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Name - Ipsita Sahoo
Reg no- 200705180160
Guided by- Dr. Sitaram Swain
School of Applied Science, CUTM, BBSR
M Sc. 1st year Zoology
Subject- Advance aquaculture
Topic- “Soil And Water Quality In
Relation To Fish Production”
Session- 2020-22
Introduction
Bottom soil management
Water quality management
Sustainable pond productivity
Conclusion
Reference
CONTENTS
Successful aquaculture depends on providing
animal with a satisfactory environment in which they
will grow.
Good initial condition for aquaculture can be
assured by a selecting a site with suitable soil and a
high quality water supply.
Good bottom soil and water quality are vital
ingredient for any successful aquaculture practices.
There is increasing evidence that the condition of
pond bottoms and the exchange of substances
between soil and water strongly influence water
quality (Boyd, 1995).
Introduction
Bottom soil is considered as the chemical laboratory
of the pond, so that physicochemical properties like
Texture, Soil acidity, Bottom soil oxidation,
Drying pond bottom should be balanced.
Bottom Soil Management
Physicochemical
properties for
Bottom Soil
Management
Texture
Soil
acidity
soil
oxidation
Drying
pond
bottom
The nature and the properties of the parent
material forming the soil determine the soil texture.
An ideal pond soil should not be too sandy to
allow leaching of the nutrients or should not be too
clayey to keep all the nutrients absorbed on to it.
For sandy soil, heavy dose of raw or composed
farmyard manure varies from 10,000 to 15,000
kg/ha/year is required.
Texture
The soil may be acidic, alkaline or neutral but the
ideal range for soil pH is 6-8.
Acid ponds do not respond well to fertilization and
liming is the only way to improve water.
Soil acidity
 When the redox potential is low at the soil
surface, hydrogen sulphide and other toxic microbial
metabolites diffuse into the pond water.
 Sodium nitrate (NaNO3) can serve as a source of
oxygen for microbes in poorly oxygenated
environment in which the redox-potential will not
drop low enough for the formation of hydrogen
sulphide and other toxic metabolites.
Bottom soil oxidation
 Evaporation of water from soil pores and
cracking of soil during drying enhances aeration and
favor microbial decomposition of soil organic
matter.
 Excessive drying makes soil too dry for microbial
activity, so a period of 2-3 weeks is adequate.
 Tilling with a disk harrow also improves aeration
but compaction is required before refilling to reduce
erosion.
Drying pond bottom
 Water is a most important element in aquaculture.
Poor water quality
Affect fish & shellfish health through
impairment of development and growth .
Water Quality Management
Physicochemical
Properties For
Water Quality
Management
pH
Temperature
Total
hardness
Total
Alkalinity
Turbidity
Hydrogen
sulphide
Dissolved
oxygen
Carbon
dioxide
Ammonia
 Temperature sets the pace for metabolism and
biochemical reaction rates.
 The optimum temperature range for cold water
and warm water fishes are 4°C-18°C and 24°C-30°C
respectively.
 Temperature can be adjusted to optimum level in
controlled condition like hatcheries but difficult to
adjust in large water bodies.
 Operation of aerator helps in breaking thermal
stratification while planting of trees gives shades.
Temperature
 pH is a measure of hydrogen ion concentration in
water and indicate how much water is acidic or
basic.
 Water pH affects fish metabolism, physiological
process, toxicity of ammonia, hydrogen sulphides
and solubility of nutrient thereby well-being and
fertility.
 pH at the range of 6-9 is best for fish growth and
can be increase by application of lime.
 Agriculture gypsum may be applied to correct
alkaline pH.
pH
 The optimum dissolved oxygen (DO) content of
pond waters is in the range of 5 ppm saturation
level.
 Aeration is a proven technique for improving DO
availability.
 Any sort of agitation improves the DO content
and among which paddle-wheel, aerators aspirators
are most common.
Dissolved oxygen
 Several factors like suspended soil particle,
planktonic organisms and organic matter contributes
to turbidity.
