Policy Brief for UK Landfill Tax

Eva Wu

Lulu Yu

4th April

 

Introduction

In the UK, landfill is the predominant form to dispose waste. Landfills account for 84% of Municipal Solid Waste. According to the report, UK’s domestic waste increases about 3% every year.  Since 2000, UK has approximately 434 tonnes of waste every year. Furthermore, the Environment Agency, who was responsible for regulating the operation of waste collection and disposal after 1996, found that the disposal with fewer voids caused various problems, such as gases generated by the waste. According to the data, disposal and  the landfill’s waste decomposition process lead to 45% of methane emissions in UK.

Landfill is a less desirable option for the waste disposal, which UK used for managing the most waste. We can see land fill is at the bottom on the list of UK waste hierarchy. The optimal choice to deal with the wastes is to reduce the generation of waste. Therefore, the government have an incentive to change the methods of management of waste from disposal to more sustainable way, including reduction, reuse and recycle.

The UK waste hierarchy

Reduction   Most attractive option centred on reduction or minimisation of waste at source include using less packging

Re-use          Including refilling of receptacles.

Recovery      Including the incineration of waste to use as energy, the composting of waste and materials recycling

Disposal         Least attractive option usually involves landfill

 

Coverage and Exemptions

Basically, all the waste disposed at licensed landfills sites, which are forced to register with the Customs and Excise, is liable to the tax.

In general, the volume of waste involved in the exemption is hardly likely to be significant and there were several types of waste are obtain exemption of the landfill tax.

1) Naturally occurring mineral waste from mines and quarries

2) Dredged spoils from inland waterways and harbours

3) Waste generated from cleaning  up historically contaminated land

4) Inert waste used for landfill site engineering

5)Water used to facilitate the transportation of waste

 

Goal and Implementation

The aims of the tax as set out in the UK Waste Strategy were: “to ensure that landfill costs reflect environmental impact thereby encouraging business and consumers, in a cost effective and non-regulatory manner, to produce less waste; to recover value from more of the waste that is produced; and to dispose of less waste,”‘ (DoE and WO 1995:12 cited in ECOTEC, 2001).

In October 1996, UK’s government implemented the landfill tax to reduce disposal of waste through a non-regulatory manner. “This Common Inheritance” indicated that government believed that both household and industry need a reform to change the way to dispose their waste.

The purpose of UK Waster Strategy is to set landfill disposal a proper price, which can reflect the environmental cost. For example, landfill activities have negative environmental impacts including methane emissions and groundwater pollution.

More specifically, the UK government expected the tax could lead to a reduction of waste to landfill from 70% to 60% by 2005. Several targets established by National Waste Strategy to manage the behaviour of industry and household.

 

UK national waste strategy targets

To stabilize household waste production at 1995 levels;

To reduce the proportion of controlled waste going to landfill to 69% by the year 2005;

To recover 40% of municipal waste by the year 2005;

The provision of close to home recycling facilities for 80% of the households by the year 2000;

For 40% of domestic properties with a garden to carry out composting by the year2000

 

Refund and Distribution

 A reduction of 2% Employers ‘National Insurance Contribution (NIC’s) is used to increase acceptance by industry and to “make  the landfill  tax revenue neutral.” The reduction of NIC’s is beneficial for the firms with insensitive employment and lower level of waste.

Partial funds generated from the tax were reinvested in waste management research and projects. ENTRUST are responsible for issuing the funds to eligible groups. In 1997, The Entrust (an environmental organization) Press stated that ₤8.5million raised by93 landfill operators were used for more than 1000 projects in 90(out of 440 registered bodies) environmental bodies. Under the Tax Credit Scheme, The specific distribution of the tax revenue is divided by 6 categories: land reclamation (13%),Land remediation(3.5%), Research and education (15%), environmental protection (46%),building restoration(22%), and administration (0.5%)


Tax Rate

The tax was one of the smallest taxes when it was introduced. After several years, the UK government decide to raise the tax rate dramatically to improve the behavioural impacts. The tax is a weight- based taxation. The calculation of the weight is used by a weighbridge and alternative methods, such as estimated amount of waste converted to weight.

Landfill Tax: Rates of Tax (£ per tonne)

Date of change Standard Rate Lower Ratea
01.10.96 7 2
01.04.99 10 2
01.04.00 11 2
01.04.01 12 2
01.04.02 13 2
01.04.03 14 2
01.04.04 15 2

Notes: a. The lower rate of tax applies to listed inactive wastes.

