Complexing Agent Control of Leachable Mercury in Fluorescent Lamps

This invention is directed to mercury vapor arc discharge lamps in which the arc discharge takes place in mercury vapor, including conventional phosphor fluorescent lamps and more particularly to avoidance of mercury pollution of landfills and groundwaters upon disposal of such lamps and during testing for leaching of toxic materials from such lamps and to compositions of matter which include metal complexing agents useful in preventing the formation of leachable mercury in disposal and testing procedures. The lamps provided herein are characterized by reduced solubilization and leaching of mercury when the lamp is pulverized for testing or upon disposal.

Low pressure mercury arc discharge lamps are standard lighting means which include electrodes sealed in a glass envelope, the interior of which may be coated with a phosphor. The lamp also contains a small amount of mercury and an inert gas at low pressure, of about 1 to 5 torr. The term lamp, as used herein, means the complete unit including the glass envelope and the end pieces and plugs for mounting in a lamp fixture, and wires which connect the internal components of the envelope with the end pieces.

During manufacture of fluorescent or low pressure mercury arc lamps an amount of elemental mercury (Hg.sup.0) is sealed in the lamp envelope. Most of the mercury adheres to the phosphor coating, a small amount being in the vapor phase.

During operation, alkali metal carbonates from the electrodes decompose and form free oxygen in the lamp. The oxygen can react with a portion of the mercury to form soluble mercury oxide (HgO). Soluble mercury oxide is leachable from landfills and other disposal facilities. Soluble mercury oxides or other oxidized forms of mercury generated or produced in the course of the test are detrimental to the accuracy and the reliability of the standard test for determination of the leachability of toxic materials from lamp waste. This test is generally referred to as the Toxicity Characteristic Leaching Procedure or TCLP test.

There is concern about the environmental impact of soluble mercury compounds which can leach into ground water sources, rivers, streams, and the like.

Ferric and cuprous ions form soluble compounds which are capable of oxidizing elemental mercury to the monovalent, mercurous, form which is soluble in an acidic aqueous environment and therefore leachable. The formation of ferric and cuprous compounds depend on exposure to and reaction with oxygen. Complexing agents which bind ferric and cuprous ions alter the oxidation/reduction potentials of the ions so that their oxidizing power is reduced. Such compounds, either organic or inorganic, incorporated in the lamp reduce oxidizing power of ferric and cuprous compounds, thereby greatly reducing or preventing the formation of leachable mercurous and mercuric compounds resulting from oxidation of elemental mercury.

The invention provides a mercury vapor discharge lamp comprising an envelope of light transmitting glass which contains, an inert gas and an amount of elemental mercury, a pair of electrodes for establishing an arc discharge, and an effective amount of at least one metal complexing agent.

The lamp further comprises at least one base or end cap which defines a cavity having an inner surface, and which is secured to the lamp envelope by a basing cement, the complexing agent being disposed within said cavity. Generally such lamps have a pair of end caps.

The complexing agent is admixed with the basing cement securing the end caps in place on the glass envelope.

The invention further provides complexing agent containing compositions which can be included in the lamp structure for the purpose of controlling oxidation potentials of iron and copper in order to minimize or prevent formation of soluble mercury compounds, thereby reducing or preventing formation of water soluble leachable mercury compounds in landfills or TCLP test samples.

In a preferred embodiment of the invention, the mercury vapor discharge lamp is provided with an complexing agent carried on the inner surface of the cavity by means of an inert water soluble adhesive binder.

FIG. 1 is a partially broken away section of a low pressure mercury fluorescent lamp 1 comprising a glass envelope 2 having a phosphor coating 9 on the inner surface of the glass. Connector pins 6 are in electrical contact with leads 4 and 5 and also with electrodes 3.

In FIGS. 2 and 3 the end caps are shown as 2, corresponding to numeral 8 of FIG. 1. The end cap is provided with connector pins 6 and complexing agent 8 deposited in the cavity of end cap 2.

The incorporation of complexing agents in a lamp structure or in the TCLP test solution reduces the oxidation potentials of iron and copper from metal components to a form which is soluble but not capable of oxidizing elemental mercury to a soluble form of mercury oxide. Accordingly there is a reduction or prevention of leachable mercury compounds.

The formation of leachable mercury when fluorescent lamps are broken and exposed to landfill conditions can be prevented or minimized by preventing oxidation of certain components of the lamp. Certain metal components of fluorescent lamps particularly iron-containing lead wires, copper coated leads, and any brass components generate ferric (Fe.sup.+3) and cuprous (Cu.sup.+1) ions when exposed to moisture, oxygen, and acidity.

In order to address the growing concern that excessive amounts of mercury from disposal of fluorescent lamps might leach into surface and subsurface bodies of water, the Environmental Protection Agency has established a maximum concentration level for mercury at 0.2 milligrams of leachable mercury per liter. This is generally determined by the standard analysis known as the Toxicity Characteristic Leaching Procedure (TCLP), a well known test procedure.

In carrying of the TCLP test, the lamps are pulverized to form lamp waste material similar to that which would result from lamp disposal in landfills or other disposal locations. The ambient conditions in such locations may be such as to promote formation of leachable mercury just as the TCLP test conditions themselves tend to allow for formation of leachable mercury in amounts greater than the established limit of 0.2 milligrams per liter.

It has been found that elemental mercury added to mercury-free pulverized lamp materials prepared for the TCLP test is converted to leachable mercury in the course of the test. If elemental mercury alone or in combination with various glass, phosphor, or non-metal lamp components is tested, little or essentially no leachable mercury is found. When elemental mercury is tested in combination with metal lamp components such as copper or iron, lead wires, pins, or other metal hardware, the mercury is transformed into a leachable form.

