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Thursday 29 January 2015

Physical feature and their influences of lakes and ponds, wetland, running water, and their color .




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Lakes and Ponds

Lakes and ponds are inland bodies of standing or slowly moving water. Although lakes and ponds cover only 2 percent of the world's land surface, they contain most of the world's fresh water. Individual lakes and ponds range in area from a few square meters to thousands of square kilometers. In general, ponds are smaller than lakes, though regional idiosyncrasies of naming abound—Henry David Thoreau's famous Walden Pond in Massachusetts has a surface area of 64 acres. Lakes and ponds are an important source of fresh water for human consumption and are inhabited by a diverse suite of organisms.


Physical Features
Light and temperature are two key physical features of lakes and ponds. Light from the sun is absorbed, scattered, and reflected as it passes through Earth's atmosphere, the water's surface, and the water. The quantity and quality of light reaching the surface of a lake or pond depends on a variety of factors, including time of day, season, latitude, and weather. The quality and quantity of light passing through lake or pond water is affected by properties of the water, including the amount of particulates (such as algae) and the concentration of dissolved compounds. (For example, dissolved organic carbon controls how far ultraviolet wavelengths of light penetrate into the water.)
Light and wind combine to affect water temperature in lakes and ponds. Most lakes undergo a process called thermal stratification, which creates three distinct zones of water temperature. In summer, the water in the shallowest layer (called the epilimnion) is warm, whereas the water in the deepest layer (called the hypolimnion) is cold. The middle layer, the metalimnion, is a region of rapid temperature change. In winter, the pattern of thermal stratification is reversed such that the epilimnion is colder than the hypolimnion. In many lakes, thermal stratification breaks down each fall and spring when rapidly changing air temperatures and wind cause mixing. However, not all lakes follow this general pattern. Some lakes mix only once a year and others mix continuously.
The chemistry of lakes and ponds is controlled by a combination of physical, geological, and biological processes. The key chemical characteristics of lakes and ponds are dissolved oxygen concentration, nutrient concentration, and pH . In lakes and ponds, sources of oxygen include diffusion at the water surface, mixing of oxygen-rich surface waters to deeper depths, and photosynthesis. Oxygen is lost from lakes and ponds during respiration by living organisms and because of chemical processes that bind oxygen. The two most important nutrients in lakes and ponds are nitrogen and phosphorus. The abundance of algae in most lakes and ponds is limited by phosphorus availability, whereas nitrogen and iron are the limiting nutrients in the ocean. The acidity of water, measured as pH, reflects the concentration of hydrogen ions . The pH value of most lakes and ponds falls between 4 and 9 (the pH value of distilled water is 7). Some aquatic organisms are adversely affected by low pH conditions caused by volcanic action, acid-releasing vegetation surrounding bog lakes, and acid rain.
Water color

Green Water

All bodies of water go through what we call an "algae bloom" that will turn the water green. It’s a very natural occurrence that happens whenever the water heats up and there is enough "fuel" in the water to feed the algae. Mother Nature has her way of clearing the water. One day, after weeks of not being able to see your fish (much less the bottom of the pond), you may walk out and find that your pond is clear. The following is a list of things that you can do to help Mother Nature do her job.
  • Sun / Shade
Algae, like most plants, need sunlight to survive. Most of us can’t move our pond to the shade, but there are ways to simulate shade. There are products available that color your water blue, such as Pond Shade. You can also create shade for your sunny pond by adding floating plants such as water hyacinths, water lettuce and waterlillies.
  • Starve the Algae
Water plants, especially floaters and anacharis, compete with algae for nutrients in the water. The more plants you have, the more the algae starves and reproduces less. Stock up with plants. You may not want to use fertilizer in your plants until your ecological balance has been met.
Do not scrub the sides of your pond. The green coat that forms on the liner and on the sides and the bottom of the pond is beneficial to the pond itself. The jelly-like substance is algae that is packed with nitrifying bacteria. Nitrifying bacteria is paramount in order to limit the Ammonia levels in the pond. If you want to give your pond a thorough cleaning, start with the bottom of the pond, where parasites and bad bacteria usually forms.

Green Tip:

Grow your own vegetables. This will help to reduces carbon from fertilizers, and transportation.

White Water

If your water is a white, milky color or cloudy you are probably experiencing a bacterial bloom. Nature Clear is a perfect remedy for this situation. It is important that you dose the water correctly and have plenty or aeration (if you have fish) because the coagulation that occurs (after Natural Clear is applied) will consume a great amount of the water’s dissolved oxygen.

