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RIGHT SOLUTIONS · RIGHT PARTNER
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RIGHT SOLUTIONS · RIGHT PARTNER
A Guide to Trace and Ultra-Trace Mercury Testing in Water
Blair Easton
General Manager – ALS Environmental Calgary
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Presentation Overview
• Mercury Sources
• Mercury Cycle
• Anthropogenic Mercury Sources in Alberta
• Relative Mercury Concentrations
• Regulatory Limits
• Sampling Considerations
• Dissolved Mercury Sampling
• Field & Transport Blanks
• Mercury Analysis
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Mercury Sources
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Mercury Cycle
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Anthropogenic Mercury Sources - Alberta
Mercury is of particular concern in the northern rivers of Alberta.
Where Coal Power Generation Plants are a source of Anthropogenic Mercury.
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Anthropogenic Mercury Sources - Alberta
Both bitumen and oil sands tailing ponds are known to contain
traces of mercury.
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Relative Levels of Mercury Concentration
• Typically Trace (low level) Mercury =
results between 5 - 50 ng/L (ppt).
• Typically Ultra-Trace Mercury = results
between 0.1 – 5 ng/L
One part per trillion (1 ppt) is a proportion equivalent to a drop of water diluted into 400Olympic-size swimming pools.
1ppt = 0.001 ppb = 0.000001 ppm
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Mercury Regulatory Limits
• The lowest AB Tier I Ground Water
Remediation Guideline = 5 ng/L
(i.e. the Aquatic Life guideline).
• AB Regional Aquatics Monitoring
Program (RAMP) has the lowest
reported result for Total Mercury
at 0.2 ng/L and the average
result is ~3 ng/L.
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Sampling Considerations
• The potential for contaminating ambient water samples
with the mercury and interfering substances cannot be
overemphasized.
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Contamination Sources
Sources of contamination can include:
Metallic sampling equipment
In-appropriate & Un-tested Sample
containers
Sampling gloves (e.g. powdered gloves)
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Contamination Sources
Atmospheric inputs such as dust and dirt from:
Automobile exhaust
Roads, bridges, wires and poles
Cigarette smoke
And, the Sampler – e.g. older dental work
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Historic Mercury Sampling Containers
• Until recently, the most
common container type
and preservative used for
routine or low level
mercury analysis of
waters was:
The High Density Polyethylene (HDPE) plastic container with nitric acid (U.S. EPA Method 245.1, 1972).
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New Trace Level Mercury Sampling Requirements
• Pre-cleaned Borosilicate
glass container with
Teflon®
lined cap with 1:1
Hydrochloric acid (HCl).
EPA Method 245.7 (2005)
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Ultra-Trace Level Mercury Sampling Requirements
• Pre-cleaned borosilicate glass or Teflon®
container with 1:1 Hydrochloric acid (HCl).
EPA Method 1631 E (2002).
The EPA further recommends the use of the
"clean hands/dirty hands" technique during
field sampling.
Some labs recommend no preservation with
(1:1) hydrochloric acid as it acts as a strong
magnet for contamination.
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Clean Hands Dirty Hands Procedure
• EPA 1631 E recommends
to follow the US EPA
“clean hands / dirty
hands” (EPA 1669)
sampling protocols when
conducting ultra-trace
mercury analyses.
EPA Method 1669: Sampling Ambient Water for Determination of Trace Metals at EPA Water Quality Criteria Levels (Sampling Method).
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Dissolved Mercury Sampling
• Filtration for dissolved
Hg should be conducted
within one hour of
sample collection using
a suitable in-line filter or
0.45 μm syringe filter.
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Field & Transport Blanks
Field Blank
A sample prepared in the field using
analyte free water and incorporate all
aspects of sampling operations.
Transportation Blank
A sample in which the analytes of
interest are absent is prepared by the
laboratory and shipped with sample
containers.
It travels to the sampling site and returns
with the collected samples.
Transport Blank
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Mercury Analysis
• Mercury Instruments
Some instruments use
enclosed samplers to
prevent sample
contamination.
• Mercury Analysis Labs
Dedicated rooms for ultra-
trace mercury analysis
prevent cross
contamination from
routine level samples.
Open Air Sampler Enclosed Sampler
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Questions