ellison building.
Total
Emissions in 2016–17 was 28,313 tonnes CO2e, not 28,200
tonnes CO2e. The difference is
due to a correction in electricity data provided by the energy
retailer ActewAGL.
Conversion
factor equals 1.9 tonnes CO2 per tonne of solid food
waste—National Greenhouse
Accounts (NGA) Factors (2016).