Brown Water

Brown water indicates that there is floating dirt and particles in the water. Rotting leaves and debris create "tanning" of the water. There are three things that you can do to clear the brown water.
  • Clean the Filter.
Don’t wash all the filter material with chlorinated water. Instead, take the least dirty pads and wash them with water from your pond (this keeps the good bacteria alive).
  • Use a Water Clarifyer.
Applying the Natural Clear pond treatment can help. It binds minute particles in your water together and forces it to the bottom of the pond. Again, follow precautions and make sure that your system is highly aerated during the process. If in doubt, we have aeration equipment that you can rent for this reason.
  • Vacuum the Pond.
Now you should be able to see the bottom of the pond and all the debris and trash you never knew existed. One of the ponder’s best tools is a shop vac or wet vac. Use it to vacuum the bottom and sides of the pond. Don’t scrub the slime off the sides. It’s beneficial to your eco-system.




Wetlands

A wetland is an ecological community that is inundated either year around or seasonally. There are very different properties of freshwater versus saline wetlands. Numerous national, state and provincial agencies have regulatory interests wetlands  A chief intent of this article is to provide the reader with special interest in wetland delineation, wetland mitigation and wetland biology with insight to additional sources that will be useful.

Wetland phenomenology

Wetland phenomenology is partially defined by plants and animals in residence, but abiotic factors are also crucial in depicting the entirety of the habitat.. Birds and vegetation, for example, are some of the most recognizable, distinguishable features in a wetland landscape, and many researchers focus on the identification of such birds and plants. The Audubon Society uses the U.S. Fish and Wildlife Service definition in The Audubon Society Nature Guides “Wetlands” by William A. Niering.
The gross elements of wetlands include surface water, as well as shallow aquifers. Surface water must be present for sufficient lengths of time that the area is dominated by hydric soils and organisms that are sustained by and physiologically adapted to such saturated and/or inundated conditions. Therefore, seasonal or vernal  pools are also considered wetlands. Hydrology largely determines how the soil develops and the types of plant and animal communities. Wetlands may support species ranging from obligate aquatic to obligate terrestrial.
When the upper part of the soil is saturated with water at growing season temperatures, soil organisms may consume the oxygen in the soil and cause anaerobic conditions unsuitable for most plants. Such conditions also cause the development of soil characteristics (such as color and texture) of so-called hydric soils. The plants that grow in such conditions, such as marsh grasses, are called hydrophytes. Together, hydric soils and hydrophytes provide clues that a wetland area is present.
The presence of water by ponding, flooding, or soil saturation is not always a good indicator of wetlands. Except for wetlands flooded by ocean tides, the amount of water present in wetlands fluctuates as a result of rainfall patterns, snow melt, dry seasons and longer droughts.
Some of the most well-known wetlands, such as the Everglades and Mississippi bottomland hardwood swamps, may have periods of dryness. In contrast, many upland areas are very wet during and shortly after wet weather. Such natural fluctuations must be considered when identifying areas subject to government regulation. Similarly, the effects of upstream dams, drainage ditches, dikes, irrigation, and other modifications must also be considered.

Types of wetlands

Wetlands vary widely because of regional and local differences in soils, topography, climate, hydrology, water chemistry, vegetation, and other factors, including human disturbance. Indeed, wetlands are found from the tundra to the tropics and on every continent except Antarctica. Two general categories of wetlands are recognized: coastal or tidal wetlands and inland or non-tidal wetlands.
Tidal (coastal) marshes occur along coastlines and are influenced by tides and often by freshwater from runoff, rivers, or groundwater. Salt marshes are the most prevalent types of tidal marshes and are characterized by salt tolerant plants such as smooth cordgrass, saltgrass, and glasswort. Salt marshes have one of the highest rates of primary productivity associated with wetland ecosystems because of the inflow of nutrients and organics from surface and/or tidal water. Tidal freshwater marshes are located upstream of estuaries. Tides influence water levels. The lack of salt stress allows a greater diversity of plants to thrive. Cattail, wild rice, pickleweed, and arrowhead are common and support a large and diverse range of bird and fish species, among other wildlife.
Inland wetlands are most common on floodplains along rivers and streams (riparian wetlands), in isolated depressions surrounded by dry land (e.g., playas, basins, and "potholes"), along the margins of lakes and ponds, and in other low-lying areas where the groundwater intercepts the soil surface or where precipitation sufficiently saturates the soil (e.g., vernal pools and bogs). Inland wetlands include marshes and wet meadows dominated by herbaceous plants, swamps dominated by shrubs, and wooded swamps dominated by trees.
Many of these wetlands are seasonal (they are dry one or more seasons every year), and, particularly in the arid and semiarid western United States, may be wet only periodically. The quantity of water present and the timing of its presence in part determine the functions of a wetland and its role in the environment. Even wetlands that appear dry at times for significant parts of the year—such as vernal pools—often provide critical habitat for wildlife adapted to breeding exclusively in these areas; in fact, biodiversity and occurrence rare and restricted range biota is highly correlated with presence of western USA vernal pools.