Source: HM Customs and Excise (2006)

Tax rate is planned to increase ₤3 per tonne each year until to reach ₤35 per tonne in a long term, which is designed to further reduce the landfilling of biodegradable municipal waste. According to UK’s government Budget 2005, between 1997-1998 and 2003-2004, the total amount of disposal waste to landfill declined 20%. The landfill tax was effective to reduce the landfilling waste.

 


 

Conclusion

The outcome of landfill tax is hard to measure, as the previous data was not precise. But we have a brief summary about the outcome from Benefit and Criticisms base on our research.

Benefits Tax brought some beneficial impacts.

First, tax increased the industry’s awareness of managing waste. A survey in 1998 revels that 1/3 firms believed that Landfill tax result in the development of waste management measures.

Moreover, survey shows that the introduction of tax lead to reduce 2/3 waste from business, councils and contractors. 50% interviewees stated that their disposal costs had increase 10% after the implementation of tax.

Criticisms As the landfill tax is an aggregated charge for total volume of disposal of waste. There is nothing criteria to manage waste production and to provide rewarding incentives for efficient household. In 2001, Ecotec stated that landfill tax increase the municipal waste, since people started to change the waste stream to avoid tax. For example, people can dispose the household waste or dumped the waste illegally which means people again little incentive for individual waste producers to reduce waste.

 

Policy brief of NOx Budget Trading Program

Lulu Yu   Eva Wu

Summary of this policy

The NOx Budget Trading Program is a market-based cap and trade program which created to reduce emissions of oxides of nitrogen (NOx). The main NOx polluters are heat-engine plant in the eastern United States.  NOx has been linked to a variety of health effects, the severity of which depends on concentration, length of exposure, and breathing rate. The NOx Budget Trading Program was designed to reduce NOx emissions during the w ozone season (May 1- September 30) when ground-level ozone emission are most serious.

 

The goal of this programme is to get 392 facilities to reduce annual NOx emissions by a total of nearly 510,000 tonnes from 2007 levels.

 

 

 

Coverage of the policy

(Contains two parts, one is the Geographical Scope and the other is Species Coverage)

The OTC consists of representatives from the Northeast and Mid-Atlantic states, the States that will now be involved include Alabama, Connecticut, Delaware, Illinois, Indiana, Kentucky, Massachusetts, Maryland, Michigan, North Carolina, New Jersey, New York, Ohio, Pennsylvania, Rhode Island, South Carolina, Tennessee, Virginia, West Virginia and the District of Columbia.

 

The main objective of implementation of this project was the large pollutant in States who make significantly contribute to the pollution. The EPA requires them to control NOx emissions in response to the Section 126 Final Action rulemaking. Some fossil fuel boilers or combustion turbines who serve an electric generating are also included in this trading programme. The standard was output of greater than 25 MW or that have a maximum rated heat input capacity of greater than 250 mm Btu/h.

 

 

How it works

 

First of all, during the “ozone season” NBP set a regional “budget” (or cap) on emissions from power plants and other combustion sources during the “ozone season”. Sources were required to reduce emissions significantly below baseline levels in each participating state to meet the budget. States allocated allowances to sources (each allowance equaled one ton of emissions) and sources could use emissions trading to achieve the most cost-efficient reductions possible.  If emissions were below budget levels, sources could “bank” unused allowances and use or trade the banked allowances to cover emissions in a subsequent ozone season.  

 

Secondly, the OTC created flow control system to control the overuse of allocated NOx allowances. Flow control was triggered when the total number of allowances overused for all sources exceeded 10 percent of the total overall (regional) budget for the next year. Then EPA calculated the flow control ratio, they will dividing  10 percent of the total regional NOx trading budget by the number of banked allowances The resulting flow control ratio established the percentage of banked allowances that could be deducted from a source’s account on a 1:1 ratio of one allowance per one ton of emissions. The remaining banked allowances, if used, were deducted at a 2:1 ratio of two allowances per one ton of emissions.

