Hong-Thih Lai

Effects of chloramphenicol, florfenicol, and thiamphenicol on growth of algae Chlorella pyrenoidosa, Isochrysis galbana, and Tetraselmis chui

This study investigated the growth inhibition effects of three phenicol antibiotics on microalgae used in aquaculture. Different dose levels of chloramphenicol (CAP), florfenicol (FF), and thiamphenicol (TAP) were added to cultures of one freshwater green alga, Chlorella pyrenoidosa, and two marine algae, Isochrysis galbana and Tetraselmis chui. For the two marine algae, FF showed higher toxicity levels (EC50, 1.3-8 mg l(-1)) than CAP (4-41 mg l(-1)) and TAP (38-158 mg l(-1)). CAP was more toxic to the freshwater algae (EC50, 14 mg l(-1)) than FF (215 mg l(-1)) and TAP (1283 mg l(-1)). TAP was the least toxic to the three algae, but maintained the highest stability during the test period. Among the tested algae, T. chui was the species most sensitive to the three antibiotics. This study demonstrates that all three phenicol antibiotics can inhibit growth of the three microalgae and should be carefully used in aquaculture.

Degradation of oxolinic acid and flumequine in aquaculture pond waters and sediments

Oxolinic acid (OA) and flumequine (FLU) are two of the quinolone antibiotics (QAs) that are widely used in aquaculture. The purpose of this study was to understand the fates of OA and FLU in waters and sediment slurries from aquaculture ponds in a laboratory experiment. Waters and sediments were sampled from an eel (Anguilla japonica) pond and a shrimp (Penaeus vannamei) pond. The effects of light, microbial activities, and temperature on the degradation of these two QAs were elucidated. Results indicated that light plays a major role in the degradation of OA and FLU in waters and sediment slurries. Under illuminated and non-sterile conditions, the half-lives (t(1/2)) of OA were 2.3-4.8 and 9.5-15.0 days in the waters and sediment slurries, respectively. For FLU, under the same conditions, t(1/2) values were 1.9-2.3 and 3.6-6.4 days, respectively. Photodegradation of OA and FLU was much faster in water than in sediment slurry. In both environments, degradation became very slow or would plateau after only minimal change in the dark. Besides the effect of light, biodegradation had very minor effects on the degradation of the two QAs in the sediment slurries. The only independent biodegradation was found when OA was placed in shrimp pond sediment slurry, but at a much lower rate (t(1/2) of 98.7 days) than in light. Biodegradation of FLU was also found in the eel pond sediment slurry but only through an additional connection with light. Also, re-addition enhanced the degradation of OA in shrimp pond sediment slurry, but slowed the degradation of FLU in the eel pond sediment slurry in the dark. The temperature experiment in this study showed no significant effects on degradation of the two QAs in either pond waters or sediment slurries.

Implication of light sources and microbial activities on degradation of sulfonamides in water and sediment from a marine shrimp pond

In this study, the effects of natural, visible and ultraviolet lights, microbial activities and aerobic and anaerobic conditions on degradation of four different sulfonamide antibiotics (SAs) were studied. Water and sediment collected from a marine shrimp pond were examined and a factorial design was employed to evaluate the effects of selected parameters. The results showed that all the SAs in water and sediment had significant declines attributed to natural light and microbial activities. The half-lives (t(1/2s)) of SAs in non-sterile water and sediment samples under natural light were 2.0-15.0 and 0.7-7.3 days, respectively, and slowed to 2.9-62.9 and 6.9-85.6 days after sterilized. Moreover, the declines of SAs were significantly faster under ultraviolet than visible light with 36.5-70.9% shorter t(1/2)s. Anaerobic condition was also effective on declines of SAs in sediment. Both sulfate-reducing and methanogenic microbes were directly involved in the decline of SDM, and indirectly contributed to SMX declines.