Wetland categories

Inland wetlands found in the United States fall into five broad categories—marshes, swamps, bogs, vernal pools and fens. Marshes are wetlands dominated by soft-stemmed vegetation, while swamps have mostly woody plants. Bogs are freshwater wetlands, often formed in old glacial lakes, characterized by spongy peat deposits, evergreen trees and shrubs, and a floor covered by a thick carpet of sphagnum moss. Fens are freshwater peat-forming wetlands covered mostly by grasses, sedges, reeds, and wildflowers. Vernal pools are wetlands not subject to permanent inundation and having clearly hydric soils.


Ecological roles of wetlands

Wetlands are among the most productive ecosystems in the world, comparable to rainforests and coral reefs. An immense biodiversity of species of microbes, plants, insects, amphibians, reptiles, birds, fish, and mammals can be part of a wetland ecosystem. Physical and chemical features such as climate, topography, geology, and the movement and abundance of water determine the plants and animals that inhabit each wetland. The complex, dynamic relationships among the organisms inhabiting the wetland environment are referred to as food chains. 
Wetlands can be thought of as "biological supermarkets." They provide great volumes of food that attract many animal species. These animals use wetlands for part of or all of their life-cycle. Dead plant leaves and stems break down in the water to form small particles of organic material called detritus. This enriched material feeds many aquatic insects, shellfish, and small fish that are food for larger predatory fish, reptiles, amphibians, birds and mammals.
The functions of a wetland and the values of these functions to human society depend on a complex set of relationships between the wetland and the other ecosystems in the watershed. A watershed is a geographic area in which water, sediments, and dissolved materials drain from higher elevations to a common low-lying outlet or basin a point on a larger stream, lake, underlying aquifer, or estuary.


Wetland_food_web.gif



Water Quality and Hydrology


Wetlands have important filtering capabilities for intercepting surface water runoff from higher dry land before the runoff reaches open water. As the runoff water passes through, the wetlands retain excess nutrients and some pollutants, and reduce sediment that would clog waterways and affect fish and amphibian egg development. In performing this filtering function, wetlands save us a great deal of money. For example, a 1990 study showed that without the Congaree Bottomland Hardwood Swamp in South Carolina, the area would need a US $5 million wastewater treatment plant.
In addition to improving water quality through filtering, some wetlands maintain stream flow during dry periods, and many replenish groundwater. Many Americans depend on groundwater for drinking.







Running Water
On the continents, aquatic ecosystems are of two kinds: lotic ecosystems, in which the water is free-flowing (streams and rivers), and lentic ecosystems, in which the water is relatively stationary. The scientists who specialize in aquatic ecosystems are limnologists.

Physical Features
The limiting factors that govern what organisms can live in lotic ecosystems include current, light intensity, temperature, pH , dissolved oxygen, salinity, and nutrient availability—variables routinely measured by limnologists to develop a profile of the environment. These conditions differ greatly between small headwater streams and the mouths of such great rivers such as the Mississippi and the Amazon. Living occupants of streams and rivers show corresponding differences along the way.
Small headwater streams, where water first collects by runoff from the land or emerges from springs, are called first-order streams. When two first-order streams meet, they form a second-order stream; two of these converge to form a third-order stream, and so on, until the water may flow into bodies as large as twelfth-order rivers (for example, the Columbia and the Mississippi). Bodies of the first to third order are usually considered streams, and those of the fourth order and larger are considered rivers.
Streams provide diverse habitats including relatively swift rapids and quiet pools. They often have hard substrates of stones, rubble, or bedrock to which animals can cling. Flat rocks and rubble typically harbor the greatest species diversity of stream animals. Stream animals often have flat, streamlined bodies that are not easily swept away by currents, and hooks, suckers, or sticky undersides for clinging to substrates. They tend to face into a current and swim against it, behavior called rheotaxis. Lake animals,



