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State/local amalgam separator/BMP programs
US Navy separator/BMP program Regulated Medical Waste vs. Hazardous
Waste concerns US EPA Office of Solid Waste dental
school initiative Dental chairside trap designs Hg vapor issues
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Amalgam separators must be installed by May 2008
All dental facilities that “apply, alter, maintain, remove, or dispose of amalgam”
Excludes orthodontists, periodontists, prosthodontists, and Oral Surgeons
Separators must be 99% efficient Separator waste must be disposed of
within one year
New York
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All dentists must recycle amalgam waste Maintain written certification of recycling Dentist must notify local sewer authority
that separator is installed New offices must install separators prior
to opening Amalgam waste cannot be disposed of in
trash, medical waste containers, or sterilized in autoclaves
Pre-encapsulated amalgam only (elemental Hg banned)
New York
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Milwaukee Metropolitan Sewerage District (MMSD) requiring separators to be installed by February 1, 2008
MMSD serves 28 municipalities 317 total amalgam using offices in
district Currently 184 amalgam using offices
with separators installed (58%) Point of contact: Tom Nowicki, (414)
225-2275
Milwaukee, Wisconsin
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Milwaukee, WisconsinInfluent Mercury
0
100
200
300
400
500
600
700
9/17
/03
11/1
7/03
1/17
/04
3/17
/04
5/17
/04
7/17
/04
9/17
/04
11/1
7/04
1/17
/05
3/17
/05
5/17
/05
7/17
/05
9/17
/05
11/1
7/05
1/17
/06
3/17
/06
5/17
/06
7/17
/06
9/17
/06
11/1
7/06
Mer
cury
(n
g/L
)
Jones Island South Shore Linear (South Shore) Linear (Jones Island)
Data from Tom Nowicki, Milwaukee County Sewerage District6
Separators and BMPs required in Dane County (Madison) by 12/31/2008
Seven major Wisconsin municipalities will also require separator installations by 2008 (GLWQI – 1.3 ng/L)
Wisconsin Dental Association is cooperating with separator effort
Contact Randy Case of the Wisconsin DNR for more information (608) 267-7639
Wisconsin Statewide
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NSSD is 2nd largest POTW in Illinois No discharge directly to Lake Michigan Mandated Pretreatment systems at Naval
Base, Great Lakes Completed survey of all dentists in service
area Working towards a program requiring BMPs
and/or separators in near future Point of Contact: Sharon R. Thieszen (847)
623-6060
Gurnee, Illinois NSSD
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Separators or permits required for all dental offices placing and/or removing amalgam
MCES Maintains a list of approved separators
99% removal efficiency with ISO 11143 Testing and certification Works closely with Minnesota Dental
Association Point of Contact: Peter Berglund of MCES,
(651) 602-4708
Minneapolis/St. Paul Metro Area 7 Counties
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Voluntary effort organized by Tim Tuominen of the WLSSD
Installed separators in all dental offices serviced by WLSSD
Works with Northeast District Dental Society (MDA)
WWTP influent is down and effluent is approaching the GLWQI level of 1.3 ng/L
Point of Contact is Tim Tuominen (218) 740-4815
Duluth, Minnesota
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Connecticut (95%), Maine (95/98%, list of approved separators), New Hampshire, Vermont, Rhode Island (eastern half of state)
Massachusetts requires 98% ISO 11143 efficient separator or equivalent method acceptable to MassDEP
VT and CT include separators in BMPs and require dentists to implement BMPs
Washington requires installation of ISO 11143 separators statewide
Non-Great Lakes States/Areas
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New Jersey is working on a requirement for separators
Montana Draft Bill 1262 would require amalgam separators and recycling of amalgam waste
Warren Air Force Base, Cheyenne, Wyoming required to install amalgam separators in dental clinics
Non-Great Lakes States/Areas
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Wichita, Kansas requires ISO 11143 separators
San Francisco Bay area East Bay Municipal Utility District Contra Costa Central Sanitation
District Union Sanitary District
Palo Alto Sanitary District Toronto (one of earliest requirements) Montreal
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Non-Great Lakes States/Areas
Navy is installing separators in all dental treatment facilities
US, overseas, and ships Installing systems that remove both
particulate and dissolved Hg Also installing chairside filtration
systems that remove particulate and protect downstream plumbing lines
Working on non-mercury filling materials 14
Disposable filter elements are housed inside reusable chambers
Filter elements are made from spun polypropylene
6 inch filter element has a vendor claimed surface area of ~2.2 square feet (depth filtration)
Cost of a disposable filter element is less than $2.00 a piece
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Pore Size 50 m 15 m 1 m 0.5 mMean Hg 79.13 23.55 17.68 4.25
Sample Size 50 50 50 50
SD 71.40 23.25 17.35 6.35
Baseline Hg levels without any chairside filtration system averaged 1,087.38 mg (n=50, SD=993.92)
Units are in mean mg of Hg per dental chair per day
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Pore Size 50 m 15 m 1 m 0.5 m
% Removal
92.72 97.83 98.86 99.61
Calculated removal efficiencies = (B Hg – F Hg / B Hg) x 100; where B Hg is the baseline Hg level, F Hg is the amount of particulate Hg collected after the chairside filter)
Baseline Hg levels without any chairside filtration system averaged 1,087.38 mg (n=50, SD=993.92)
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Empty Full Pass ISO
0.5m 97.5% 96.8% Yes
15m 94.8% 96.1% No
The 0.5 m filter passed at 96.8% The 15 m filter failed at 94.8% Currently testing the 1.0 and 5.0 m filters with the
ISO protocol ISO 11143 protocol is currently up for revision to
close the “loophole” of flow rate and other changes (The threshold for maximum testing will be 1 liter/minute, where there was no threshold before)
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Reusable filter chambers require periodic cleaning to remove debris
A disposable unit has been developed to address this issue
19
Chairside filtration systems substantially reduce Hg emissions into wastewater
Low cost and minimal maintenance 0.5 m filter passed ISO 11143 protocol Location at the chair protects
downstream plumbing lines from amalgam debris
Minimal impact on vacuum levels at the HVE tip
20
In some locations amalgam waste is both a regulated medical waste (Potentially Infective Medical Waste, PIMW) and a hazardous waste
In Illinois teeth, contiguous bond and gum are excluded from PIMW classification
Some recyclers require a “certificate of disinfection” before they will accept dental waste
Medical waste is routinely incinerated or autoclaved which would release Hg to atmosphere
21
EPA is seeking to partner with US Dental Schools to develop a curriculum based dental recycling program
Student dentists Practicing dentists though CE
Gray Bag program (ANSI/ADA Specification 109)
Point of contact is David Carver, USEPA OSW (703) 308-8603
22
Standard procedure to collect, store, and prepare amalgam waste for shipment to recyclers
Disinfecting of wastes (if required by recyclers)
Keep written records: mass, name and address or recycler, etc.
