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Showing posts with label water quality. Show all posts
Showing posts with label water quality. Show all posts

WATER QAULITY IN FISH FARM

Fish need water quality to
survive, grow, and reproduce.
Quality water has no
pollutants, is high in dissolved
oxygen, and does not have
excessive organic matter. Fencing a pond is needed to
prevent livestock from
trampling pond banks, which
causes pond shallowing, muddy
water, and loss of fish. Fences
should be 50 to 100 feet from the pond bank and completely
enclose the pond. A vegetated
border is needed at least 50 feet
wide that will reduce soil
erosion and the amount of
fertilizer and pesticides entering the pond. Trees along
the shore line are desirable for
shading and nutrient uptake.
Water clarity should be at least
18 inches through out the year
and is necessary for plankton production. For help and consultancy call 08032861326.

WATER IN FISH FARMING

One of the first per-requisite (important thing) in fish farming is water, fish lives and sustains it's self in water.
Sources of water for fish farming include: ocean, river, streams, dams boreholes and wells. In fish farming two things are considered before deciding the water to use for the culture.
(1) Type of fish to be cultured
(2) Availability of quality water
If the farmer have in mind to culture fresh water fish, the farmer have to locate fresh water and if the fresh water is not available it becomes a big problem to culture the fish. Therefore not all can be cultured in fresh water some does well in salt water and cannot survive in fresh water. Providing a suitable environment for the fish to be cultured is very important.
AVAILABILITY OF QUALITY WATER
Water supplies for catfish ponds are usually of good quality, however, once the water used for culture, it's quality deteriorates.this deterioration of environmental conditions is ultimately traceable to the use of feed. Despite the use of high quality feeds and carefully feeding practices, relatively little of the nutrient value of feed is converted to catfish flesh. The remaining nutrients derived from fish wastes stimulates excessive phytoplankton growth, high rates of phytoplankton metabolism cause pronounced diurnal fluctuations in dissolved oxygen concentrations, dissolved carbondioxide concentrations and ph, such fluctuations cause stress in fish resulting in reduced fish growth rates, poor feed conversation and reduced resistance to disease, in extreme instances, such as depletion of dissolved oxygen, fish may be unable to adapt and will die.

CONTROL AND MAINTANACE OF QUALITY WATER IN FISH FARMING.
Frequent change of water in fish farming increases the oxygen content of the water, therefore a flow through system of culture will help in replacing used oxegen and boost oxygen content of the water for fish culture. Natural waters soure such as rivers, streams can be diverted and be used in flow through system in an eathen and even concrete ponds settings. Thereby reducing cost for water maintenance and management. Lastly, water for fish farming must be a quality one for optimum fish production.
FOR CONSULTANCY FOR YOUR FISH POND CONSTRUCTION, FISH BREEDING, FINGERLINGS, FEASIBILITY STUDY, FISH FEED PRODUCTION AND ANY AGRO SERVICES: CALL US ON 08032861326. FOR QUALITY SERVICES.

CATFISH FARMING IN NIGERIA

Call (08032861326) Kingsway Agro Services:we are too good to deliver every services about fish production, Hybrid fingerlings
production and supply, setting up aquaculture environment decoration in beautifying ur homes, and aquarium designs, pond construction,fish feed
production, supply of machines used in fingerlings production and feed production, consultancy in all fishery matters. Drugs used in
treating ponds,piggery house construction and fish disease treatment etc. Call us on 08032861326 for excellent
services at low price.