Estuaries
Estuaries are partially enclosed bodies of water that occur where the land meets the ocean. The world's largest estuaries are at the ocean ends of rivers that deliver freshwater from surrounding and sometimes remote upland areas. Estuaries may be configured as sounds, bays, lagoons, or networks of tidal creeks and marshes. Many estuaries are separated from the ocean by barrier islands and do not have major sources of freshwater inflow. Estuaries are more common on coasts with wide and shallow continental shelves than on coasts close to tectonic plate boundaries.
Estuaries are physically and chemically dynamic and complex ecosystems . Annual, seasonal, and daily fluctuations in freshwater input, tidal inundation, temperature, wind, and other hydrological and meteorological factors are responsible for the highly changeable character of estuaries. Due to variations in tidal height, currents, wave exposure, sediment types, salinity, and depth within estuaries, many different types of submerged and intertidal habitats exist. The diversity and interrelatedness of habitats contributes to the biological richness of estuaries.
Temperate and tropical estuaries are among the most biologically productive ecosystems on Earth. Salt marshes dominated by Spartina grasses can produce 5 to 10 tons of organic matter per acre per year, which is more than most agricultural crops. In tropical estuaries, mangroves are the dominant producers. Submerged seagrass beds, macroalgae ("seaweeds"), and phytoplankton also produce organic material that supports abundant and diverse populations of animals. Direct consumption of estuarine plants is important, but many small estuarine animals process decomposing plant material and associated microbes known as detritus. Rich populations of invertebrates living in the sediments and water provide food for shrimps, crabs, fishes, birds, and mammals.
Estuaries support large commercial and recreational fisheries. Crabs, clams, oysters, herrings, drums, striped bass, and other harvested species reproduce and grow within estuaries and rivers. In addition, major fishery species such as shrimps, flounders, mullets, and menhaden, which spawn in the ocean, rely on estuaries as nurseries for juveniles. At least 70 percent of the species harvested in the United States requires a period of estuarine residency




to complete their life cycles. Adult fish, marine mammal, and bird migrations are often timed to coincide with best conditions for reproduction and feeding in estuaries.
Coastal areas, especially estuaries, have always attracted and supported human populations. About 40 percent of the world's population lives within 60 miles of the coast, and 22 of the 32 largest cities are located on estuaries. Human impacts associated with agricultural, industrial, and residential development in coastal watersheds have resulted in changes in freshwater inflow, increases in nutrients, and the destruction of wetlands. Dredging, diversion, and damming have also altered estuarine habitats. Reductions in water and habitat quality and overharvesting have reduced resources and changed biological communities.
Healthy estuaries help to regulate flooding and decompose contaminants. Increasing awareness of impacts and advances in scientific knowledge and technology have led to some success in reducing impacts and restoring water quality. Education and long-term planning are keys to achieving a balance between sustaining economies and preserving the ecological integrity of estuaries.





Wednesday 14 January 2015

Impact of diseases on fish production of baors in Jessore, Bangladesh

Impact of diseases on fish production of baors in Jessore, Bangladesh

Bipul Kumar Dey Md. Mer Mosharraf Hossain Sanjoy Banerjee Bappa Shirin Akter Shoumo Khondoker
Department of Fisheries and Marine Bioscience, Jessore University of Science and Technology, Jessore-7408, Bangladesh
Correspondence: Bipul Kumar Dey, Department of Fisheries and Marine Bioscience, Jessore University of Science and Technology;
Email: bipulkumar.jstu@gmail.com
Received: 07 Jan 2014, Received in revised form: 14 Apr 2014, Accepted: 22 Apr 2014, Published online: 24 Apr 2014
Citation: Dey BK, Hossain MMM, Bappa SB, Akter S and Khondoker S (2014) Impact of diseases on fish production of baors in Jessore,
Bangladesh. Journal of Fisheries 2(1): 70-75. DOI: dx.doi.org/10.17017/jfish.v2i1.2014.11


Abstract
The study was carried out to assess the impact of diseases on fish production in baors of Jessore district,
Bangladesh from March 2012 to January 2013. Studied baors were selected randomly from each sub-district
which covered 39.22% of total baors and 71.87% baor areas in Jessore district. All the surveyed baors were
affected more or less by various diseases and in 80% baors noticeable production loss occurred almost every
year. The main diseases were epizootic ulcerative syndrome (EUS), dropsy, gill rot and fin rot; out breaking
time ranged from November to February each year. EUS was recorded in 85% baors whereas other diseases
were found in various baors at various percentages: dropsy (75%), gill rot (45%) and fin rot (55%). Conferring
to the number of affected fishes, 31.25% were affected by EUS, 37.5% by dropsy, 12.5% by gill rot and 18.75%
by fin rot. In the year 2012, 0.513% loss of production has occurred that designated 0.7599 million BDT.
Through successful work on disease control and management, production loss may be minimized.
Keywords: Impact, fish diseases, production, baor, oxbow lake
INTRODUCTION
Bangladesh has achieved remarkable progress in the
fisheries sector since its independence in 1971 and this
sector have been playing a very significant role and
deserve potential for future development in the agrarian
economy of Bangladesh (DoF 2012). The sector's
contribution to the national economy is much higher than
its 4.39% share in GDP, as it provides about 60% of the
animal protein intake and more than 11% of the total
population of the country is directly or indirectly involved
in this sector for their livelihoods (DoF 2012). The
increasing rate of exporting of fish and fishery products
was 45.54% from the fiscal year 2009-2010 to 2010-2011.
In recent years, this sector performs the highest GDP
growth rate in comparison to other agricultural sectors
(crop, livestock and forestry) (DoF 2012). The growth rate
of this sector over the last 10 years is almost steady and
encouraging, varying from 4.76% to 7.32% with an
average 5.61%. Whereas last four years average growth
rate of this sector is 6.22%. The country's export earnings
from this sector were 2.46% during the fiscal year 2011-
12 (DoF 2012).
Bangladesh is one of the world's leading fish producing
countries and it’s total fish production shows a
consistently increasing trend from the fiscal year 1983-
1984 to 2011-2012 and the production increased more
than four times (754,000 MT in 1983-1984 to 3,262,000
MT in 2011-12) (DoF 2013). The diversified fisheries
resources of the country are divided into three groups,
i.e., inland capture, inland culture and marine capture.
Inland culture includes mainly pond/ditch, baor (oxbow
lake), shrimp/prawn farm, seasonal cultured water body
etc. covering an area of about 774,055 ha and produces
1,726,067 MT fish and shrimp that covers 52.92% of total
production during the fiscal year 2011-2012 (DoF 2013).
There are about six hundred oxbow lakes in four greater
districts of Jessore, Faridpur, Khulna and Kushtia having
many of these concentrations in greater Jessore district
(Hasan 2003, Biswas et al. 2009 and Abdullah-Bin-Farid et
al. 2013). Total 51 baors are situated in Jessore region
(Personal communication: Mr. Haridash, Statistics Officer,
70
BdFISH Publication | journal.bdfish.org | © Creative Commons BY-NC-ND 3.0 License