 

Implementation

 

Montioring system was widely used during the implementation of this project. This project begin monitoring on May 1, 2002.  If sources do not have enough allowances to cover their emissions based on their initial allocation, they may buy allowance from other sources who didn’t used up the allowance. This cap and trade system works really flexibility and sources have two months time to ensure they hold adequate extra allowance which was until November 30 each year. Usually the way sources ensure they hold adequate emissions allowances through two ways. One was the standardized monitoring and the other was reporting procedures. Usually budget sources must monitor and report their actual emissions to the EPA to ensure demonstrate compliance. Under the trading system, sources with large NOx emissions must monitor their emissions using continuous emissions monitoring systems. Sources with lower NOxemissions may use simpler estimation methods.

 

The sources had two option to evaluate the allowance. One was to allocate allowances based on each source’s share of statewide ozone season heat input. The other was based ozone season outputto reward sources that generated more energy with less fuel input.

 

 

Cost-effectiveness

 

About 290,000 NOx allowances will be allocated in total region-wide to sources every year. Sources that retire will continue to receive allocations until the next allocation update. EPA  also making additional allowances available to participating sources through a compliance supplement pool during the initial two years of the programme, the. These allowances will be distributed among sources which made early reductions during the 2001 and 2002 ozone seasons. Sources may use these allowances for compliance purposes as they would other allowances for the 2003 and 2004 compliance periods. However, the EPA will retire all remaining pool allowances from the allowance tracking system after the 2004 ozone season compliance determination process is completed. New sources entering into the programme will be allocated allowances from a portion of the State budget that is set aside for new sources

 

A new source is eligible to receive allowances from the new source set-aside until it has sufficient operating data to receive an updated allocation as an existing source. Each new electric generating unit will be allocated allowances based on the product of either a NOxx emissions rate of 0.17lbs/mm Btu or the unit’s permitted limited, whichever is less, times their actual utilisation for the control period. Sources that are not currently subject to the programme but undergo major modifications and are subsequently required to participate in the programme are initially treated as new sources and therefore are eligible to receive allowances from the new sources set-aside. After compliance has been determined, any allowances remaining in the new source set-aside will be redistributed to existing sources.

 

 

 

Result

There’s a significant outcome in NOx. In 2006, under the NOx Budget Program, the budget sources emitted 491,483 tons, which means a reduction of NOx by more than 38,000 tons, or 7 % from the emission in 2005 and 74 % from 1990 emissions. In addition, like improvements in NOx, there’s also changes in ozone. Ozone concentrations in urban and rural areas had decreased during 2004-2006 in comparison to that during the period 2000-2002. The average reduction in ozone concentrations in states participating NOx Budget Program was estimated as 5%.

 

In 2009, CAIR’s NOx ozone season program began, effectively replacing the NBP in the East and achieving further summertime NOx reductions from the power sector.

Rescource

http://www.epa.gov/airmarkets/progress/docs/otcreport.pdf

http://www.epa.gov/airtransport/pdfs/SNPRAllocations.pdf

http://daq.state.nc.us/monitor/eminv/noxbudget/nox_budget_program_overview.pdf

http://ekh.unep.org/files/GP-10.pdf

 

 

 

 


Carbon Tax Policy Brief for Netherlands

Carbon Tax Policy Brief for Netherlands

Lulu Yu   Eva Wu

 

The Coverage of RET

The regulatory energy tax (RET) was forced to implement on January1, 1996 in Netherlands as a consequence of the Netherlands’ second National Environmental Policy Plan. In order to avoid economic risk the initiate RET was mainly focusing on small scale energy consumption for large industrial energy user. The main purpose of the tax was stimulating additional energy conversation.

The implementations of the RET were generally consisting of two parts: before and after 2004.Before 2004 there was a Benchmark Protocol which proving effective in inducing large energy consumers to save energy, exposing them to the economic risks of an unilateral tax was felt to be unwarranted. So the main fuels being taxed before 2004 was small scale energy like NG (natural gas) and mineral oil products which can be used as substitutes for gas by households. Apart from this, mineral oil products which can be used as substitutes for gas by households or small commercial establishments are also taxed (home heating oil, light fuel oil, non-transport applications of LPG/butane/propane). RET is expected to generate extra energy conservation majorly through the price impact on the demand side. After 2004 also the large scale energy consumption is brought under RET on the basis of the implementation of the new European directive on energy taxation and the incorporation of a part of the tax on fuels in the RET. In order to prevent double taxation, natural gas used in the generation of electricity is exempted. Also fuels used to power road vehicles are not subject to this regulatory tax. Besides the greenhouse horticulture sector in the Netherlands is characterized by a unique combination of features. The European Commission allowed the use of the zero-rate until the end of 1999. Nevertheless, beginning in 2000 the greenhouse horticulture sector also have to pay a (also in 2004 still rather low) tax on natural gas and mineral oil products.

