email: tfl3543@blackfoot - United States Antimony Corporation

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email: tfl3543@blackfoot.net
BEAR RIVER ZEOLITE CO., INC.
4005 East Glendale Road
Preston, ID 83263
tel: 406-827-3523
fax: 406-827-3543
PRODUCT DESCRIPTION
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Sizes: ½” x 4, 4 X 14, 14 x 40, 4 X 8
Surface Area: 24.9 square meters per gram
Weight: 55 pounds per cubic foot
CEC: Cation Exchange capacity 160 to 180 meq/100 grams
ZEOLITE BASICS
Zeolites are a group of volcanic minerals that are hydrated calcium potassium sodium aluminosilicates in which water is
held in channel ways by absorption. The lattices are negatively charged, and they loosely hold positively charged
cations such as calcium, sodium, potassium, and ammonium. Their ability to exchange one cation for another is known
as their “cation exchange capacity” or CEC. Once the ammonium ion is in the lattice, it is not water-soluble. They
chemically filter
out the ammonium.
BRZ™ zeolite is especially adapted as a direct replacement for sand, sand and anthracite, and multi-media water
filtration media. It has a much finer nominal rating (3 to 5 microns) than sand (20 microns), and consequently it filters out
more fine particulates. See Usage documents on water filtration.
INTRODUCTION TO AQUACULTURE
Oxygen and ammonia are the two most important parameters in aquaculture. The oxygen is relatively easily controlled,
but the ammonia is much more difficult. Ammonia, the un-ionized form of ammonia (ammonia gas) is produced from the
gills and urine from the fish as well as from the bacterial decomposition of the unused food and fecal material. Fish
utilize the nitrogen component of digested proteins, the amino group (NH2) to build new proteins. However, when they
utilize the proteins for energy, they cannot metabolize the nitrogen, and the amino group is split off as ammonia gas.
Ammonia gas solubilizes readily in water to form ammonium ion. Ammonia is toxic, and it reduces the ability of the
hemoglobin in the blood to hold oxygen. Additionally, ammonia damages the gill structure further impairing the fish in
getting oxygen.
There are three ways to reduce ammonia in the water. First would include mechanical filtering of unused food and fecal
material. Although sand and charcoal have been used extensively, zeolite is much more effective. It has a nominal
rating of 3 to 5 microns (sand is typically 20 microns), it loads 2 to 3 more times the particulate load of sand, and it
reduces the number of backwashes (see usage document on water filtration). Second would be the use of a biological
filter in which bacteria mineralize the organic nitrogen compounds. The process can be aerobic or “nitrification,” or
anaerobic or “denitrification.” Nitrification is the most popular, and it involves the oxidation of ammonia to nitrite and then
to nitrates by autotrophic bacteria (Nitrosomonas and Nitrobacter). The huge surface area of BRZ™ makes it an
excellent host for bacteria. Third, the ammonia can be chemically filtered by clinoptilolite. A zeolite filter system can be
used to mechanically remove food wastes and fecal material. It also removes the ammonia and becomes a host for
aerobic bacteria that eat the ammonia. As such, it becomes all three filter systems in one if properly applied.
NOTES ON THE USE OF CLINOPTILOLITE IN AQUACULTURE
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The ammonium promotes the growth of algae in the pond or tank and the algae will grow on the BRZ™ where
they utilize some of the ammonium. However, the algae on the BRZ™ will inhibit the absorption of the ammonium
into the BRZ™. The algae must be washed off to accelerate the adsorption of the ammonium.
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Excretion of ammonia by fish increases with the activity of the fish, an increase in the temperature, and an
increase in the feed ration. A rise of 13 degrees F can cause a 10-fold increase in the rate of excretion.
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The percentage of ammonia gas in solution increases with an increase in temperature.
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A reduction of dissolved oxygen (DO) increases the acute and chronic toxicity of ammonia.
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The toxicity of ammonia decreases with an increase of salinity up to 30% sea water (9 % salt).
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Adsorption efficiency of BRZ™ is unaffected by water temperature.