Transformation of chloramphenicol and oxytetracycline in aquaculture pond sediments

Abstract Transformation processes of two antibiotics, chloramphenicol (CM) and oxytetracycline (OTC), in aquaculture pond sediments collected from a freshwater eel pond and a marine shrimp pond were investigated. The sorption rates of CM in the freshwater and marine sediment slurries (10%, wt/vol) were 4% and 2%, respectively. In contrast, the sorption rates of OTC in the freshwater and marine sediment slurries (10%, wt/vol) were 99.8% and 90.3%, respectively. CM amended at 60–70 mg/L was transformed within 4 days in the freshwater and marine pond sediment slurries when incubated under anaerobic conditions, and within 12 days under aerobic conditions. OTC amended at 60–70 mg/L was not transformed after incubation for 70 days in the freshwater and marine pond sediment slurries under anaerobic conditions. However, OTC was transformed to undetectable levels within 47 days when incubation proceeded under aerobic conditions. OTC was in fact also removed in the sterile sediment slurries under aerobic conditions...

Difference in the regulation of IL-8 expression induced by uropathogenic E. coli between two kinds of urinary tract epithelial cells

Bacterial adherence to epithelial cells is a key virulence trait of pathogenic bacteria. The type 1 fimbriae and the P-fimbriae of uropathogenic Escherichia coli (UPEC) have both been described to be important for the establishment of urinary tract infections (UTI). To explore the interactions between the host and bacterium responsible for the different environments of UPEC invasion, we examined the effect of pH and osmolarity on UPEC strain J96 fimbrial expression, and subsequent J96-induced interleukin-8 (IL-8) expression in different uroepithelial cells. The J96 strain grown in high pH with low osmolarity condition was favorable for the expression of type 1 fimbriae; whereas J96 grown in low pH with high osmolarity condition was beneficial for P fimbriae expression. Type 1 fimbriated J96 specifically invaded bladder 5637 epithelial cells and induced IL-8 expression. On the contrary, P fimbriated J96 invaded renal 786-O epithelial cells and induced IL-8 expression effectively. Type 1 fimbriated J96-induced IL-8 induction involved the p38, as well as ERK, JNK pathways, which leads to AP-1-mediated gene expression. P fimbriated J96-induced augmentation of IL-8 expression mainly involved p38-mediated AP-1 and NF-κB transcriptional activation. These results indicate that different expression of fimbriae in J96 trigger differential IL-8 gene regulation pathways in different uroepithelial cells.

Modeling the effects of sodium chloride on degradation of chloramphenicol in aquaculture pond sediment

Sodium chloride was added to aquaculture pond sediment to determine effects of different salinities on degradation of chloramphenicol (CM). In this experiment, freshwater (0 ppt salinity) eel pond sediment slurries (10% w/v) were amended with sodium chloride to obtain salinities of 12, 24 and 36 ppt. There were no significant differences in sorption rate either between aerobic and anaerobic conditions or among various salinities. Degradation of CM fitted well to the decaying exponential curve. The degradation rates under anaerobic conditions were significantly greater than those under aerobic conditions. As salinity increased, the degradation rates decreased under both aerobic and anaerobic conditions. The differences in degradation rates either between aerobic and anaerobic conditions or among various salinities were attributed to the effects of microbial activities under different environments.

Effects of light and microbial activity on the degradation of two fluoroquinolone antibiotics in pond water and sediment.

Enrofloxacin (ENR) and ciprofloxacin (CIP) are two fluoroquinolone (FQ) antibiotics widely used to treat diseases of human beings and cultured animals. These two FQs are usually detected in the effluent of municipal sewage plants and related aquatic environments. The purpose of this study was to understand the fates of ENR and CIP in aquaculture pond water and a sediment slurry in a laboratory-scale experiment. Effects of light and microbial activity on the degradation of these two FQs were investigated. Results indicated that natural irradiation plays a major role in the degradation of ENR and CIP in pond water and the sediment slurry. The 50 % dissipation times (DT50) with non-sterile treatment were 0.01 and 18.4 d for ENR, and 0.04 and 17.3 d for CIP in the water and sediment slurry, respectively. On the other hand, the degradation of ENR and CIP under dark conditions was slow or even hindered, and all of their DT50 values exceeded 100 d. These two FQs degraded faster in the sediment slurry than in pond water under dark conditions. Artificial ultraviolet (UV) and fluorescence light had similar effects on the degradation of ENR in the pond water and sediment slurry. Degradation of CIP was faster with UV than with fluorescence light treatment, while no such difference was found for ENR degradation. CIP was a degradation product of ENR under both light and dark conditions, and DT50 values for both compounds were shorter in the presence of light. The phenomenon of biodegradation was observed during degradation of CIP in the sediment slurry under natural light.

Toxicity of the veterinary sulfonamide antibiotic sulfamonomethoxine to five aquatic organisms.

