• Korean Journal of Veterinary Research
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• v.36 no.3
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• pp.681-692
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• 1996

The present study was conducted to isolate Babesia gibsoni by culture method of the microaerophilous stationary phase(MASP) and analyse the antigenic properties of the parasite by SDS-PAGE and immunoblot. The results obtained were summarized as follows. The protozoan parasite Babesia gibsoni multiplied in canine erythrocytes in RPMI 1640 medium(pH7.0) containing 20 40% normal canine serum under the MASP condition of 5% CO2 and 95% air at $37^{\circ}C$ incubator. The levels of parasitaemia in the erythrocytes were shown more higher by exchanging the medium at 24 hours interval. Under the above condition of MASP, the percentage of parasitized erythrocytes(PPE) after incubation for 8 days increased about 14 times more than that in the initiation of the 1% infected canine erythrocyte culture. The parasites were purely isolated from the MASP culture of red blood cells collected from dogs infected with Babesia gibsoni naturally or artificially. Among the total of 36 canine(Pit-bullterier) blood samples the parasites were isolated from 17 cases(47.2%) in the MASP culture while the parasites were detected from 20 cases(56%) and 12 cases(33.3%), respectively, by indirect fluorescent antibody(IFA) test and direct light microscopy(DLM). On the other hand, Babesia gibsoni was isolated by MASP culture from 15 cases(75%) and 11 cases(92%) of positive cases of IFA and DLM, respectively. In the analysis of the erythrocytic merozoite(AEOM) antigen derived from infected dog approximately 11 antigenic bands in molecular weight of 130, 120, 97.4, 92, 80, 52, 50, 42, 36, 30 and 29 KDa were observed on SDS-PAGE. Antigenic bands in the endoerythrocytic merozoite(CEOM) antigen derived from infected erythrocyte (sediment) in MASP culture were much similar to those of AEOM bands. In the exoerythrocytic merozoite(CEEM) antigen derived from supernatant of the infected erythrocyte culture approximately 20 antigenic bands were observed and the molecular weight of the major bands among these were 140, 120, 114, 105, 96, 93, 92, 80, 60, 52, 50, 38, 36, 30, 24, 18.5 and 16 KDa. In the protein patterns of AEOM and CEOM antigen by immunoblot 15 bands were observed and these patterns were much similar between each other. The molecular weight of the major bands in the both antigens were 130, 120, 80, 60, 52, 50, 42, 30, 29, 18.5 and 16 KDa. Approximately 21 bands were observed in CEEM antigen and the molecular weight of the major bands were 140, 120, 96, 92, 85, 80, 76, 60, 52, 50, 37, 30, 24, 16 and 15 KDa. The specific antigenic bands in the artificially infected dogs were firstly observed at 3 weeks afrer inoculation of infected blood and these antigenic bands were maintained up to 18 months after inoculation. In the immunoblot of the sera of the splenectomized dogs the specific antigenic bands with the molecular weight of 93 KDa and 52 KDa, respectively, were observed weakly comparing to those of non-splenectomized dog. In immunoblot of the sera collected from the naturally infected dogs the antigenic bands were observed as same as those of artificially infected dogs while antigenic band of 29 KDa in some individual dog showed strongly. In comparison of immunoblot of the sera collected from dogs non-treated and treated with diminazene aceturate(7mg/kg, IM) after artificial infection no differences of antigenic bands were observed. In analysis of antigenic bands by digoxigenin glycan/protein double labeling, antigenic bands in the molecular weight of 106, 60 58, 36, 30 and 29 KDa were determined as glycoproteins.

• Journal of Life Science
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• v.17 no.10
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• pp.1309-1314
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• 2007

Investigation on health conditions of Thai koi (Anabas testudineus) were carried out through clinical and histopathological observations from different farms of Mymensingh district for seven months during August 2006 to February 2007. Fish sampling and water quality parameters (temperature, dissolved oxygen and pH) were monitored on a monthly basis. Clinical examination of fishes was also carried out for any kind of abnormalities at monthly intervals. Samples of skin, muscle, gill, liver and kidney were observed by histological technique. Among the water quality parameters the values of water temperature, dissolved oxygen were found to be at unfavorable level for fish during the colder months in the farms. Clinically it was observed that fishes were more affected from December to January and almost normal in appearance during August to September and February. Different clinical symptoms like scale loss, dermal lesion, ulcer and loss of caudal fin were noticed in December and January. In histopathological study, structures of fish organs were normal from August to September. In the months of October and November, minor pathologies were found to be started. Marked pathological changes like necrosis, pyknosis, inflammation, hemorrhage, hypertrophy, hyperplasia, missing of primary and secondary gill lamellae were observed in the months of December and January. Whereas, in the month of February the pathological condition of fish gradually reduced. Again when considered individual fish farm, fishes of Reliance Aqua Farm were more affected than Sotota Matshya Hatchery. The study showed that severity of clinical and pathological changes were increased in December and January. During the period EUS and protozoan diseases were noticed in A. testudineus of the investigated farms.