HOW TO MORNITOR PH IN FISH POND WATER

The pH is the measure of the
hydrogen ion concentration in soil
or water. An ion is an electrically
charged atom. Water exists as a
balance between hydrogen ions (H
+) and hydroxyl ions (OH -) and has the formula H20. The pH scale ranges from 0-14 with 7 neutral.
When there are more hydrogen
ions (H+) present the pH will be
lower than 7 and the water acidic.
The water is basic (alkaline) when
there are more hydroxyl ions (OH-). Silver perch grow best in a pH
range of 6.5 to 9. Fig. 1 shows the
relationships of pH of pond waters
to their suitability for fish. Carbon dioxide has an acidic
reaction in water. The pH in ponds
rises during the day because
phytoplankton and other aquatic
plants remove carbon dioxide from
the water during the process of photosynthesis. The pH decreases
at night because of respiration and
production of carbon dioxide by all
organisms. Signs of Sub-optimal pH: increase of mucus on gill surfaces damage to eye lens and cornea abnormal swimming behaviour fin fray death poor phytoplankton and
zooplankton growth. Effects of Sub-Optimal pH: stress increased susceptibility to disease low production levels poor growth. Causes of Sub-Optimal pH: acidic water and soils acid sulphate soils poorly buffered water, i.e. low
alkalinity (<20 data-blogger-escaped-alkalinity="" data-blogger-escaped-and="" data-blogger-escaped-br="" data-blogger-escaped-having="" data-blogger-escaped-high="" data-blogger-escaped-l="" data-blogger-escaped-mg="" data-blogger-escaped-waters=""> low hardness acid rain. Sub-optimal pH - What can I do? To decrease high pH: flush the pond reduce feeding rates to lower
nutrient input and plant growth ponds built in acid sulphate soils
should be refilled immediately to prevent
drying built no deeper than necessary grassed on the walls limed on the walls add gypsum (CaSO4) to increase
the calcium concentration add alum (AlSO4) for immediate
reduction of pH to avert imminent
fish mortality. To increase pH: lime the ponds increase phytoplankton abundance
by fertilization.
08032861326.

HOW TO MAINTAIN WATER TEMPERATURE IN POND

Fish are ectotherms because heat is
obtained from outside the animal
unlike endotherms (e.g. mammals)
that generate their own body heat.
Usually, the body temperature of
ectotherms is close to that of their surroundings; they are often
described as poikilothermic
(having variable temperature). Temperature affects all chemical
and biological processes. The
metabolic rate of fish doubles for
every rise of 10°C. Therefore,
temperature has a direct effect on
important factors such as growth, oxygen demand, food
requirements and food conversion
efficiency. The higher the
temperature, the greater the
requirement for oxygen and food
and the faster the growth rate. Temperature partly determines the
concentration of oxygen in water.
The solubility of oxygen decreases
with increasing temperature, and
so concentrations are usually lower
in summer. Silver perch have a temperature
tolerance range of 2 to 38°C with
optimum growth occurring
between 23 and 28°C. During
winter when water temperatures
are lower, silver perch will require less food and have a slower growth
rate. At temperatures below 10°C
the fish may enter a state of
torpor, with greatly reduced
appetite and activity. As the water
temperature increases in spring and summer, the fish will require a
larger quantity of food due to the
increase in their metabolic rate. Temperature also has a crucial role
in stimulating silver perch gonadal
maturation and spawning activity.
Silver perch can be induced to
breed in hatcheries when water
temperatures rise to about 21°C

HOW TO MAINTAIN DISSOLVED OXYGEN IN POND WATER

Dissolved oxygen (DO) is the most
critical and limiting factor in
intensive aquaculture. Oxygen
enters water through
photosynthesis by aquatic plants,
principally phytoplankton, and by diffusion at the air-water interface.
Diffusion occurs when waters are
below saturation, and the greater
the deficit between the oxygen
concentration in the water and the
saturation concentration, the greater the rate of diffusion. In
ponds, diffusion is promoted by
wind and wave action and by
artificial aeration. Oxygen is lost
from water through respiration by
fish, plankton and other organisms, and by aerobic decay of organic
matter. There are distinct diurnal
fluctuations of oxygen, with
concentrations lowest just after
dawn, increasing during daylight
hours. This is because of the photosynthetic production of
oxygen, (there is also usually more
wind during the day) to a
maximum in late afternoon, before
decreasing again during the night. Silver perch can tolerate low levels
(2 mg/l) for short periods (a few
hours) but exposure to sub lethal
levels (<3 data-blogger-escaped-br="" data-blogger-escaped-extended="" data-blogger-escaped-for="" data-blogger-escaped-l="" data-blogger-escaped-mg=""> periods will reduce growth and
stress fish. The Signs Fish Exhibit to Low DO loss of appetite lethargy gasping near the surface fish facing into current of inlet or
aerator death of larger fish, followed by
smaller fish Effects of Low DO stress increased susceptibility to
disease poor feed conversion efficiency poor growth death of fish and other pond
organisms. Causes of Low DO large blooms of phytoplankton,
zooplankton and other pond
organisms respiring during the
night high stocking densities of fish and
high feeding rates "crash" of phytoplankton/
zooplankton booms excessive turbidity, i.e. no or
limited oxygen production through
photosynthesis series of cloudy, windless days combinations of the above
conditions. Low DO – What can I do? monitor DO routinely and chart
diurnal fluctuations to predict
periods of low DO maintain aeration day and night provide additional aeration place another aerator in the pond spray water across the pond
surface