It was determined by controlled experimentation that both ferric iron (trivalent) and cuprous (monovalent) copper are generated under the TCLP test conditions when carried out in the presence of oxygen and that these ionic species are able to oxidized elemental mercury to soluble mercury compounds which are measured as leachable mercury.

Corrosion or dissolution of metals from the metallic state requires the presence of both oxygen and a solvent such as water conditions that exist in the TCLP test and landfill situations.

Organic or inorganic metal complexing agents incorporated into fluorescent lamps during manufacture become operative in the course of preparing lamps for the TCLP test or upon destruction of the lamp during disposal. The presence of such complexing agents will make the TCLP test more accurate and reliable and will reduce the formation of soluble mercury compounds when the lamps are disposed of.

Suitable complexing agents include any metal chelating materials, compounds, or compositions which reduce the activity of ferric and cuprous ions in the mercury-containing environment. Illustrative complexing agents include sodium gluconate and ethylenediamine tetraacetic acid (EDTA) or a salt thereof, and nitrilotriacetic acid (NTA). Sodium gluconate is a preferred complexing agent for use in this invention.

The principles and practice of this invention will be more fully understood when considered in view of the following examples.

All TCLP test data was obtained by the test procedure prescribed on pages 26987-26998 volume 55, number 126 of the Jun. 29, 1990 issue of the Federal Register.

Briefly, lamps being tested are pulverized into particulate form having the prescribed particle size which is capable of passing through 3/8 inch sieve. The test material is then extracted with a sodium acetate-acetic acid buffer at a pH of about 4.93.

To prevent the spurious formation of leachable mercury upon disposal of mercury vapor discharge lamps and to improve the reliability of the TCLP test an effective amount of complexing agent is incorporated in the lamp structure, for example within the glass envelope exterior to the plasma discharge or in an end-cap, or in the base of the lamp. An effective amount of the complexing agent is that amount which will substantially prevent formation of ferric and cupric compounds which can oxidize elemental mercury to a soluble form. In general, an effective amount of the complexing agent will be enough for the TCLP test results to show the presence of less than about 0.2 parts per million of leachable mercury.

The formation of soluble mercury compounds is illustrated by the data in Table 1, below. Carrying out the TCLP test in the presence of air generates about 1 part per million of copper and about 0.3 parts per million of soluble iron. The amount of soluble mercury formed under these conditions exceeds the regulatory limit of 0.2 parts per million. Increasing the exposure to oxygen increases the amount of soluble copper and soluble mercury formed. Decreasing exposure to oxygen decreases the formation of soluble copper and soluble mercury

When the amount of oxygen is varied by increasing the volume of the head space in the TCLP test jar, the effect of both soluble iron and copper on the formation of soluble mercury is evident from the data in Table 2, below. As the head space volume increases, the amount of soluble mercury increases in response to the formation of increasing amounts of soluble copper and iron.

When a complexing agent is added to the t solution, the formation of soluble mercury is reased as shown in Table 3, below.

Table 3 shows examples if complexing agents which have been added to the TCLP extraction to study the effect upon leachable mercury. The first entry is a control showing the amount of leachable mercury generated when the pulverized lamp is dosed with 20 mg of elemental mercury. The leachable mercury generated in that case is 745 ppb in the absence of any complexing agent. The complexing agent can be incorporated in the lamp by encapsulation of the material in a glass capsule that can be placed either in the base of the lamp between the aluminum cap and flare of leaded glass, or placed within the positive column of the lamp. Since the complexing agent is enclosed in a glass capsule it could be present in the inside or positive column of the lamp without affecting lamp function.

The complexing agent material can also be incorporated in the basing cement of the lamp that holds the aluminum cap to the leaded glass portion of the end of the lamp. The basing cement generally comprises about 80 weight % marble flour (limestone-CaO), and the balance shellac a phenolic resin binder, a solvent for blending, and a dye used to color the cement. The cement is dispensed through a feeder into the base and heated to cure once assembled with the lamp. Curing drives off the solvent and solidifies the cement. The complexing agent is blended with the cement components and incorporated into a lamp manually or by automated manufacturing equipment. The complexing agent is released only when the lamp is destroyed or crushed in preparation for TCLP testing. In this method the active scavenger material is always exterior to the positive column of the lamp.

Another method for incorporating the active complexing agent material in the lamp structure is to admix it with an inert water soluble adhesive carrier or binder. Gums and gelatins have been used as such adhesives and binders. The nature of the gums and gelatins is that they adhere to surfaces when heated. The composition containing the complexing agent material can be placed on the inner surface of the aluminum end cap as a ring or discrete button. When the lamp is crushed and exposed to an aqueous environment or placed in the TCLP solution, the water soluble binder allows the complexing agent to be released quickly.

The ability of sodium gluconate and related complexing agents to inhibit formation of soluble mercury in the TCLP test is shown by the data in table 4, below.

Chelating agents are incorporated into the lamps or test solutions in an effective amount. An effective amount is that amount which will result in less than 200 parts per billion (0.2 ppm) of leachable mercury. The effective amount of any complexing agent for any amount of mercury per lamp can easily be determined by routine dose response data. Table 5, below, shows dose response data in parts per million of leachable mercury for several complexing agents and a range of amounts of complexing agent. The amount of mercury metal was 20 mg per lamp. The TCLP tests were carried as described above. About 0.2 to about 3 grams, and preferably about 2 grams, of complexing agent per lamp is generally effective to control the formation of soluble mercury within regulatory limits.