 Measured using Secchi disc the optimum
visibility range from 40-60 cm.
 It can be controlled by application of organic
manure at 500-1000 kg/ha, gypsum at 250-500
kg/ha or alum 25-50 kg/ha.
Turbidity
 Fish are very sensitive to unionized ammonia
(NH3) and optimum range is 0.02-0.05 ppm in the
pond water.
 The same is reduced in the case of high DO and
high CO2.
 Aeration, healthy phytoplankton population
removes ammonia from water. Addition of salt 1200-
1800 kg/ha reduces toxicity. Formalin are also use in
certain cases.
 Biological filter may be use to treat water for
converting ammonia to nitrate and then to harmless
nitrate through nitrification process.
Ammonia
 Fresh water fish pond should be free from
hydrogen sulphide because at concentration of 0.01
ppm fish lose their equilibrium.
 Frequent exchange and increase of pH through
liming can reduces its toxicity.
Hydrogen sulphide
Carbon dioxide
Pond water should contain low concentration of
free CO2.
 Ideal range from 60-300 ppm as CaCO3 and it can
be treated with lime.
 Less than 20 ppm leads to fluctuation and more
than 300 ppm may become unproductive due to
limitation of carbondioxide availability.
Total Alkalinity
Total hardness
It should be greater than 40 ppm because it helps
to protect fish against harmful effect of pH and
metal ions.
Low hardness can be treated with lime.
Sustainable Pond Productivity
Nutrient
removal
Liming
Plankton
removal
Chlorination
Sustainable
Pond
Productivity
It is possible to precipitate phosphorus from pond
water by applying sources of iron, aluminium or
calcium ions.
Alum (aluminium sulphate) or ferric chloride are
commercially available of which the former is cheap
and widely used.
Alum 20-30 ppm is more suitable in alkaline
water (>500 ppm) and gypsum (calcium sulphate)
100-200 ppm is better in low alkaline water.
Nutrient removal
Copper sulpahte 1/100 of the total alkalinity is
recommended for reducing phytoplankton
abundance and blue-green algae in particular.
Plankton removal
It is possible to disinfect bottom of empty pond
and waters in newly filled and unstocked ponds by
applying chlorine products 1ppm or more of free
chlorine residual.
The residuals will detoxify naturally in a few
days so that ponds can be stock safely.
Chlorination
 Liming should be always done depending upon
the pH of the water and the soil.
 As the health of the soil determines the nature of
the pond water, pH of the water can be taken as
reference to determine appropriate dose of
application
Liming
pH
Soil / Water
condition
Dose of lime
(Kg/Ha)
4.0-4.5 Highly acidic 1000
4.5-5.5 Medium acidic 700
5.5-6.5 Slightly acidic 500
6.5-7.5 Near neutral 200
Conclusion
Fish being aquatic are more prone to disease and are
difficult to control. The equilibrium of disease,
environment and fish health are important. Any
change in the equilibrium leads to “stressed” and
becomes vulnerable to disease which have
influences on growth and survival. This equilibrium
can be maintained by proper management of water
and soil, two vital ingredient for any successful
aquaculture practices.
Reference
 Boyd, 1995
 Boyd, C. E., Wood, C. W., & Thunjai, T. (2002). Aquaculture pond
bottom soil quality management. Pond Dynamics/Aquaculture
Collaborative Research Support Program, Oregon State University.