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Adsorption efficiency of BRZ™ decreases in water of low pH.
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Adsorption efficiency of BRZ™ decreases as water hardness increases. Other cations such as Ca, Na, Mg, and K
compete more effectively than ammonium for the exchange position. Optimum efficiency occurs when the
hardness is less than 44 mg/l.
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The effective depth of penetration for ammonium into BRZ™ is about ½ inch. As a result, smaller granules are
more effective than larger granules. Too many fines increase the turbidity, however.
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BRZ™ will reduce ammonia in proportion to the amount of BRZ™ used.
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BRZ™ is typically not used in seawater due to the high hardness and the amount of sodium. In seawater, BRZ™
has approximately only 5% of the capacity that it has in fresh water. Much more massive amounts of BRZ™ must
be used in seawater that is typically not economic.
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Ammonium loaded BRZ™ can be regenerated by using a saline back wash solution followed by a rinse cycle.
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Alternatively, aerobic bacteria, algae, or plants can be used to regenerate the BRZ™.
RECOMMENDED USES OF ZEOLITE FOR AQUACULTURE
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DECORATIVE ROCKS. -- Decorative rocks can be placed in ponds, aquariums, streams, fountains, and other
tanks. Although these can be large in size, the effective penetration is only about ½ an inch. Consequently,
BRZ™ larger than 1 inch diameter looses its effectiveness as a chemical or chemical/biological filter.
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MECHANICAL FILTRATION. -- BRZ™ makes an excellent mechanical filter media for unused food and fecal
material or aquaculture ponds.
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CHEMICAL FILTRATION. -- BRZ™ is an excellent chemical filter for ammonium as well as for certain heavy
metals by virtue of its cation exchange capacity.
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MEDIA FOR BIOLOGICAL FILTRATION.—the tremendous surface area and irregular surface of BRZ™ makes it
a perfect media for biological colonies of aerobic bacteria. In effect it becomes a chemical/biological filter.
BRZ™ CONTROL OF AMMONIUM IN TROPICAL FISH BOWL - OCTOBER 2003
OBJECTIVE: This test is designed to test the effectiveness of ammonium reduction in a aquarium with one Beta fish
using two different zeolites: BRZ™ zeolite, and Brand X.
PROCEDURE:
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4 small fish bowls were prepared and filled with water to study 3 groups of Beta fish.
1 fish was placed in each of four bowls designated the “control group” with no zeolite.
1 fish was placed in each of four bowls containing a 0.3 oz rock of zeolite screened at 1” x ¾” and designated
“Brand X” zeolite.
1 fish was placed in each of four bowls containing a 0.3 oz. rock of Bear River zeolite screened at 1” x ¾” and
designated “BRZ™.”
The water was static. There were no pumps or aerators.
All fish were fed two times per day 0.03 grams of food.
RESULTS: The results are in ppm ammonium.
Bowl
Day 1
Day 2
Day 3
Day 4
Day 5
Control Group
1
2
3
4
0
0
0
0
0
0
0.25
0.25
0.5
0.5
1.0
1.0
1.0
1.25
1.0
1.0
2.0
2.0
2.0
2.0
1.0
0.5
1.0
1.0
2.0
1.25
1.5
1.25
1.5
1.5
1.0
1.5
1.25
1.75
2.0
1.5
1.5
2.0
2.0
2.0
BRZ™
1
2
3
4
0
0
0
0
0.25
0
0.25
0
Brand X
1
2
3
4
0
0
0
0
0
0
0
0.25
1.0
1.5
1.5
1.0
Averages
Control
BRZ™
Brand X
0
0
0
0.1875
0.125
0.125
0.75
0.875
1.25
1.3125
1.5
1.625
2.375
1.375
1.875
COMMENTS:
 Agitation of the water would have brought more ammonium in contact with the zeolite,
and it would have been more effective.
 Smaller particles of the zeolite would have been more effective. One quarter inch is penetrated
fairly fast, but greater depths of penetration in the zeolite are slower.
 The annual market for Betta fish and related supplies is $150,000,000 in the United States.
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