The purpose of this study was to investigate the acute and chronic toxicity of sulfamonomethoxine (SMM) to aquatic organisms to evaluate its impact at different trophic levels in the ecosystem. Regarding the growth inhibition of microalgae, SMM exhibited 72-h median effective concentration (EC50) values of 5.9mgL(-1) for freshwater Chlorella vulgaris and 9.7mgL(-1) for marine Isochrysis galbana. In a study on the cladocerans, SMM exhibited acute toxicity and 48-h median lethal concentrations of 48mgL(-1) for Daphnia magna and 283mgL(-1) for D. similis. An examination of chronic toxicity revealed that SMM inhibited the brook production of the cladocerans and exhibited 21-day EC50 values of 14.9mgL(-1) for D. magna and 41.9mgL(-1) for D. similis. This study investigated the potentially adverse effects of SMM on aquatic organisms and revealed that microalgae exhibited higher sensitivity to SMM than cladocerans did. The residue of SMM in water is recommended to be carefully evaluated to reduce ecological impacts after applied to cultured animals.

Effects of light regime and oxygen profile on transformation of oxolinic acid in pond sediment

This study investigated the effects of light (visible light - 5800 lux, 24h) or dark regime and aerobic or anaerobic condition on the decay of added oxolinic acid (OA) at 5, 10 and 20 mg L(-1) in eel pond sediment. An asymptotic decaying exponential model C(t)=C(min)+C(o) × exp (-k × t) was used to facilitate quantitative approach to OA transformation, where C(t) is the concentration of OA after t days, C(min) the estimated level-off concentration of OA residue, C(o) the concentration of added OA and k the decaying coefficient. OA decayed faster under light (C(min)=4.6 mg L(-1)) than under dark (C(min)=7.8 mg L(-1)) and also decayed faster under aerobic (C(min)=4.0 mg L(-1)) than under anaerobic condition (C(min)=8.5 mg L(-1)). C(min) increased with C(o). Sundrying and tilling eel pond bottom should be able to reduce OA residue significantly.

Development and assays estradiol equivalent concentration from prawn (p-EEQ) in river prawn, Macrobrachium nipponense, in Taiwan.

The present study established a fast and convenient bioassay method for aqueous ecosystems using the prawn estradiol equivalent concentration (p-EEQ) of male Macrobrachium nipponense, which produce vitellogenin (VTG) after exposure to xeno-estrogens. This method was then used to determine the concentrations of xeno-estrogen pollutants in the rivers of Taiwan. To establish the calibration curve for the concentrations based on the p-EEQ, the induced VTG content was determined using the alkali-labile phosphate method after male M. nipponense were exposed to 0, 10, 100, 1,000 and 10,000ng/L of 17β-estradiol for 1, 3, 5, 7, 10 and 14 days, respectively. The results of the experiments showed that the induced VTG content in all of the experimental groups stabilized after 10 days, except for the 10,000ng/L experimental group, in which the induced VTG content decreased after 10 days. A 17β-estradiol-VTG10day response curve was then established based on the induced VTG content in the 0, 10, 100 and 1000ng/L experimental groups at day 10. After establishing the curve, male M. nipponense were captured from the upper, middle and lower reaches of the Chuo-shui River, the Beigang River, the Jishui River, the Agongdian River and the Sichong River in Taiwan, and the VTG content in these prawns was determined. In addition, the p-EEQ in the waters was determined based on the VTG content, and the estradiol equivalent concentration (EEQ) in the waters was also measured immediately after sampling using the solid-phase extraction-enzyme-linked immunosorbent assay (SPE-ELISA) method. The results showed that the p-EEQ in the middle and lower reaches of the rivers in certain parts of Taiwan ranged from 38 to 400ng/L, and the detection rate was 100%. Moreover, the EEQ ranged from 7.9 to 92.9ng/L, and the detection rate was 42.9%, indicating that most of the middle and lower reaches of the rivers in Taiwan were polluted by xeno-estrogens. The 17β-estradiol concentrations determined based on the p-EEQ were all higher than those based on the EEQ (SPE-ELISA method). The results of the present study showed that the use of M. nipponense to determine the p-EEQ in environmental waters provided advantages that included a high detection rate, high sensitivity and convenience. However, the p-EEQ cannot be used in waters that do not contain M. nipponense.