RET was first introduced in1996 .However, at first the tax was aimed to influence behaviour. Then the tax rate was gradually into force.  Zero-rate and waste incineration plants for electricity were introduced in 1998. Then in coming 1999 several new tariff groups were introduced. Because of the faster growth of the use of electricity than of the other products, the tax rate for electricity had a big change in 2000. During 2001-2003 there were also some changes in the tax rate. In 2004 most of the tax was stopped because of the European directive tax on energy was implemented.

Compared with the previous tax system (for example the Fuel), RET is a stronger tax system for small scale NG consumption. However, RET converted the tax policy from “input” tax to “output” tax. Instead of tax NG input for producing electricity, RET tax on per unit of energy content. Therefore, RET failed to provide direct incentives for electricity producers to reduce co2emissions by substituting input.

Distributional Effects of RET

In 2004 RET generate the most part of environmental tax revenue  reached at €3213 billion, which occupied the 3% of total tax in Netherlands.The main purpose of RET is to reduce the consumption of “grey” energy by household and small business. According to the CPB calculation, € 1.4billion additional tax revenue will lead to a  reduction of 1.7-2.2Mton co2 emissions. In addition, the tax stimulate users to choose alternative sustainable energy, which have positive impacts equal to reduction of 0.7-6.5 Mton CO2 emission.

On general, this policy has many positive effects. Firstly, the tax raised a large amount of tax revenue and many of them are being recycled back to taxpayer (both household and business). For households, they changed the personal income tax like reduction in the rate charged over the first income bracket. For business, there were two main ways. The one was a reduction in the wage component paid by employers to cover social premiums paid by employee tax deduction for energy investments. The other was the accelerated depreciation of investments in environmental equipment and the tax deduction for energy investments. Secondly, the RET actually finished the goal which was the CO2 emission reduction increases from the initiate 1.7 to 2.7 million tons by the end of 2000. Thirdly, the tax and recycling had some positive effects on job creation.

RET is an innovative instrument created to balance budget (green tax reform).RET introduced some abatement incentives by subsidising the non-fossil fuel products. First, parts of the revenue raised by RET used to subsidize households of using energy efficient products .Since 2000, government introduced the “energy premium” to provide positive fiscal incentives for green energy users. For example, using solar power for buildings can receive benefit. Simultaneously, firms who use solar power, biomass, and wind for electronic generation can obtain the subsidies. Second, the revenue is used to reduce the income tax and corporate tax, which help alleviate the impacts from other taxes. For example, government reduce the tax rate for lower income group and decrease income tax for senior citizens. Third, the revenue reinvested in the environmental equipment to improve energy efficiency. The government provide free-interest for certain environmental investment.

RET stimulated the long-term growth of innovations by different fields in Netherland. According to the research, RET combined with previous policies help Netherland improve the energy-efficiency technology in various industries, including instance insulation, high-efficiency boilers, solar energy and lighting. For example, Phillips has become a pioneer in the lighting industry, which is due to the positive impacts of the environmental policy.

Actually, the RET policy has significant impacts on the energy price and labour market. First, higher energy price could induce extra investment. One the one hand, the extra jobs will be created in the service and construction sector. On the other hand, labour shortage might occur in the labour market. Second, instead of the direct investment in job creation program, the RET created a modest way to keep balance social benefits among different groups. For example, direct subsidies will the purchasing power of lower income groups, which is not beneficial for the development of labour market. Third, the RET tried to reduce the risk of double compensation for employees. For example, if employees claimed extra compensation for their cost on energy my increase the overall wage rate, which increase cost for employers and   create difficulties on job creation.

 

 

 

Resources:

http://papers.ssrn.com/sol3/papers.cfm?abstract_id=500863

http://ec.europa.eu/research/energy/pdf/nn/the-netherlands_annex-viii-report_en.pdf

http://www.wind-works.org/FeedLaws/Netherlands/NLEnergytax2004.pdf

http://www.wind-works.org/FeedLaws/Netherlands/NLgreentaxes2.pdf