Impact of diseases on fish production of baors in Jessore, Bangladesh
                                                             Dey et al.
DoF, Jessore). Total area of baors in Jessore region is
1,882 ha (DoF 2011). Though the inland closed water area
is only 16.47% of the total inland water-bodies, but
52.92% of the total yield comes from this inland closed
water area (DoF 2013).
Fishery is the second export earning sector which
contributes about 4.43% of the gross domestic product
(GDP) and it contributes 22.21% in agriculture 2.73% of
total foreign exchange income comes from Fisheries sub
sector (DoF 2012). Disease is one of the major limiting
factors to obtain the production target and among
various diseases bacterial disease in fish is a serious
threat to aquaculture system in Bangladesh. Fish farmers
have been facing great problems due to fish diseases that
cause severe damages and mortality in both culture and
wild fishes (Rahman and Chowdhury 1996). Various types
of diseases such as ulcer type disease including epizootic
ulcerative syndrome, bacterial hemorrhagic septicemia,
tail rot and fin rot, bacterial gill rot, dropsy, columnar
disease, fungal disease and parasitic disease are
important limiting factors for sustainable fish production
(Chowdhury 1997). The major fish diseases occurred in
Bangladesh are epizootic ulcerative syndrome (EUS),
different types of fungal and parasitic diseases etc.
(Chowdhury et al. 2003). Moreover, Tail rot and Fin rot
disease is also found in different fish farms and the rate of
incidence of this type of disease is assumed to be
increased in the recent years (Faruk et al. 2004).
Bangladesh has many baors and Jessore district possesses
a great portion of baor area but no remarkable work was
conducted on fish diseases in baors. So, in the present
study, impact of fish diseases on fish production of baors
in Jessore district was investigated.
METHODOLOGY
Study area and duration: The study was conducted in
various baors of Jessore district, situated in the south-
west part of Bangladesh (Figure 1). The total area of
sample baors is 1352.63 ha which covers 71.87% of total
area of baors in Jessore and the duration of the study was
March 2012 to January 2013.
Sampling framework: Sample baors were selected
randomly ensuring the inclusion of each Upazila (sub-
district, 7 in number). Bangladesh has 5,488 ha baor area
and in Jessore district the total area of baors is 1,882
hectors and thus the Jessore district contains 34.29% baor
area of Bangladesh. Twenty baors (Table 1) were selected
and primary data were collected employing effective
techniques such as personal interview (home visit), focus
group discussion (FGD), and telephonic interview.
Figure 1: Map of Bangladesh indicating the study area.
All the studied baors were managed under community
based fisheries management approach. A total of 144
farmers and concerned members were interviewed for
primary data collection. Fish production, investment and
income data were collected from the respondents during
interview.
Table 1: Surveyed baors and their areas
Name of the baors Area (ha) Name of the baors
Hamidpur
Bukvora
Koikhali
Joghati
Radhanagar
Manikdaha
Purakhali
Zhapa
Khedapara
Khatura
17.40
153.0
47.00
46.47
31.56
08.51
54.25
245.39
57.00
65.00
Hariharnagar
Morshina
Uzzalpur
Krishnachandrapur
Bergobindapur
Kharincha
Konnadaha
Rajgonj
Mohishakura
Bahadurpur
Area (ha)
21.25
21.18
24.29
21.63
226.12
94.67
36.37
37.85
22.64
121.05
Total area: 1352.63 ha
Common fishes of those baors were Labeo rohita, Catla
catla, Cirrhina mrigala, L. calbasu, Hypophthalmichthys
molitrix, Ctenopharyngodon idella, Cyprinus carpio,
Puntius spp., Colisa fasciatus, Channa punctata, C.
striatus, Salmostorma bacaila, Amblypharyngodon mola,
Mystus tengra, Notopterus notopterus, Heteropneustes
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BdFISH Publication | journal.bdfish.org | © Creative Commons BY-NC-ND 3.0 License