Wastes include extracted teeth with amalgam fillings
23
Scrap amalgamContactNon Contact
Used capsules Chairside traps Extracted teeth with amalgam
fillings Amalgam from amalgam
separators and vacuum pump filters 24
Landfills vs. Retorting Facilities Need for the disinfection of
amalgam waste? Universal Waste Laws
Ease regulatory burdens Promote proper recycling,
treatment, or disposal Provide for collection
opportunities 25
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Most dental chairs have built in chairside traps
While not originally designed to function as amalgam separators, chairside traps remove substantial amounts of amalgam waste
There is confusion in the literature concerning pore sizes of traps
This project used image analysis to obtain more accurate estimates of trap pore sizes from four selected chairside traps
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Uncovered type trap
Trap used in new ADEC Dental chairsCovered trap
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Example of an inline chairside trap after 5 days of use
29
SEM of amalgam waste from removal of amalgam restorations. Note that
the particles have high aspect ratios.30
Length,μm
Width,μmFeret’s
1,μmAspect 2
Trap 1 n=99
1156.76 (108.81)
1121.51(103.51)
1348.95(21.56)
1.03(1.01)
Trap 2n=110
1126.61 (233.73)
1038.54(293.90)
1239.74(242.77)
1.41(4.56)
Trap 3n=200
749.18 (77.79)
600.44 (122.99)
889.45 (87.36)
1.43(1.44)
1 Feret’s Diameter is the greatest dimension between any two points along the boundary
2 Aspect is the ratio of the longest dimension to shortest dimension
Table 1: Mean and Standard Deviations (SD) from Traps with Square Pores
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Table 2: Mean and Standard Deviations (SD) Trap with Round Pores – Trap 4
Diameter,μm (max)
Diameter,μm
(min)
Diameter,μm
(mean)Roundness 3
Trap 4n=199
936.18(29.07)
894.63 (79.55)
918.84 (55.00)
1.37(1.96)
3 Roundness is a measure of how far the pore shape differs from a circle
32
Trap 1 – DentalEZ
33
Trap 2 – Pinnacle Products, Inc.
34
Trap 3 – Pinnacle Products, Inc.
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Trap 4 – Parts Warehouse, Inc.
36
All traps had at least one dimension greater than 700μm
When traps are the only Hg abatement mechanism, our findings suggest greater potential for Hg emissions than was previously assumed
Manufacturers have the opportunity to contribute to the reduction of environmental Hg contamination
Covered traps help prevent waste amalgam from entering plumbing lines
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Recycling means that more amalgam waste is “stored” in dental treatment rooms
May result in Hg vapor levels exceeding human exposure limits
Another issue is Hg vapor levels in exhaust air from dental vacuum systems
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A Permissible Exposure Limit for Hg vapor is a time weighted average for an 8-hour workday and a 40-hour workweek. This is the legally enforceable limit for the workplace
B Recommended Exposure Limit for Hg vapor for up to a 10-hour workday and 40-hour workweek
C Hg threshold limit value as a time weighted average for an 8-hour workday and a 40-hour workweek
Federal OSHA PELA 8-Hour TWA 0.1 mg/m3 (100,000 ng/m3)
NIOSH RELB 8-Hour TWA 0.05 mg/m3 (50,000 ng/m3)
ACGIH TLVC 8-Hour TWA 0.025 mg/m3 (25,000 ng/m3)
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Location Hg Vapor Levels
Open Oceans 1-2 ng/m3
Urban Atmosphere 2-20 ng/m3
Coal-Fired Power Plants
(Combustion zone)1,000-20,000 ng/m3
Great Lakes, IL, USA 13.2 ng/m3
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We’ve surveyed a number of dental operatories
Hg vapor levels in breathing zone is well below OSHA/NIOSH/ACGIH exposure levels
Hg vapor levels inside recycling containers can exceed exposure levels
Care should be taken when opening containers 42
Clinic I(110 chairs)
Clinic II(30 chairs)
Clinic III(2 chairs)
Hg, ng/m3 45,316 73,737 35,421
ng of Hg/min
532,684 131,353 18,079
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Mean for all three clinics and both methods was 51,684 ng/m3
Exhaust air form dental vacuum systems contains 3,915 times more Hg than ambient air samples
Exhaust air from dental vacuum systems had 2.6-to-51.7 times higher concentration of Hg than flue gas from combustion zones in coal-fired power plants
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