Mercury Recycling in Artisanal Gold Mining: The Good and the Bad
The promotion of simple mercury recycling technologies called retorts to reduce human exposures and environmental contamination is one of the most widely
recommended interventions in artisanal and small-scale gold mining (ASGM)
communities. However if they aren't introduced correctly, retorts are often
abandoned or misused, which wastes resources and develops cynicism from miners, prevents reduction of environmental contamination, and in some cases actually increases mercury exposures.
Retorts are relatively
simple devices that condense and collect the mercury vapour released from
heating gold mercury amalgam. The collection and capture of mercury is
important to reduce both the amount of mercury contamination released into the
air and to reduce direct human exposure. There are many different types of
retorts – from simple kitchen bowl retorts made from a series of bowls purchased
from the local market, to custom welded retorts with water-cooled condensers.
Retorts are relatively inexpensive to build
and operate, they are simple and intuitive in construction and use, and they can significantly reduce environmental
contamination and human exposure. However, in order for them to do this
successfully, proper instruction with sufficient education is crucial. To
illustrate this, here are three case studies and lessons from the AGC’s field
work (names are changed):
1. Financial
incentives for using retorts can be misleading.
- Retorts don’t always save money and in some cases actually incur a cost, especially for small amounts of amalgam.
- Promoting the financial benefits of retorts with out a proper cost benefit understanding is risky and can fail; but health benefits of proper use are universal.
2. Field
retorts always leak dangerous mercury vapour and need to be used outside.
When retorts are introduced
into Mariam's community she is relieved to have a tool to protect herself and
her family from mercury, which she had heard is dangerous and possibly illegal.
Her husband now uses the new retort donated to him to burn the amalgam in their
house. On a typical day, her husband burns about 3 grams of amalgam in a retort
that is approximately 95% efficient at capturing mercury. This efficiency is
typical of a well-designed field retort that is used correctly, but some only
capture 80%. The 5% of the mercury vapour that leaks from the
retort produces an indoor air concentration that is 50 times higher than
the WHO occupational limit [2]. In addition to the acute exposure,
burning indoors will also cause long-term chronic exposure to the family because
mercury sticks to the household walls and surfaces and is re-emitted overtime into the
air.
Burning amalgam indoors, even with a retort, causes acute and long term mercury exposure.
Burning amalgam indoors, even with a retort, causes acute and long term mercury exposure.
- If mercury is illegal, burning inside of houses or cars becomes more common.
- Retorts should never be used in areas that women and children frequent because they are much more sensitive to mercury poisoning.
3. Used
retorts are highly contaminated and emit mercury vapour into any area where
they are stored or transported.
Lemah is very happy when a pilot project
was launched in his community and he was chosen to receive a retort. Only 10 retorts were given out and he was
eager to use it. He and some friends use the retort outside where they apply
the heat but then he stores it under his bed when he isn't using it for safe
keeping. While it is stored under his bed, the retort releases residual mercury vapour into
his bedroom exposing himself and his family to dangerous levels over long periods of time.
- Retorts should always stay outside or in a dedicated contamination zone with good ventilation.
- Retorts should not be transported inside the passenger cabin of a car.
Summary
Retorts can be an excellent tool in
reducing mercury consumption, environmental contamination and human exposure if
they are introduced with the proper training and education. However, without a
carefully thought-out intervention, the intended benefits of retorts can fail
and in some cases actually increase human exposure to mercury. This is
particularly concerning when women and children are endangered through
unintended secondary exposures, as they are more susceptible to mercury
toxicity. With the creation of the
Minamata Convention, mercury-reduction interventions in ASGM communities will certainly
increase, and so too will the importance of proper retort training. When a
retort intervention is being planned, consider these three key points:
- Retorts don’t always save money so other incentives need to be explained and re-enforced such as the protection of health.
- Retorts leak mercury so they must be used outdoors and away from women and children.
- Used retorts are contaminated and continuously emit residual mercury, so they must be stored in a dedicated well-ventilated contamination zone (typically outside) and not be transported in a closed car.
Footnotes:
Spot $ = $1400/toz (31.1 g/toz) = $45/g
Sponge gold is 50:50 Au:Hg, 0.26 g of gold
Miners in most regions get at least 70% of spot price in the field.
0.26 g Au = ($45/g * 0.26 g * 0.70) = $8.19
0.26 g Au = ($45/g * 0.26 g * 0.70) = $8.19
Field price of Hg = $200/kg = $0.2/g
0.26 g of Hg = 0.247 g of Hg = $0.05
$0.05/$8.19 * 100 = 0.6%
~ The relative cost of the lost Hg is < 1% of the value of the gold.
$0.05/$8.19 * 100 = 0.6%
~ The relative cost of the lost Hg is < 1% of the value of the gold.
1. Inside a hut without a retort
Volume of a hut = volume of a cone + cylinder
Cone : height = 2 m; radius = 2 m; volume
= 1/3piR2 = 4.189 m3
Cylinder: height = 2 m; radius= 2 m; volume =
piR2H = 25.13 m3
Air volume of a hut = 4.189 + 25.13 = 30 m3
Air concentration if 1.5 g of Hg is burned (50%
of amalgam is Hg, 50% is gold) = 1.5 g/30m3 = 1,500,000,000 ng/30m3
= 50,000,000 ng/m3
The WHO occupational limit for Hg
concentrations in air = 50,000 ng/m3
50,000,000 ng/m3 /50,000 ng/m3
= 1000
~ The
mercury air concentration in the hut would be 1000 X higher than the
occupational limit.
2. Inside a hut with a retort
Retorts are ~95% efficient at capturing mercury
(5% in the air of the hut)
Air concentration (from calculation 1. above) = 0.05 * 50,000,000 ng/m3 =
2,500,000 ng/m3
2,500,000 ng/ m3/50,000 ng/ m3=
50
~ Even
with a retort, the mercury air concentration in the hut would be 50 X higher
than the occupational limit.
3. Outside in an open bowl
949,000 ng/m3 = time-weighted average of breathing zone
concentrations during two 8-hour work shifts for burners (Drake et al., 2001)
50,000,000 ng/m3/949,000 ng/m3
= 526.9
~
Burning amalgam outside rather than inside, even without a retort, reduces
exposure by more than 500 times. However, this increases
environmental contamination.
4. Outside in a retort
2000 ng/m3 = Air concentration
during a burn with a retort at 1.5 m distance (personal communication, 2013)
949,000/2000 ng/m3 = 474.5
~ Using a retort reduces Hg air concentrations
by 475 times when used outdoors, provided the retort is not opened until it is
cool.
This is cool!
ReplyDeleteAlways keep a layer of water on top of the mercury when storing in a container. Mercury will evaporate at roughly 65 degrees F
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