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Fringe Benefits Tax (FBT) Favours Cars over Public Transport

FBT is a tax paid on certain benefits employers provide to their employees. Provision of a car for private use is the most common FBT paid for by employers representing 46% of the total payment benefit types (Endnote 1).

The taxable value of the fringe benefit for a car under salary packaging arrangements is a percentage of the car’s value calculated by using either a ‘statutory formula’ method or an ‘operating cost’ method. The ‘statutory formula’ method provides generous concessional tax rates that reduce with kilometres travelled – see table 1. This method was used by almost 69% of FBT payers in 2004/05. (Endnote 1)

Overseas Actions.Table 1 – Statutory Formula – FBT Rates 

Total km Travelled During Year FBT
Less than 15,000 26%
15,000 - 24,999 20%
25,000 - 40,000 11%
Over 40,000 7%

There is also an option for cars to be purchased under a novated lease arrangement where the:

  • employee enters into a lease with the finance company; and
  • employer enters into a deed of novation (tripartite agreement) with the employee and the finance company.

This allows the employer to claim a GST credit for the GST included in the lease charges, if the car is being leased to the employer in the course of its business.

Car parking facilities are another employer provided benefit available to employees under salary packaging.

By contrast, the FBT payable on a public transport yearly ticket provided by the employer under similar salary packaging conditions, is around 96% of the ticket value.

FBT and the Environment

Australia contributes 1.5% of global greenhouse gas emissions. Transport contributes 14% of Australia’s total greenhouse emissions caused by our reliance on the use of cars (for passenger transport) and trucks (for freight) and is one of the fastest growing sectors of greenhouse gas emissions.

Greenhouse gas emissions from total transport are projected to increase by nearly 30% between 2005 and 2020 and Table 1 shows actual and projected emissions from the transport sector from 1990 (base year for the Kyoto Protocol) to 2020

Table 1 – Emissions from Transport sector (Endnote: 2) - Mt CO2-e

 

1990

1995

2000

2005

Kyoto Period
2008-12

2020

Cars

35.2

37.7

41.3

44.0

45.7

49.3

Total Road

54.3

58.9

65.9

71.1

76.5

88.8

Rail

1.7

1.6

1.6

2.1

2.6

3.3

Domestic Aviation and Shipping

5.9

7.7

7.4

7.5

9.0

11.5

Total Transport

62.1

68.2

74.9

80.8

88.1

103.6

Australian capital cities are home to around 65% of the nation’s total population. Low density, sprawling suburbs have been created aided by the rapid improvement of the road system and expanded ownership of private motor vehicles. It is estimated that 35% of car use (private and company owned) is for travel to/from work (Endnote 3) often involving single occupancy.

Road use and urban road congestion is on the rise in Australia’s major cities. Almost half of Australia’s total urban vehicle kilometres travelled are currently performed under congested traffic conditions (Endnote 4). This contributes to increased levels of air and noise pollution.

Ambient air pollution caused by motor vehicles is also a major health problem. In 2000, such pollution caused an estimated 2,700 cases of morbidity and an estimated 1,400 cases of premature death. The main causes of death were cardio-vascular problems, bronchitis and other respiratory diseases. The cost of death and disease that can be attributed to motor vehicle pollution was of the order of $2.9 to $3.9 billion in 2000 (Endnote 5).

There are significant benefits of an effective public transport system which offer compelling benefits to the Australian economy, community and environment including:

  • relieving road congestion in metropolitan areas, reducing delays for drivers and freight transport;
  • providing relief from rising fuel costs particularly for households in the ‘mortgage belt’ middle and outer suburbs that are most impacted by rising petrol prices;
  • reducing transport emissions that contribute to climate change emissions and providing communities with safer and healthier modes of transport. The urban rail alternative:
    • is almost 6 times as energy efficient as cars:
    • can deliver significant land use savings compared to moving the same number of people by road. A double-track railway requires only one quarter of the land of a dual carriageway road and has about one third of the construction and maintenance costs: and
    • can move at least 20,000 people per hour - a six-lane freeway can manage only a quarter of this volume. A peak hour train carrying 2,000 passengers replaces 1,600 cars, significantly reducing congestion and pollution.

However, retention of existing FBT arrangements favouring cars over public transport restricts the potential of Australia’s public transport system to help Australia reduce car dependency and transport greenhouse emissions.

Overseas Actions

Overseas countries are actively pursuing increased public transport use including changing the taxation arrangements to promote public transport.

USA (Endnote 6)

Legislation was introduced in 1984 to allow eligible employers to give employees up to US$15 monthly in tax-exempt public transport benefits to offset commuting expenses. By 2008 this benefit had increased to US$115 per month. Employers get a tax deduction for their expense and save on payroll taxes. When first introduced, public transport patronage increased 25% at participating workplaces and in some areas 30% of participants were new users of public transport.

Canada (Endnote 6)

‘Over the past decade, a coalition of business, labour, health and environmental groups has urged Canada’s Federal government to give tax-exempt status to employer-provided public transport benefits. In 2005, the Canadian federal budget identified tax-exempt public transport benefits as an environmental measure that would be considered, subject to further assessment of its environmental effectiveness, fiscal impact, economic efficiency, fairness and simplicity’.

Independent research and analysis commissioned by the Canadian Urban Transit Association concluded that ‘among the notable results expected by 2016 are a projected increase in commuter public transport patronage of 8.3% to 31% and a net economic benefit of C$385 million to C$1.4 billion per year that would vastly outweigh the loss in federal tax revenues’.

Conclusion

Changing travel behaviour to avoid the negative impacts of the large and growing dependence on private motor vehicles in Australian cities requires a concerted and coordinated approach and a sustained commitment involving Commonwealth, State and Local governments, the business community and public transport operators. The following 2008 Federal and State government initiatives could provide opportunities for change:

  • Formation of Infrastructure Australia to coordinate infrastructure (including transport) and the audit of national infrastructure to identify bottlenecks and deficiencies ahead of developing future strategies;
  • Australian Transport Ministers’ agreement to develop a National Transport Policy;
  • Review of the Australian Taxation System; and
  • Climate Change Policy including the Garnaut Climate Change Review (April 2008) and the Strategic Review of Climate Change Programs (May 2008).

Endnotes

1.  Australian Taxation Statistics 2003-04 – Fringe Benefits Tax for 2004-05 FBT Year
2.  Australian Greenhouse Department of Climate Change – Transport Sector Greenhouse Gas Emissions Tables 1.2 & 2.3
3.  Australian Bureau of Statistics – 1301.0 – Yearbook Australia, 2008
4.  BTE (2000), Information Sheet 16, Urban Congestion – the implications for Greenhouse Gas Emissions.
5.  Australasian Railway Association ‘National Passenger Transport Agenda’ (2006), - Exhibit 53 and pg 53.
6.  Canadian Urban Transit Association, Issue Paper 15

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