• Journal of Life Science
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• v.22 no.10
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• pp.1324-1329
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• 2012

The objective of this study was to evaluate the in vitro effects of organic acids on methane emission and ruminal fermentation characteristics. We expected our methodology to result in a decrease of methanogens attached to the surface of rumen ciliate protozoa by addition of organic acids and in particular a decrease in methane emission. A fistulated Holstein cow of 650 kg body weight was used as a donor of rumen fluid. Organic acids (aspartic acid, fumaric acid, lactic acid, malic acid, and succinic acid) known to be propionate enhancers were added to an in vitro fermentation system and incubated with rumen fluid. The microbial population, including bacteria, protozoa, and fungi, were enumerated, and gas production, including methane and fermentation characteristics, were observed in vitro. Organic acids appeared to affect the rumen protozoan community. The rumen protozoal popuation decreased with the addition of aspartic acid, fumaric acid, lactic acid, and malic acid. In particular, the methane emission was reduced by addition of lactic acid. The concentration of propionate with all organic acids that were added appeared to be higher than that of the control at 12 h incubation. Addition of organic acids significantly affected rumen bacteria and microbial growth. The bacteria in added fumaric acid and malic acid was significantly higher (p<0.05) and protozoa was significantly lower (p<0.05) than that of the control. Microbial growth with the addition of organic acids was greater than the control after 48 h incubation.

• Korean Journal of Ecology and Environment
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• v.44 no.1
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• pp.9-21
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• 2011

This study is conducted to know the change in water environment of Lake Hwajinpo from 2000 to 2008 with physico-chemical parameters; salinity, dissolved oxygen, total phosphorus and total nitrogen and others. And zooplanktons and phytoplanktons were studied from 2007 to 2008. From the water quality data of Lake Hwajinpo from 2000 to 200S; water temperature, salinity, transparency, chemical oxygen demand and dissolved oxygen ranges are $2.8{\sim}29.4^{\circ}C$, 0.23~33.2‰, $0.2{\sim}1.8\;m$, $0.2{\sim}20.2\;mg\;L^{-1}$ and $0.1{\sim}17.4\;mg\;L^{-1}$ and the average values are $18.0^{\circ}C$, 15.7‰, 0.7 m, $5.7\;mg\;L^{-1}$ and $8.0\;mg\;L^{-1}$, respectively. Total phosphorus (TP) and total nitrogen (TN) ranges are $0.024{\sim}0.869\;mg\;L^{-1}$ (average 0.091) and $0.240{\sim}5.310\;mg\;L^{-1}$ (average 1.235). Average TN/TP ratio is 16.4. The annual variations in COD, TP, TN and Chl.${\alpha}$ are compared. COD in 2000 is $4.83\;mg\;L^{-1}$ and 2008 is $1.80\;mg\;L^{-1}$ which is reduced by $0.34\;mg\;L^{-1}$ every year. TP in 2000 is $0.07\;mg\;L^{-1}$ and 2008 is $0.05\;mg\;L^{-1}$ reduced gradually. Yearly reduction in TN is $0.09\;mg\;L^{-1}$, in 2000 and 2008 the values are $1.54\;mg\;L^{-1}$ and $0.77\;mg\;L^{-1}$ respectivly. Chl.${\alpha}$ in 2000 is $46.30\;{\mu}g\;L^{-1}$ and $5.78\;{\mu}g\;L^{-1}$ in 2008; yearly reduction is $4.50\;{\mu}g\;L^{-1}$. The tropic state index (TSI) in south and north parts of Lake Hwajinpo in 2000 are 67 and 63 which are reduced to 63 and 59 in 2008 respectively. North and south part of Lake Hwajinpo have 67 species of phytoplankton under 47 families in 2007 and 2008. Dominant species in south part in 2007 are; Asterococcus superbus in May, Lyngbya sp. in September and Trachelomonas spp. in November and in 2008 Anabaena spiroides in August are abundant and varies with time. Zooplankton species in Lake Hwajinpo are 25 of 25 families. Dominant species in south part in May and August 2007 and May and November in 2008 Copepoda larvae and in September 2007 Protozoa spp. of Protozoan and Brachionus plicatilis and Brachionus urceolaris of Cladocera in August 2008. Dominant species in north part Asplanchna sp. of Cladecera in August and November 2007 and rest of the time are larvae of Copepoda. In this way, the water quality of Lake Hwajinpo is changing with slow rate in the long period specially nutrients concentration (TP, TN etc) is decreasing.