Boyd, C. E., & Tucker, C. S. (2014). Handbook for aquaculture water
quality. Handbook for Aquaculture Water Quality, 439.
https://www.slideshare.net/KRISHNACOF/soil-and-water-
interaction1
 Loganathan, P. (1987). Soil quality considerations in the selection of
sites for aquaculture.
http://epao.net/epSubPageExtractor.asp?src=education.Science_and
_Technology.Soil_and_Water_Quality_Management_in_Aquaculture
https://www.slideshare.net/harapriyabehera3/soil-and-water-
standards
 https://www.slideshare.net/YuvarajanPandiyan/water-quality-
management-in-aquaculture-production-system-aqc-601
Soil And Water Quality In Relation To Fish Production

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Soil And Water Quality In Relation To Fish Production

  • 1. Name - Ipsita Sahoo Reg no- 200705180160 Guided by- Dr. Sitaram Swain School of Applied Science, CUTM, BBSR M Sc. 1st year Zoology Subject- Advance aquaculture Topic- “Soil And Water Quality In Relation To Fish Production” Session- 2020-22
  • 2. Introduction Bottom soil management Water quality management Sustainable pond productivity Conclusion Reference CONTENTS
  • 3. Successful aquaculture depends on providing animal with a satisfactory environment in which they will grow. Good initial condition for aquaculture can be assured by a selecting a site with suitable soil and a high quality water supply. Good bottom soil and water quality are vital ingredient for any successful aquaculture practices. There is increasing evidence that the condition of pond bottoms and the exchange of substances between soil and water strongly influence water quality (Boyd, 1995). Introduction
  • 4. Bottom soil is considered as the chemical laboratory of the pond, so that physicochemical properties like Texture, Soil acidity, Bottom soil oxidation, Drying pond bottom should be balanced. Bottom Soil Management Physicochemical properties for Bottom Soil Management Texture Soil acidity soil oxidation Drying pond bottom
  • 5. The nature and the properties of the parent material forming the soil determine the soil texture. An ideal pond soil should not be too sandy to allow leaching of the nutrients or should not be too clayey to keep all the nutrients absorbed on to it. For sandy soil, heavy dose of raw or composed farmyard manure varies from 10,000 to 15,000 kg/ha/year is required. Texture
  • 6. The soil may be acidic, alkaline or neutral but the ideal range for soil pH is 6-8. Acid ponds do not respond well to fertilization and liming is the only way to improve water. Soil acidity
  • 7.  When the redox potential is low at the soil surface, hydrogen sulphide and other toxic microbial metabolites diffuse into the pond water.  Sodium nitrate (NaNO3) can serve as a source of oxygen for microbes in poorly oxygenated environment in which the redox-potential will not drop low enough for the formation of hydrogen sulphide and other toxic metabolites. Bottom soil oxidation
  • 8.  Evaporation of water from soil pores and cracking of soil during drying enhances aeration and favor microbial decomposition of soil organic matter.  Excessive drying makes soil too dry for microbial activity, so a period of 2-3 weeks is adequate.  Tilling with a disk harrow also improves aeration but compaction is required before refilling to reduce erosion. Drying pond bottom
  • 9.  Water is a most important element in aquaculture. Poor water quality Affect fish & shellfish health through impairment of development and growth . Water Quality Management Physicochemical Properties For Water Quality Management pH Temperature Total hardness Total Alkalinity Turbidity Hydrogen sulphide Dissolved oxygen Carbon dioxide Ammonia
  • 10.  Temperature sets the pace for metabolism and biochemical reaction rates.  The optimum temperature range for cold water and warm water fishes are 4°C-18°C and 24°C-30°C respectively.  Temperature can be adjusted to optimum level in controlled condition like hatcheries but difficult to adjust in large water bodies.  Operation of aerator helps in breaking thermal stratification while planting of trees gives shades. Temperature
  • 11.  pH is a measure of hydrogen ion concentration in water and indicate how much water is acidic or basic.  Water pH affects fish metabolism, physiological process, toxicity of ammonia, hydrogen sulphides and solubility of nutrient thereby well-being and fertility.  pH at the range of 6-9 is best for fish growth and can be increase by application of lime.  Agriculture gypsum may be applied to correct alkaline pH. pH
  • 12.  The optimum dissolved oxygen (DO) content of pond waters is in the range of 5 ppm saturation level.  Aeration is a proven technique for improving DO availability.  Any sort of agitation improves the DO content and among which paddle-wheel, aerators aspirators are most common. Dissolved oxygen
  • 13.  Several factors like suspended soil particle, planktonic organisms and organic matter contributes to turbidity.  Measured using Secchi disc the optimum visibility range from 40-60 cm.  It can be controlled by application of organic manure at 500-1000 kg/ha, gypsum at 250-500 kg/ha or alum 25-50 kg/ha. Turbidity
  • 14.  Fish are very sensitive to unionized ammonia (NH3) and optimum range is 0.02-0.05 ppm in the pond water.  The same is reduced in the case of high DO and high CO2.  Aeration, healthy phytoplankton population removes ammonia from water. Addition of salt 1200- 1800 kg/ha reduces toxicity. Formalin are also use in certain cases.  Biological filter may be use to treat water for converting ammonia to nitrate and then to harmless nitrate through nitrification process. Ammonia
  • 15.  Fresh water fish pond should be free from hydrogen sulphide because at concentration of 0.01 ppm fish lose their equilibrium.  Frequent exchange and increase of pH through liming can reduces its toxicity. Hydrogen sulphide Carbon dioxide Pond water should contain low concentration of free CO2.
