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For more information, contact David Eppstein by email at
deppstein@masco.harvard.edu, or by calling 617-632-2860.

 
1.0 EXECUTIVE SUMMARY

In its June 1995 report, the End-of-Pipe Alternatives Subcommittee in Phase I of the MWRA/MASCO Mercury Work Group concluded that 29 local hospitals discharged approximately 2 percent of the total daily mass loading of mercury to the MWRA sewer system of the Boston Metropolitan Service Area. The loadings estimate of the MWRA itself was higher because of different assumptions and data. In an effort to better understand the mercury loadings contributed by these and other similar dischargers, the Facilities Loadings Subgroup of the Mercury Management Subcommittee was formed in 1996 under Phase II of the MWRA/MASCO Mercury Work Group.

The goal of the Facilities Loadings Subgroup was to estimate known and projected mercury loadings to the MWRA Metropolitan Boston sewer system contributed by hospital and medical facilities over a two-year period. The Subgroup was also asked to reexamine the mercury loadings contributed by the 29 local hospitals studied in Phase I.

The Subgroup decided to examine five study groups of hospital-like facilities as follows: clinical laboratories, medical waste incinerators, hospital laundries, other related facilities (including college laboratories, steam suppliers, pharmaceutical manufacturers, and testing laboratories), and medical and biotech research laboratories. From a list of all MWRA permitted facilities, the Subgroup found 242 of these facilities and further determined that these facilities had a total of 355 qualifying permitted discharges or sampling locations.

We found that the sampling locations of the five study groups made significant contributions of mercury to the sewer system. We estimated that, collectively, they contributed about 50 percent of the known daily industrial mercury loadings during the two-year study period. Yet, these sampling locations discharged only about 16 percent of the estimated total daily industrial discharge flow. We also estimated that their combined mercury loadings represented about 6 or 7 percent of total mercury loadings to the sewer system while their discharge flows were only about 0.5 percent of the total treatment plant headworks flow. However, since these results are based upon a limited amount of data, we advise appropriate caution in their use.

On an individual basis, we found that a typical medical waste incinerator discharged the highest mercury loadings followed by a typical medical and biotech research laboratory. In contrast, we found that a typical clinical laboratory discharged relatively high mercury concentrations but relatively low mercury loadings because of its lower discharge flows.

In Phase I of the Work Group, the End-of-Pipe Alternatives Subcommittee had estimated that the mercury discharge loadings from 29 local hospital facilities represented between 2.6 and 3.6 percent of MWRA total system loadings during the MWRA 1995 fiscal year (FY). In this new study, our results instead suggest that the FY 1995 loadings contribution from these facilities may have been between 0.6 and 0.9 percent. For FY 1996, we estimate that their loadings contribution may have been between 1.8 and 2.5 percent of MWRA total system loadings.

Finally, we found that the total average mercury loadings discharged from the five study groups may have been between 0.02 and 0.08 pounds per day over the study period. Since this sum represents such a small quantity of mercury, one sporadic peak discharge had the potential to significantly affect the overall loadings for a particular day.1 We observed such sporadic impacts in the discharge concentration data over the two-year study period for sampling locations within several clinical laboratory, medical waste incinerator, hospital laundry, and research laboratory facilities. During FY 1995, for example, the data suggests that a research laboratory may have discharged 0.24 pounds of mercury in one day and, during FY 1996, a hospital laundry may have discharged 0.11 pounds of mercury in one day.

             1Readers of this report are encouraged to refer to the Work Group's Mercury Management Plan Guidance Document for recommended guidelines to address mercury management issues including the control of sporadic high mercury discharges.

 

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08/16/2006

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