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Types of Pricing Mechanisms

 

moneyBullet pointSubsidies and Bounties
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Charges
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Deposit-refund systems
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Financial enforcement incentives

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Subsidies and Bounties

Subsidies are payments from the government to the producer which effectively reduce the price of goods or services, and therefore encourage their sale. A similar device is a bounty that is paid to the producer for the goods produced (rather than one that is paid when goods and services are bought). An example of a bounty that can impact on the environment is the steel industry bounty, which was designed to protect employment and maintain production of steel. However, because steel production has adverse environmental impacts, the bounty also maintains these impacts.

An example of a subsidy that can harm the environment is that provided for agricultural fertilisers. In the years 1983&endash;84, the government was subsidising fertilisers to the amount of $51 million to encourage farmers to use more of them to increase production. The subsidy was also supposed to reduce farm costs (Department of Arts, Heritage and Environment 1985, p. 10). Chemical fertilisers, however, contribute to poor soil structure and pollution of the water used for agriculture and by humans, aquatic plants and animal communities. Also, the fertilisers enabled farmers to increase their cropping and stock rates, and thereby placed more pressure on the land. This short-term increase in production was probably attained at the expense of long-term sustainable production. Moreover, while the use of these fertilisers was being encouraged, research into substitutes was discouraged, and the incentive to use the fertilisers sparingly or more efficiently was reduced.

Subsidies can also mean that goods and services are underpriced. For example, subsidies for irrigation to farmers can encourage excessive water use, change groundwater flows, and cause environmental damage downstream such as increased salinity. Similarly, past practices of charging low royalties on forestry operations have created a whole industry which is dependant on low-priced raw materials. This provides a heavy disincentive to the establishment of an alternative industry based on commercial plantations, because so much specialised equipment and human skills has been invested in the old industry (James 1991, p. 9).

It is argued that subsidies can also be used as economic instruments to benefit the environment by providing an incentive for polluters to change their polluting practices or by helping them to meet environmental standards. Subsidies include tax deductions and rebates. For example, some tax-deductible activities&emdash;for money spent on soil conservation, recycling schemes or for donations to environmental groups&emdash;are aimed at encouraging environmentally beneficial behaviour.

The government can also provide grants for particular programs and projects, including environmental projects such as the National Soil Conservation Program or the National Tree Program. Another example is grants for environmental technology. These amounted to $3.4 million in 1991, and were aimed at projects such as the recycling of wastes (ESD Working Groups 1991a, p. 46).

Subsidies, bounties and tax concessions do not in general conform to the polluter-pays principle, because the polluter is not bearing the full cost of pollution control measures. The OECD (1989) has found that environmental subsidies tend to serve economic rather than environmental goals&emdash;such as the provision of financial support to firms that find it expensive to meet environmental standards.

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Charges

A charge can be considered as a 'price' that is paid for polluting the environment. Charges are supposed to provide an incentive for reducing pollution; but this will depend on how high the charge is. The ESD working group on manufacturing argues that where pollution charges have been used they have usually not been high enough to provide an incentive to minimise pollution. The OECD has also found that, in most cases, charges are too low to provide an incentive; instead, they merely act to redistribute money from the polluter to the government. Governments can use the money raised in this way for environmental protection, such as collective treatment and research into pollution control technologies; but often they do not.

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Deposit-refund systems

The most well-known deposit-refund system is that used for soft-drink bottles. This traditional mechanism for encouraging people to return bottles for recycling has largely disappeared, although it is still used in South Australia, and environmental groups such as Friends of the Earth are lobbying for it to be reintroduced into other Australian states. Basically, with such a system, a potentially polluting product is given a price that includes an amount which is refundable if it is returned.

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Financial enforcement incentives

These include non-compliance fees or fines for those who do not comply with regulations. In theory, the fee should be more than the profits made by not complying; but in practice the amounts charged are often very low and do not provide enough incentive to comply. An alternative to these fees would be to charge the polluter the full social costs of his or her non-complying activities. The problem with non-compliance fees is the high administrative costs that are associated with having to go to court to get them.

Performance bonds are an enforcement incentive that seek to avoid court costs; payments are made to the authorities, but are refunded if compliance is achieved. If compliance is not achieved, the bond is forfeited and it is the polluting company which has to go to court if it disputes the decision. Performance bonds have rarely been used outside Australia.

Liability insurance schemes are also sometimes used to cover compensation for possible environmental damage. The incentive for potential polluters to clean up their production processes is that lower insurance premiums will be charged if there is only a low probability of those processes causing damage.

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© 2001 Sharon Beder