WATER HARDNESS AND AKALANITY CONTROL IN FISH FARM

Alkalinity refers to the total
amount of bases in water
expressed in mg/l of equivalent
calcium carbonate. A base is a
substance that releases hydroxyl ions (OH-) when dissolved in water. In most waters these bases are
principally bicarbonate (HCO) ions and carbonate ions (CO32-). These ions are the buffers in water; that
is they buffer the water against
sudden changes in pH. They can do
this by absorbing hydrogen ions
when the water is acid and
releasing them when the water becomes basic. Waters of low
alkalinity (<20 data-blogger-escaped-are="" data-blogger-escaped-br="" data-blogger-escaped-l="" data-blogger-escaped-mg="" data-blogger-escaped-poorly=""> buffered, and the removal of
carbon dioxide (CO2) during photosynthesis results in rapidly
rising pH. Waters, with greater
than 20 mg/l alkalinity have
greater buffering capacity and
prevent large fluctuations in pH
during photosynthesis (Fig. 1). Fig. 1. The effect of buffering on pH at low and high alkalinities Hardness is the concentration of
metal ions (primarily calcium and
magnesium) expressed in mg/l of
equivalent calcium carbonate.
Alkalinity and hardness values are
normally similar to magnitude because calcium, magnesium,
bicarbonate, and carbonate ions in
water are derived in equivalent
quantities from the solution of
limestone in geological deposits.
However, in some waters alkalinity may exceed its hardness and vice
versa. If alkalinity is high and
hardness low, pH may rise to very
high levels (greater than 10.5)
during periods of rapid
photosynthesis. Waters are often categorised
according to degrees of hardness
as follows: 0-75 mg/l - soft 75-150 mg/l - moderately hard 150-300 mg/l - hard over 300 mg/l - very hard Alkalinity and hardness are not
greatly affected by biological
activity or aquacultural operations,
and the initial concentrations in
ponds are determined by their
level in the water supply; any changes are largely the result of
rainfall and evaporation. Desirable
levels for fish culture generally fall
within the range of 20-300 mg/l. If
total alkalinity and total hardness
are too low, they may be raised by liming. However, there is no
practical way of decreasing
alkalinity and hardness when they
are above desirable levels. As a general rule, the most
productive waters for fish culture
have a hardness and alkalinity of
approximately the same
magnitude. For example, a water
with an alkalinity of 100 mg/l and hardness of 10 mg/l is not as good
for fish culture as water in which
the alkalinity is 100 mg/l and the
hardness is 100 mg/l. Greater
production does not result directly
from higher levels of hardness and alkalinity per se, but from the
higher concentrations of
phosphorus and other essential
elements that increase along with
hardness and alkalinity.