  • 16.  Ideal range from 60-300 ppm as CaCO3 and it can be treated with lime.  Less than 20 ppm leads to fluctuation and more than 300 ppm may become unproductive due to limitation of carbondioxide availability. Total Alkalinity Total hardness It should be greater than 40 ppm because it helps to protect fish against harmful effect of pH and metal ions. Low hardness can be treated with lime.
  • 18. It is possible to precipitate phosphorus from pond water by applying sources of iron, aluminium or calcium ions. Alum (aluminium sulphate) or ferric chloride are commercially available of which the former is cheap and widely used. Alum 20-30 ppm is more suitable in alkaline water (>500 ppm) and gypsum (calcium sulphate) 100-200 ppm is better in low alkaline water. Nutrient removal
  • 19. Copper sulpahte 1/100 of the total alkalinity is recommended for reducing phytoplankton abundance and blue-green algae in particular. Plankton removal It is possible to disinfect bottom of empty pond and waters in newly filled and unstocked ponds by applying chlorine products 1ppm or more of free chlorine residual. The residuals will detoxify naturally in a few days so that ponds can be stock safely. Chlorination
  • 20.  Liming should be always done depending upon the pH of the water and the soil.  As the health of the soil determines the nature of the pond water, pH of the water can be taken as reference to determine appropriate dose of application Liming pH Soil / Water condition Dose of lime (Kg/Ha) 4.0-4.5 Highly acidic 1000 4.5-5.5 Medium acidic 700 5.5-6.5 Slightly acidic 500 6.5-7.5 Near neutral 200
  • 21. Conclusion Fish being aquatic are more prone to disease and are difficult to control. The equilibrium of disease, environment and fish health are important. Any change in the equilibrium leads to “stressed” and becomes vulnerable to disease which have influences on growth and survival. This equilibrium can be maintained by proper management of water and soil, two vital ingredient for any successful aquaculture practices.
  • 22. Reference  Boyd, 1995  Boyd, C. E., Wood, C. W., & Thunjai, T. (2002). Aquaculture pond bottom soil quality management. Pond Dynamics/Aquaculture Collaborative Research Support Program, Oregon State University. Boyd, C. E., & Tucker, C. S. (2014). Handbook for aquaculture water quality. Handbook for Aquaculture Water Quality, 439. https://www.slideshare.net/KRISHNACOF/soil-and-water- interaction1  Loganathan, P. (1987). Soil quality considerations in the selection of sites for aquaculture. http://epao.net/epSubPageExtractor.asp?src=education.Science_and _Technology.Soil_and_Water_Quality_Management_in_Aquaculture https://www.slideshare.net/harapriyabehera3/soil-and-water- standards  https://www.slideshare.net/YuvarajanPandiyan/water-quality- management-in-aquaculture-production-system-aqc-601