Impact of diseases on fish production of baors in Jessore, Bangladesh
J Fish 2(1): 70-75, Apr 2014
fossilis, Clarias batrachus, Glossogobius giuris, Wallago
attu and Chanda ranga. The main diseases were EUS,
dropsy, gill rot and fin rot which were identified in
relation to identifying keys (Table 2). Secondary data
were collected from various government and fisheries
correlated institutions and also collected from websites
and published literatures.
Table 2: Identifying keys for various diseases
Disease Identifying keys
EUS
Abnormal swimming with project out of water;
floating listlessly near the bank; red spots on the body;
ulceration covers large area; deep hemorrhage and
necrosis with black.
Distended abdomen; straw colored inside the body;
scale protrusion; exophthalmia; inflammation of
intestine; swelling and vacuolation of hepatocytes.
Grasping; remain to the surface; lethargic; anorexic
opercula become swollen; frayed appearance of
affected gill tissues; excessive mucus secretion;
damaged opercula.
Whitening area and lesions on the fin margin; frayed
and disintegration of soft tissues between fin rays; loss
of the total fin; damaged caudal fin.
Table 3: Total fish production, total cost and total income from
the studied baors
                                               Year
                        2007 2008 2009 2010 2011 2012
HamidpurTFP23.00 27.00 34.00 38.00 42.00 45.23
               TC00.65 00.54 00.58 00.60 00.65 00.69
               TI00.75 01.16 01.05 01.23 01.35 01.40
BukvoraTFP155.0 163.0 206.0 281.0 337.0 360.5
               TC03.24 03.48 04.29 05.21 06.41 07.24
               TI09.85 12.50 13.84 14.25 19.52 20.75
KoikhaliTFP62.30 62.00 89.30 180.3 110.0 112.6
               TC01.52 01.00 01.92 01.00 01.13 01.13
               TI4.299 3.100 6.230 7.255 7.925 7.928
JoghatiTFP87.43 89.30 94.63 98.79 102.0 105.7
               TC12.98 13.89 18.01 18.79 21.77 25.30
               TI45.79 46.07 49.74 54.93 58.71 62.00
Radhanagor TFP54.60 56.72 62.33 69.02 74.33 80.01
               TC00.82 00.94 01.70 01.96 01.71 01.83
               TI03.80 03.96 04.20 04.63 05.25 05.54
Manikdaha TFP15.03 15.98 18.35 20.01 20.37 22.29
               TC00.20 00.22 00.28 00.30 00.35 00.38
               TI00.60 00.60 00.71 00.78 00.80 00.84
PurakhaliTFP42.20 52.20 63.80 73.80 108.5 115.1
               TC01.56 01.51 02.07 02.13 02.80 03.09
               TI01.54 02.49 02.96 03.17 05.62 06.05
ZhapaTFP95.03 99.50 106.8 112.1 116.3 119.7
               TC01.08 01.15 01.32 01.40 01.60 01.78
               TI05.91 06.08 06.68 07.19 07.28 07.49
Khedapara TFP51.50 59.30 91.70 114.5 116.9 125.6
               TC00.45 00.65 00.96 01.36 01.55 01.72
               TI02.06 02.97 05.28 07.14 06.74 07.20
KhaturaTFP89.25 87.00 114.2 126.8 143.3 153.2
               TC01.52 01.55 01.51 01.98 02.55 02.72
               TI04.84 04.40 06.28 07.79 08.99 09.78
Hariharnagar TFP37.70 35.50 42.60 46.20 50.20 54.70
               TC00.74 00.73 00.73 00.83 00.94 01.17
               TI02.39 02.33 02.57 02.57 02.79 02.99
MorshinaTFP29.70 21.58 28.75 27.15 31.12 34.20
               TC00.28 00.31 00.35 00.35 00.30 00.37
               TI01.53 01.62 01.83 01.43 02.20 02.70
UzzalpurTFP17.00 26.00 34.00 37.50 48.52 51.91
               TC00.24 00.28 00.42 00.47 00.62 00.71
               TI01.04 01.78 02.62 02.76 03.19 03.61
Krishnachan- TFP23.00 23.50 28.00 34.57 47.68 52.71
drapurTC00.35 00.40 00.41 00.54 00.76 00.83
               TI01.50 1.800 2.885 2.701 3.176 3.620
Bergobinda- TFP327.0 330.0 336.0 340.9 344.1 350.3
purTC04.10 04.51 05.02 05.20 05.27 05.65
               TI18.46 20.48 21.34 21.41 21.77 22.63
KharinchaTFP218.0 221.1 225.4 227.0 227.0 230.6
               TC01.91 02.20 02.11 02.31 02.35 02.50
               TI12.08 12.50 12.81 13.06 13.02 13.25
Konnadaha TFP63.60 72.72 76.33 80.02 87.33 93.57
               TC01.09 01.16 01.91 02.17 01.91 02.07
               TI03.82 04.36 05.65 04.36 05.65 06.08
RajgonjTFP54.88 56.78 69.60 74.05 86.78 92.25
               TC00.63 00.66 00.86 00.93 00.96 01.13
               TI03.13 03.29 03.80 04.43 05.22 07.08
Mohishakura TFP31.50 36.25 40.40 44.50 50.94 55.58
               TC00.50 00.58 00.65 00.71 01.02 01.18
               TI01.89 02.18 02.42 02.67 02.85 03.13
Bahadurpur TFP175.5 182.5 202.1 247.5 273.3 292.3
               TC05.01 05.11 05.83 06.31 06.74 07.02
               TI09.65 10.22 11.32 11.65 12.92 13.63
    TFP=Total Fish Production in metric tons, TC=Total cost in million BDT,
                                           TI=Total income in million BDT
Baor
Issues
Dropsy
Gill rot
Fin rot
The following equations were used for estimation of
production loss, the percentage of disease affection and
are average production loss are as follows:
Percentage (%) of production loss
=
                       