WATER QUALITY CONTROL IN FISH FARMING

Water quality can be more
unstable in recirculating systems
than in large ponds or flow-
through systems. Water quality
fluctuations, such as temporary
increases in ammonia or nitrite, can, by themselves, result in
disease or significant losses. These
environmental fluctuations often
lead to suppressed immune
systems and greater susceptibility
to pathogens (i.e., disease-causing organisms, such as bacteria,
parasites, fungi, and viruses) and
disease outbreaks. Recirculating systems favor the
growth of many disease-causing
organisms and spread of disease.
There are a number of reasons for
this tendency, including higher
densities of fish when compared to other culture systems; build up of
biofilms and sediment and
subsequently pathogens in tanks,
sumps, or filtration components
(especially mechanical and
biological filters); and slower turn over of water. Over time, pathogens can become
concentrated (i.e., present in high
numbers). Most pathogens are
considered opportunistic, causing
disease only in fish with
suppressed immune systems. However, if pathogens become
sufficiently numerous they can also
cause disease in healthy fish. In
addition, the continuous flow of
water throughout a system can
spread pathogens rapidly, especially in a system lacking
adequate disinfection protocols or
components, such as ultraviolet
sterilization or ozone (see System
Disinfection below). Bacteria, parasites, fungi and
viruses can all become
concentrated in recirculating
systems. Bacteria that seem to
increase in number in recirculating
systems include Aeromonas spp., Vibrio spp., Mycobacterium spp.,
Streptococcus spp., and
Flavobacterium columnare
(Columnaris disease) (see UF/IFAS
Fact Sheets FA-14 Aeromonas Infections, FA-31 Vibrio Infections of Fish and VM-96 Mycobacteriosis in Fish; UF/IFAS Circular 57 Streptococcal Infections of Fish; and SRAC Publication No. 479b Columnaris Disease, respectively).
Parasites that tend to thrive and
spread relatively easily in
recirculating systems include
Trichodina,
Ichthyophthirius,Cryptocaryon, Amyloodinium, Costia and
monogeneans (see UF/IFAS
Circulars 716 Introduction to Freshwater Fish Parasites and 920 Ichthyophthirius multifiliis (White
Spot) Infections in Fish; UF/IFAS Fact sheet Amyloodinium Infections in Fish VM-90;and UF/ IFAS Fact Sheet FA-28 Monogenean Parasites of Fish, respectively). Closed systems can also foster the
spread of fungi and viruses (see
UF/IFAS Fact Sheets VM-97 Fungal Diseases of Fish and FA-29 Introduction to Viral Diseases of
Fish, respectively). Adequate control of pathogens in a
system, and consequently
reduction of disease in these
systems, requires an
understanding of where pathogens
may be found, how they can be transmitted to fish, and how their
numbers may be reduced. In
addition, understanding the proper
use of chemicals to reduce or
eliminate pathogens is an essential
part of good management. Biosecurity Biosecurity has been mentioned in
Part 1 of this series (recommended
reading), but its importance
warrants further discussion. The
purpose of a biosecurity program
is to prevent entry of specific pathogens (disease-causing
organisms, i.e., bacteria, viruses,
parasites, or fungi) that may cause
significant disease and are not
present either in the environment
or on the fish in a given facility or system. In some cases, this is
achieved by extensive testing of
fish prior to receiving them from a
supplier, or during isolation and
quarantine, prior to placing them
in their intended system. For some pathogens, this may not
be an absolute elimination of risk
of entry, but primarily an overall
reduction of the number that do
enter the facility, so that fish
already on the property do not receive an overwhelming load. Biosecurity measures are
important not only when bringing
new fish into a facility; these
measures are also important for
reducing overall numbers of
potential pathogens in a given system, and to avoid transferring
pathogens from one system to
another. For this reason, it is
important to understand where
pathogens may be found
(reservoirs), and why quarantine, disinfection, and sanitation are
important to a good biosecurity
program. Pathogen Reservoirs There are many areas within an
aquaculture facility and
recirculating system that can act as
reservoirs for pathogens. The most
important reservoirs are the fish
themselves. Fish can act as asymptomatic carriers of disease.
In other words, they may be
immune to a specific pathogen but
still be able to shed the organism
into the water or transfer it to
other fish by contact. Sick and dead fish are often major reservoirs of
disease-causing organisms. For this
reason, sick, moribund (dying), and
dead fish should be removed as
soon as possible from a system and
disposed of according to county, state, or federal regulations. In
most instances, disposal can be as
simple as placing the dead fish in a
plastic bag and putting it in a trash
receptacle. Water can also act as a
reservoir. Water can spread pathogens to anything it touches. The ground (e.g., concrete slab)
can contain pockets of water that
contains pathogens. Equipment,
including nets, siphon hoses and
buckets, can also contain pockets of
disease-causing organisms. For this reason, disinfection of floors, and
use of footbaths (either small
containers or mats containing
disinfectants) placed at entrances
and exits to system rooms is
