From Intro
In the United States, there are an estimated 4.2 billion mercury-containing lamps in circulation, of which about 4 billion are fluorescents (14). Some 700 million of these lamps are discarded annually (15). Several studies have examined the loss of mercury from fluorescent bulbs, most of them focusing on the disposal stage (15-17). More general research on the material flows of mercury also typically covers the lighting sector (18-20). According to these studies, mercury contained in fluorescent bulbs is emitted to the atmosphere in three primary ways: bulb breakage during transport, vaporization during incineration, and evaporation from landfills. Estimates of emissions from end-of-life handling of fluorescent bulbs range from 6.6% to 30% of the contained mercury, most due to breakage in transit. The most comprehensive analysis, which is still highly uncertain, estimates that approximately 13% of the mercury contained in fluorescent lamps is eventually released to the atmosphere (18). Proper recycling can reduce the environmental burden of lamp disposal. In aggregate, proper recycling (with mercury recovery) is applied to approximately 20% of all discarded bulbs in the United States, accounting for the recovery of almost 2.3 tons of mercury (2).
While there are strong concerns about mercury losses to the environment from breakage, fluorescent lamps also decrease total emissions of mercury through reduced demand for electric power. The relative risks posed to humans and the environment by release of mercury through power plants versus that of fluorescent light bulbs is complex. The toxicity of elemental or inorganic mercury that one might incur from direct exposure to a broken bulb is significantly less than that of organic mercury and is primarily associated with chronic exposure. Organic mercury, most commonly methyl mercury, formed through biological processes following deposition of inorganic mercury in the environment from sources such as power plants, is known to have a wide range of serious toxicological end points.
Nearly all (99%) mercury emissions from the power generation sector are a result of coal-combustion (9). This indicates that any potential reduction in mercury emissions is largely dependent on the characteristics of the coal-fired power sector and the specific coal being used for energy generation. Previous research into net mercury emissions from fluorescent bulbs has focused simply on the percentage of coal in the mix of electricity generation; however, other important factors include the quality and mercury content of the coal, the level of coal precleaning, power plant thermal efficiencies, electricity imports/exports, and any mercury control technologies that are utilized.
The present study aims to incorporate these factors into a detailed geographic accounting of the tradeoff between reduced atmospheric mercury emissions from the energy sector through the use and disposal of fluorescent bulbs and direct mercury emissions at end of life, both domestically and globally. Clearly there are other benefits associated with reducing electricity demand, particularly the reduction of energy use and associated greenhouse gas emissions; however, this study focuses on mercury only. As such, this quantitative analysis will provide insight as to where fluorescent lamp use is most beneficial in terms of reducing total atmospheric mercury emissions, considering both energy savings and bulb disposal. A global perspective is important as atmospheric mercury is a transboundary pollution issue; for example, current estimates are that less than half of all mercury deposition within the United States comes from domestic sources (21), with much of the balance originating from industrial facilities in Asia.
Selected parts of discussion
The analysis reveals a large geographic variation in the net emissions of mercury that can be prevented by a marginal increase in the use of fluorescent bulbs. This is true both for the United States and globally. In general, for regions where coal is a major source of power, the substitution of CFLs for incandescent bulbs will result in a significant reduction in mercury emissions to the atmosphere. In places where coal will contribute less to electricity production or if energy portfolios expand to include renewables as a substitute for coal, the relative reduction of mercury emissions from this substitution would decrease.
For the United States, the greatest reduction in emissions occurs in North Dakota, West Virginia, and New Mexico, all of which derive more than 85% of their electricity from coal. Interestingly, both Indiana and Wyoming use a higher percentage of coal and yet the reductions in those states is approximately half of that of New Mexicos. This is due primarily to differences in coal quality and mercury content, precombustion treatment of coal, and the use of pollution control technology. There are several states where marginal increases in the use of CFLs will result in increased atmospheric mercury emissions, namely Alaska, California, Oregon, Idaho, Vermont, New Hampshire, Maine, and Rhode Island. All of these states use little coal for electricity production, with the notable exception of New Hampshire (18.3%), which has a fairly low input mercury emissions rate for its coal (39).
.....n general, it appears that increasing the use of fluorescent lighting is an effective way to reduce life-cycle mercury emissions. In countries where there is a small percentage of coal-based power generation and little to no recycling, the use of fluorescents may instead increase national atmospheric mercury emissions. It is also the case that many of the countries where fluorescent lighting would be most effective at reducing emissions are also places where recycling infrastructure is lacking, such as those in Central Asia and southern Africa.
.....luorescent Lighting Policy Analysis
Around the world, there are a number of interesting policies regarding fluorescent lighting that have been enacted in recent years or are being discussed. These fall into three general categories: those that limit the amount of mercury in bulbs, those that mandate increases in recycling rates for fluorescents, and those that restrict the use of incandescents. There are also national and state programs to promote the use of CFLs, particularly for residential customers (40).
In the European Union, the use of mercury and several other heavy metals in products is prohibited through the Restriction of Hazardous Substances (RoHS) directive, which went into effect July 1, 2006. However, fluorescent lamps with 5 mg or less of mercury are eligible for an exemption, due to their usefulness for energy savings and a lack of functional alternatives (41). Canada has a standard in place to reduce the amount of mercury in lamps by 80% from 1990 baseline levels by 2010 (37).
Increasing the recycling rate of fluorescent bulbs clearly shifts net mercury emissions, as shown in Figure 4. The United States aims to increase fluorescent lamp recycling rates to 80% by 2009 (35). By achieving this rate for the more than four billion fluorescent lamps currently in service, our analysis indicates that the United States would reduce the amount of mercury emitted to the atmosphere from the treatment and disposal of these bulbs by two-thirds, for a total savings of nearly 2 Mg (metric tons) for the current stock of fluorescents. Emissions can be reduced further through safeguards against mercury losses from lamp breakage during transport, such as plastic sheathing or other effective end-of-life packaging.
National and regional governments in Australia, Brazil, Canada, New Zealand, and several European countries (among others) have policies banning the future sale and/or use of incandescents; in December of 2007, the United States enacted similar legislation to phase out the use of incandescent bulbs by 2012−2014 (42). A significant proportion (40%) of the several billion incandescent bulbs currently in use in the United States are for small fixturesthese will likely be replaced by small, low-power solid state bulbs such as light-emitting diodes (LEDs) (43). But the remainder may well be substituted with low-mercury-content CFLs. Assuming that demand for residential lighting grows at an annual rate of 0.8% (43), that in 2012 all large incandescent bulbs will be replaced by CFLs, that the recycling rate will increase to 25%, and that the power mix will be unchanged from the current situation, the United States will avoid approximately 25 Mg of mercury emmisions.
......The private sector is also working to reduce mercury emissions from fluorescents, both by manufacturing low-mercury-content lamps and by increasing recycling and mercury recovery. Many of the largest CFL manufacturers such as GE, Royal Philips, Osram Sylvania, and Lights of America have achieved mercury levels 50% or more below the NEMA 5 mg standard. Looking to the future, the U.S. Department of Energys Vision 2020 project brought together researchers, manufacturers, and policy makers to push for the elimination of mercury from CFLs by 2020 (46). These reductions, coupled with appropriate handling systems and new technologies for the end of life could help reduce the negative impacts on human health and the environment.