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Sizes: ½” x 4, 4 X 14, 14 x 40, 4 X 8
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Surface
Area:
24.9 square meters per gram
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Weight: 55 pounds per cubic foot
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CEC:
Cation Exchange capacity 160 to 180 meq/100
grams
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.
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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.
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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™.
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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
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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.
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1 fish was placed in each
of four bowls designated the “control
group” with no zeolite.
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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.
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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™.”
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The water was static.
There were no pumps or aerators.
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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
0
0
0.5
1.0 2.0
2
0
0
0.5 1.25
2.0
3
0
0.25
1.0
1.0 2.0
4
0
0.25
1.0
1.0 2.0
BRZ™
1
0
0.25
1.0
2.0 1.5
2
0
0
0.5 1.25
1.5
3
0
0.25
1.0
1.5 1.0
4
0
0
1.0
1.25 1.5
Brand
X
1
0
0
1.0 1.25
1.5
2
0
0
1.5 1.75
2.0
3
0
0
1.5
2.0 2.0
4
0
0.25
1.0 1.5
2.0
Averages
Control
0 0.1875
0.75 1.3125
2.375
BRZ™ 0
0.125 0.875
1.5
1.375
Brand X
0 0.125
1.25 1.625
1.875
COMMENTS:
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Agitation of the water would have
brought more ammonium in contact with
the zeolite,
and it would have been more
effective.
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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.
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The annual market for Betta fish and
related supplies is $150,000,000 in the
United States.
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