recommended, as is disinfection of all equipment when used with fish
in different tanks or vats or
systems. Nets should be kept off
the floor and placed in an
appropriate clean location to avoid
contamination. Quaternary ammonium
compounds are commonly used to
disinfect equipment but they must
be rinsed adequately prior to reuse
because these compounds are toxic
to fish (see UF/IFAS Fact Sheet VM-87, Sanitation Practices for Aquaculture Facilities). Chlorine can be used but will destroy nets and
must be neutralized or rinsed off
adequately to avoid killing fish.
Equipment disinfected with iodine-
containing compounds must also
be rinsed off prior to use because they can be toxic. Virkon Aquatic ®
is used by numerous aquaculture
facilities and has been shown to be
safe and effective against a wide
variety of aquatic pathogens when
used as directed. Contact a fish health or aquaculture specialist for
recommendations on disinfectants
for equipment, floors, and
footbaths. System hardware, including sumps
and filters, sediment, and tank
walls, are common sites for
pathogens. Sumps and tanks often
contain a fine film (biofilm) or
layer of sediment that may harbor pathogenic organisms. Sediment
on the bottom of sumps and tanks
should be vacuumed routinely.
Uneaten food lying on the bottom
of tanks can also provide areas for
pathogens to flourish. Filter beds, because of their
particulate nature, concentrate
microorganisms. Mechanical filters
should be backwashed, as
frequently as possible, to reduce
the loads of the undesirable (non- biofilter) bacteria, as well as other
potential pathogens. Pathogen Transmission Pathogens can be transmitted
several ways within a recirculating
system: in the water fish to fish by vectors and fomites in the food Introduction of water used to ship
fish can be a key source of
pathogens. Shipping water often
contains high numbers of bacteria
and may also contain parasites or
other pathogens. These organisms are easily transferred from tank to
tank in the recirculating water, or
by aerosolization (in mist or spray)
of water from one tank or system
to another. Within a single tank or vat,
pathogens can be spread directly
from fish to fish. Higher stocking
densities and increased fish-to-fish
contact (as seen in aggressive
species) can increase the rate of spread of pathogens. Vectors are organisms that can
transmit disease-causing
organisms from one animal to
another. For example, the
crustacean parasite Argulus (“fish
louse”) causes damage by itself, but it is also believed to transmit
bacteria and viruses between fish.
Leeches are another vector that
can transmit blood-borne parasites
and bacteria between fish.
Additionally, people can act as vectors by transmitting water and
pathogens from one tank to
another via their hands or arms. Fomites are inanimate objects that
can transmit diseases. Examples of
fomites in aquaculture systems
include equipment, such as nets
and siphon hoses, that are not
properly disinfected before being used in other tanks or vats. Food can also be a source of
disease. Frozen and live foods can
transmit bacteria, parasites,
viruses, and fungi. In addition,
feeds that have been improperly
stored can contain pathogenic bacteria or mycotoxins, dangerous
chemicals produced by the growth
of certain types of fungi in the feed
(see UF/IFAS Fact Sheet FA-95,
Molds in Fish Feeds and
Aflatoxicosis). Improperly stored feeds also have reduced nutritional
value, due to degradation of
micronutrients (e.g., reduction of
vitamin C levels) and
macronutrients (e.g., rancidity of
fats). System Disinfection or
Sterilization As described previously, water
may spread pathogens and also be
a potential reservoir for them.
Water from a tank containing sick
fish often carries numerous
disease-causing microorganisms. When this same water enters
another tank of fish, those fish are
then exposed to the
microorganisms and they will have
an increased risk of developing
disease. Disinfection helps to greatly reduce the spread of some
pathogens. Two techniques
commonly used to disinfect water
in aquaculture systems are
ultraviolet sterilization and
ozonation. Ultraviolet Sterilization Ultraviolet (UV) sterilizers typically
consist of UV-producing lamps
encased in a glass or quartz sleeve.
Water is passed over the lamps.
The lamps emit ultraviolet light (a
wavelength of approximately 254 nm is considered optimal) that
penetrates cells and damages
genetic material (DNA and RNA)
and proteins. For each type of microorganism, a
specific “zap dose,” measured in
microwatt seconds per square
centimeter, is required to
selectively sterilize the system (i.e.,
kill the unwanted organism). The zap dose is determined by the
intensity or wattage of the lamp,
contact time or flow rate of the
water, water clarity, and size and
biological characteristics of the
target organism. In general, larger organisms require a larger zap
dose (see Table 1 and Figure 1);
however, the specific structure of
certain viruses (which are
generally much smaller than
bacteria) makes some of them more difficult to “kill” than
other larger organisms. In general,
the zap dose required is lowest for
gram-negative bacteria, and it
increases progressively for gram-
positive bacteria, viruses, spore- forming bacteria, and protozoans. Table 1. Recommended zap doses for different organisms

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