                       
100
Percentage (%) of specific disease
=
.                                              
                       
                       
                       
                       
                       
                       
                                                
                       
                       
                       
100
Percentage (%) of average production loss
=
                       
                       
100
Data analysis: The collected data were subjected to
descriptive analyses using the computer software
Microsoft Excel version 2007.
RESULTS
Total fish production, total cost and total income from the
studied baors are presented in Table 3. Total income was
increased in maximum cases between the year of 2007
and 2012. Total cost was also increased this time with
some rare exceptions (Table 3).
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72


Impact of diseases on fish production of baors in Jessore, Bangladesh
                                                             Dey et al.
No specific treatment was used in these baors for specific
fish disease and liming is the only one treatment in every
type of diseases in some baors (Table 4). In 50% baors
lime is used without calculation of the required dose. The
highest average loss from the year 2007 to 2012 has
occurred in Manikdaha Baor (1.446%) and the lowest in
Koikhali Baor (0.428%) (Table 4). Carps and other native
species were found to be affected by disease in all the
baors except Zhapa Baor where only snakeheads (Channa
sp.) were affected. The most violent disease was dropsy
(37.5%), covered the greatest portion in pie chart and
then EUS (31.25%) followed by fin rot (18.75%) and gill rot
(12.5%) in fishes (Figure 2). Because of those diseases
some loss has occurred in almost every year (Table 4). In
80% baors mortality was found noticeable (Table 4). In
50% baors lime was used as control measure of the
diseases and potash (KMnO4) was applied in only one
baor (Table 4).
Table 4: Disease status in studied baors
Baor
Hamidpur
Bukvora
Koikhali
Disease
         Existing AverageAverage % of
Time of
         treat- production lossaverage
outbreak
         ment (kg/yr)(kg/yr) loss
Liming 34871.67
-
-
420
1.204
0.839
0.428
2.700
0.484
1.446
-
-
0.858
0.925
0.531
Due to mortality for diseases total loss of production of
fishes in plotted baors was 0.513% in weight (Table 5) and
that referred 0.7599 million BDT on the aspect of the year
2012.
Figure 2: Various fish diseases recorded in baors
Table 5: Fish production and percentage of fish loss in 2012
Total
production
(MT)
45.23
360.51
112.59
105.71
80.01
22.29
115.07
119.67
125.57
153.24
54.70
34.21
51.91
52.71
350.28
230.56
93.57
92.25
55.58
292.31
2547.97
Total loss
(MT)
0.42
2.10
0.44
2.60
0.32
0.27
-
-
0.80
1.10
0.24
0.21
0.22
0.43
2.09
-
0.50
-
0.29
1.03
13.06
Name of the baors
Hamidpur
Bukvora
Koikhali
Joghati
Radhanagar
Manikdaha
Purakhali
Zhapa
Khedapara
Khatura
Harihornagar
Morshina
Uzzalpur
Krishnachandrapur
Bergobindopur
Kharincha
Konnadaha
Rajgonj
Mohishakura
Bahadurpur
Total (MT)
(%) of loss
EUS, dropsy, Dec-Jan
gill rot
EUS, dropsy, Dec-Feb
gill rot
Dec-Feb
Dec-Jan
Dec-Jan
Nov-Jan
Dec-Feb
Nov-Jan
250418.33 2100
102743.17 440
2600
320
270
           EUS, dropsy,
           fin rot
JoghatiEUS, gill rot,
           fin rot
Radhanagar EUS, dropsy,
           gill rot
Manikdaha EUS, dropsy,
           fin rot
PurakhaliEUS, dropsy
ZhapaEUS
Khedapara
 Only 96306.67
liming
   -66168.33
 Only
liming
   -
 Only
liming
 Only
liming
   -
Potash
  and
 lime
 Lime
   -
 Lime
Lime
18671.67
0.513%
75922.17 Ng
108221.67 Ng
93241.67
800
             EUS, dropsy, Dec-Jan
