The Use of Agricultural Limestone
and Gypsum in Ponds
Forrest
Wynne, Aquaculture Extension Specialist,
Cooperative
Extension Program,
Fax: (270)247-5193
Ponds
built in areas which have acid soils and soft water may not always perform well
for fish production. Such ponds may benefit from liming if the water has a
total alkalinity of less than 20 mg/l (20 ppm). If alkalinity is more than 20 mg/l, liming
may not be beneficial. Alkalinity
measures the buffering capacity of the water and is usually a good indicator of
productivity. Carbonates, bicarbonates,
hydroxides, phosphates, and organic substances are the main components of water
alkalinity. Water hardness is caused by
calcium, magnesium, iron, and aluminum salts, most often in the form of
carbonates, sulfates, or chlorides. Ponds which have water hardness
concentrations of less than 20 mg/l may also benefit from liming. Alkalinity
and hardness can be measured with commercially available water test kits, or by
State Fisheries or Extension Service Aquaculture Specialists. Generally, total alkalinities of 100‑120
mg/l, water hardness concentrations of 100‑250 mg/l, and pH values
between 6.5 ‑ 9.0, are considered desirable for freshwater fish
production.
Liming
a pond properly will raise the pH of bottom muds and
water, and make phosphorus more available for plant production. Low levels of phosphorus may limit the growth
of a pond's microscopic plants which are the foundation of the aquatic food
chain and pond productivity. Fish
populations should benefit from liming.
Liming can enhance nutrient cycling; the breakdown of organic matter and
may also help clear muddy pond water.
Liming
may be less effective if the pond has a large watershed and water is exchanged
more than once every 3 or 4 weeks.
Surface, coal mining spoils contain pyrites which can produce sulfuric
acid when exposed and weathered. Ponds
should not be constructed on these watersheds unless the soil has been tested
or the acidic runoff water can be diverted away from the pond. Ponds should be limed during the late fall or
winter, especially if a pond fertilization program is begun the following
spring. If low alkalinity ponds are
fertilized before being limed, much of the phosphorus may be lost to the bottom
muds.
Therefore, the effort and expense of fertilization could be wasted. However, lime should not be added to a pond
which has been recently fertilized as it tends to remove phosphorus from the
water.
Ponds
can be limed with liquid lime, basic slag, or agricultural limestone. The acid neutralizing value represents the
ability of a liming material to neutralize acid when compared with pure calcium
carbonate (which represents 100%).
Liquid lime works rapidly but contains 50% water which doubles the
amount of material to apply. Basic slag
has a neutralizing value of 50‑79%.
The values for agricultural limestone range from 95 to 108%. Hydrated or slaked lime has a value of 136%
and calcium oxide has a value of 179% and should not be used to lime fish
ponds. Calcium oxide or hydrated (slaked) lime will not increase carbonate
alkalinity and could drastically raise water pH, which may kill fish. Agricultural limestone is usually the best
choice. It is inexpensive ($9.00‑$22.00/ton)
and safe to use in fish ponds.
Agricultural limestone should be ground fine enough to pass through a 10
mesh sieve. Small particles will dissolve more readily in water. A sieve
analysis may be required to determine particle size and assign the lime an
efficiency rating. The amount of lime
required per surface acre of pond is determined by analyzing pond mud
samples. Samples should be taken
randomly from deep and shallow areas, making an "S"‑shaped
pattern over the entire length and width of the pond. Mud samples can be collected from existing
ponds using a boat and an 8‑oz. can attached to a long pole or by taking
small plugs of mud with a length of PVC pipe.
In ponds greater than 5 surface acres, three to six similar sized mud
samples should be taken per acre.
Smaller ponds require 10‑15 mud samples per surface acre. The samples should be mixed together and
allowed to air dry on a flat surface.
Pond mud samples should then be pulverized and placed in a soil sample
box marked "fish pond". These
samples can then be submitted to a private soils testing lab or to your county
extension office to be sent out for processing (for a small fee).
Lime
application rates will usually be made on the basis of 1,000‑10,000 lbs./ surface acre. The
equation used is similar to the following:
Application rate =
Liming Rate
‑‑‑‑‑‑‑‑‑‑‑‑‑‑‑‑‑‑‑‑‑‑
Neutralizing x Efficiency
Value Rating
‑‑‑‑‑‑‑‑‑‑------ ‑‑‑‑‑‑‑‑‑‑----
100 100
Lime should be distributed as evenly as
possible over the entire surface of a full or dry pond. The best time to lime a pond is before
filing; lime can be applied with a spreader and mixed into the pond bottom with
a disc‑harrow. Small, full ponds
can be limed by spreading bagged lime from a boat or by broadcasting it from
the shore. Large ponds may require
greater amounts of lime which is more economical when purchased in bulk
quantities. Lime can be loaded onto a ½
inch plywood platform placed over the bow of a large boat or between two small
boats. The material can be shoveled or
washed off the platform using a water pump, while moving slowly across the
pond. A boat 18 feet long by 6 feet wide can carry 1,500 lbs. of agricultural
limestone.
Ponds
may need to be limed every 3‑5 years.
A good general rule for liming ponds is to apply lime at rates similar
to those used for alfalfa field preparation.
To maintain a pond's pH and alkalinity at desirable levels, the lime
should be applied annually by adding one‑fourth of the initial
application. Pond alkalinity and pH
should be checked each year to evaluate the effectiveness of supplemental
liming. Total alkalinity should not be
less than 20 mg/l with pH values between 6.5‑9.0.
Considering
the relatively low cost involved in the maintenance of a pond's lime
requirement, ponds should be limed before implementing a pond fertilization
program. If liming does not improve fish
production to a satisfactory level after one year, a fertilization program
should then be tried.
Agricultural
Gypsum
Adding
agricultural gypsum to ponds to percipitate available
phosphates which can reduce dense algae blooms, increase water hardness and may
reduce turbidity. The pH of pond waters (generally with a pH of 9.5 or
greater), which have high alkalinity and comparatively low calcium hardness,
may be reduced by the addition of gypsum (calcium sulfate) or land
plaster. High water alkalinity and low
calcium hardness often occur where bicarbonate and carbonate ions are
associated with the more soluble sodium, potassium and magnesium elements, as
opposed to calcium. When plants remove carbon dioxide from the water during
photosynthesis, carbonate ion concentrations increase. In the presence of the less soluble calcium,
the hydrolysis of carbonate to hydroxyl ions elevates the afternoon water pH to
approximately 9.5 or 10.0. At this
point, calcium carbonate begins to percipitate. Since
the hydrolysis of carbonate and the formation of hydroxides which elevate pH
have been limited by carbonate precipitation, pH will not increase further.
However, where alkalinity is high and calcium concentrations are low, afternoon
pH may rise above 10 and become toxic to some aquatic organisms.
According
to
Application
rate of agricultural gypsum in mg/L = total alkalinity mg/L - total hardness
mg/L X 4
The
following example will calculate the pounds of agricultural gypsum needed per
acre foot of water which has a total alkalinity of 80 mg/L and a total hardness
of 15 mg/L.
Total Alkalinity 80 mg/L -
Total Hardness 15 mg/L x 4 = 260 mg/L of gypsum to add per liter.
260 mg/L of gypsum to add x 2.718 lbs per acre foot
= 707 lbs of gypsum to add per acre foot
of water (assuming gypsum is 100% active).
Factors:
1 acre foot contains 325,850 gallons or 1,233,500 L
of water.
To increase gypsum content 1 mg/L per acre foot of
water will require 2.718 lbs of gypsum (100% active).