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No. 104 - Miljøstyrelsen

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28<br />

time unit, but this formula (as illustrated with the graph above) only applies to<br />

the average content of mercury of 4.55 mg of mercury per straight fluorescent<br />

lamp.<br />

Stahler et al. (2008) has also made measurements of release of mercury from<br />

compact fluorescent lamps in a room of around 12.7 m 2<br />

and with a floor-toceiling<br />

height of around 3 m 2 , corresponding to a volume of around 39 m 3 .<br />

The tests were made with different lamps, flooring, ventilation scenarios and<br />

cleaning scenarios. Many different tests were made, but one lamp was broken<br />

at a time after which a new test (new lamp with new flooring material etc.)<br />

was analysed. The concentration of mercury was measured at a height of<br />

around 30 cm (corresponding to the inhalation height of a child) and at a<br />

height of around 1.5 m (corresponding to the inhalation height of an adult).<br />

To simulate worst case new compact fluorescent lamps were broken with a<br />

hammer, and measurements showed a tendency to higher concentrations at<br />

30 cm height than at 1.5 m height in tests without vacuuming. This reflects<br />

that mercury vapours are very heavy and concentrate near the floor. The tests<br />

showed that when one compact fluorescent lamp broke mercury<br />

concentration in the air of the room often exceeded 0.0003 mg Hg/m 3<br />

for a<br />

period of time (corresponding to the USEPA reference long-term<br />

concentration without hazardous effects (RfC)). Short fluctuations with<br />

concentrations above 0.05 mg/m 3 (upper measurable limit) were also<br />

registered. In comparison, Danish occupational threshold limit values for<br />

mercury vapours are at 0.025 mg Hg/m 3<br />

during a workday (AT, 2007).<br />

It was seen, however, that a short period of ventilation of the room (open<br />

window) in most cases reduced the mercury concentration significantly, both<br />

in 30 cm’s height and in 1.5 m’s height. For all tests (a total of six) the<br />

concentration in 30 cm’s height decreased to below 0.0003 mg Hg/m 3 within<br />

9½ minutes after breakage of the lamp. Concentrations increased again,<br />

however, when the room was no longer ventilated, especially for some types of<br />

lamps as well as during and after vacuuming. Measurements showed that<br />

there are large differences between different types of compact fluorescent<br />

lamps, and between the period of time before mercury concentrations<br />

decrease to below 0.0003 mg/m 3<br />

.<br />

One test was also conducted with a cracked lamp instead of a broken lamp as<br />

well as one test where lamps were warm further to use. The results from these<br />

tests were similar to results from previous studies (Stahler et al., 2008).<br />

The main conclusion of the Stahler et al. (2008) study was that the release of<br />

mercury vapour is much more variable for scenarios with compact fluorescent<br />

lamps from different manufacturers than between different accident and<br />

cleaning scenarios with compact fluorescent lamps from the same<br />

manufacturer. In other words, release of mercury depends more on type of<br />

lamp, i.e. especially quantities of mercury in the lamp and it may also depend<br />

on the mercury compound found in the lamp. In the study six different<br />

brands of compact fluorescent lamps with different effect were used so results<br />

from the study are assumed to represent a general picture if a compact<br />

fluorescent lamp should break in a home.<br />

Stahler et al. (2008) is concerned about postponing cleaning after an accident<br />

with a broken compact fluorescent lamp. Three tests were made with exactly<br />

the same type of lamp, but with cleaning after 1 minute and 46 minutes after<br />

the accident. It was seen that even if the initial mercury concentration was the

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