             gill rot
KhaturaDropsy, gill Dec-Jan
             rot
Harihornagar EUS, dropsy Dec-Feb
118955.00 1100
44483.33
236
            EUS, fin rot
            EUS, gill rot
            EUS, dropsy,
            fin rot
            EUS, dropsy,
            gill rot, fin
            rot
KharinchaDropsy
Konnadaha EUS, dropsy
RajgonjDropsy, fin
            rot
Mohishakura EUS, gill rot,
            fin rot
Bahadurpur EUS, dropsy,
            fin rot
Morshina
Uzzalpur
Krishnachan-
drapur
Bergobindo-
pur
Nov-Jan
Nov-Jan
Dec-Jan
Dec-Jan
28749.50
35820.83
34909.33
210
215
430
0.730
0.600
1.232
0.619
338046.67 2092
[MT=Metric Ton]
Nov-Jan
Dec-Jan
Dec-Feb
Dec-Jan
Dec-Jan
Lime
  -
  -
-
Lime
224841.67 Ng
78928.33 496
72390.00 Ng
43195.00
285
-
0.628
-
0.660
0.450
DISCUSSIONS
In present study, surveyed baors were stocked with
Indian major carps and some exotic carp species. EUS,
dropsy, gill rot and fin rot were the common diseases.
Because of these diseases some lose has occurred due to
death of fish in baors. Similar findings was also reported
by Frerichs and Roberts (1989), they have mentioned that
73
228855.00 1030
[Yr=Year; Ng=Negligible]
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Impact of diseases on fish production of baors in Jessore, Bangladesh
J Fish 2(1): 70-75, Apr 2014
tail rot and fin rot diseases are widely distributed in
tropical as well as temperate countries and most species
of fish are susceptible to these diseases. The major fish
diseases occurred in Bangladesh are EUS, Aeromonas
septicemia, different types of fungal and parasitic
diseases etc. affording to Chowdhury et al. (2003).
In this study, in all studied baors, time of disease outbreak
ranges from November to February (4 months) and
during this period mortality of fishes has been reported in
many baors. During December 1992 to February 1993
EUS was found in Puntius sp. and another carp in
Karnataka, India (Karunasagar et al. 1995). Various
diseases of fish were also recorded in Indian major carps
in the months November to December in Mymensingh,
Bangladesh (Baqui 1995). Necrosis, inflammation,
hemorrhage, hypertrophy, hyperplasia missing of primary
secondary gill lamellae were found within the months of
December and January in Anabas testudineus that was
recounted by Ahmed et al. (2007). So, it can be said that
fishes are susceptible to various diseases among the
months of November to February.
This was estimated that 31.25% fishes were affected by
EUS, 18.75% by fin rot, 12.5% by gill rot and 37.5% by
dropsy and totally 0.513% production loss has occurred
during the year of 2012. Most species of fish are
susceptible to tail rot and fin rot diseases and those may
cause large mortality that was stated by Frerichs and
Roberts (1989). Tail rot and fin rot diseases also reported
in C. catla and A. testudineus in some fish farms of
Bangladesh and the affected fishes showed lesion and
erosion on the tail and fins and approximately 40%
mortality was recorded in those farms (Foysal 2010).
Among the studied baors, the fish production and income
are increased with the increasing cost and/or investment
except some exceptions; some losses were occurred
between 2007 and 2012.Four diseases were responsible
for the loss of 0.513% of total fish production in the year
of 2012. In 50% disease affected baors lime was used
which was not sufficient to control the diseases.
Further study on fish diseases to find out their causes and
pathogens are recommended. An adaptable treatment
process should be developed and recommended to the
farmers so that loss of fish production due to fish diseases
could be reduced.
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