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Welcome to the 31st IUBS General Assembly and Conference on ...

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Xinqing ZHAO, Chun WAN, Suolian GUO <str<strong>on</strong>g>and</str<strong>on</strong>g><br />

Fengwu BAI<br />

Dalian University of Technology, School of Life Science <str<strong>on</strong>g>and</str<strong>on</strong>g><br />

Biotechnology, 2 Lingg<strong>on</strong>g Road, Dalian 116024, China. Email:<br />

xqzhao@dlut.edu.cn<br />

Microalgae have been used extensively as alternative raw<br />

materials for bioenergy producti<strong>on</strong>. Some microalgae<br />

strains accumulate high c<strong>on</strong>tent of lipids or starch, <str<strong>on</strong>g>and</str<strong>on</strong>g><br />

are promising for biodiesel <str<strong>on</strong>g>and</str<strong>on</strong>g> bioethanol producti<strong>on</strong>.<br />

However, ec<strong>on</strong>omic producti<strong>on</strong> of microalgae products in<br />

large scale is restricted by <str<strong>on</strong>g>the</str<strong>on</strong>g> high cost in cell recovery,<br />

which normally has high energy requirements <str<strong>on</strong>g>and</str<strong>on</strong>g> capital<br />

investment. Recovery of microalgae cells using<br />

biodegradable microbial flocculent is a promising method<br />

without energy costs or sec<strong>on</strong>dary c<strong>on</strong>taminati<strong>on</strong> of<br />

metals. In this study, a novel biflocculant producing<br />

bacterial strain W01 was isolated from active sludge of<br />

civil wastewater, <str<strong>on</strong>g>and</str<strong>on</strong>g> was identified as Solibacillus<br />

silvestris. Culture broth of W01 showed excellent<br />

flocculating ability <strong>on</strong> marine microalgae. The maximum<br />

flocculati<strong>on</strong> efficiency (90%) was obtained after<br />

cultivati<strong>on</strong> of W01 at 37°C for 48 h. The flocculati<strong>on</strong><br />

efficiency of W01 retained stable without any additi<strong>on</strong> of<br />

metal i<strong>on</strong>s. Anthr<strong>on</strong>e reacti<strong>on</strong>, carbazole‐sulfuric acid test<br />

<str<strong>on</strong>g>and</str<strong>on</strong>g> Els<strong>on</strong>‐Morgen method were carried out for natural<br />

sugar, ur<strong>on</strong>ic acid, <str<strong>on</strong>g>and</str<strong>on</strong>g> amino sugar c<strong>on</strong>tent analyses<br />

respectively, <str<strong>on</strong>g>and</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> Fourier‐transform infrared (FTIR)<br />

spectrum of <str<strong>on</strong>g>the</str<strong>on</strong>g> purified bioflocculant indicated <str<strong>on</strong>g>the</str<strong>on</strong>g><br />

presence of hydroxyl, amino groups, peptide linkage <str<strong>on</strong>g>and</str<strong>on</strong>g><br />

ester linkage. The bioflocculant produced by W01 has <str<strong>on</strong>g>the</str<strong>on</strong>g><br />

potential <str<strong>on</strong>g>to</str<strong>on</strong>g> harvest microalgae for cost‐effective energy<br />

producti<strong>on</strong> using microalgae.<br />

Heavy metal stress­induced biological effects<br />

<str<strong>on</strong>g>and</str<strong>on</strong>g> molecular mechanisms investigati<strong>on</strong><br />

Lan WANG<br />

Shanxi University, 92 Wucheng Road, Taiyuan 030006, China.<br />

Email: angel198408@126.com<br />

Many xenobiotics released by industries may exert<br />

potentially adverse effects <strong>on</strong> aquatic organisms.<br />

Cadmium (Cd) is <strong>on</strong>e of <str<strong>on</strong>g>the</str<strong>on</strong>g> most deleterious heavy metals<br />

in aquatic systems. To investigate Cd‐induced biological<br />

effects <str<strong>on</strong>g>and</str<strong>on</strong>g> molecular mechanisms in freshwater<br />

crustacean, freshwater crabs (Sinopotam<strong>on</strong> henanense)<br />

were exposed <str<strong>on</strong>g>to</str<strong>on</strong>g> different c<strong>on</strong>centrati<strong>on</strong>s of Cd for<br />

different time. The relati<strong>on</strong>ship between tissue‐specific<br />

Cd accumulati<strong>on</strong> <str<strong>on</strong>g>and</str<strong>on</strong>g> metallothi<strong>on</strong>ein (MT) inducti<strong>on</strong><br />

was first investigated using <str<strong>on</strong>g>the</str<strong>on</strong>g> Cd saturati<strong>on</strong> assay <str<strong>on</strong>g>and</str<strong>on</strong>g><br />

a<str<strong>on</strong>g>to</str<strong>on</strong>g>mic absorpti<strong>on</strong> spectropho<str<strong>on</strong>g>to</str<strong>on</strong>g>metry method. The<br />

results showed that a positive correlati<strong>on</strong> existed<br />

between MT inducti<strong>on</strong> <str<strong>on</strong>g>and</str<strong>on</strong>g> Cd accumulati<strong>on</strong> both in<br />

hepa<str<strong>on</strong>g>to</str<strong>on</strong>g>pancrease <str<strong>on</strong>g>and</str<strong>on</strong>g> gill. Antioxidant defense system,<br />

including glutathi<strong>on</strong>e (GSH), <str<strong>on</strong>g>and</str<strong>on</strong>g> enzymes such as<br />

superoxide dismutase (SOD), catalase (CAT), <str<strong>on</strong>g>and</str<strong>on</strong>g><br />

glutathi<strong>on</strong>e peroxidase (GPx) <str<strong>on</strong>g>to</str<strong>on</strong>g>ge<str<strong>on</strong>g>the</str<strong>on</strong>g>r with lipid<br />

peroxidati<strong>on</strong> indica<str<strong>on</strong>g>to</str<strong>on</strong>g>r mal<strong>on</strong>dialdehyde (MDA) level<br />

were <str<strong>on</strong>g>the</str<strong>on</strong>g>n determined. The results showed <str<strong>on</strong>g>the</str<strong>on</strong>g>se indices<br />

were changed in a Cd‐c<strong>on</strong>centrati<strong>on</strong> <str<strong>on</strong>g>and</str<strong>on</strong>g> ‐time manner,<br />

<str<strong>on</strong>g>and</str<strong>on</strong>g> severe oxidative damage was observed. Lastly,<br />

apop<str<strong>on</strong>g>to</str<strong>on</strong>g>tic changes were studied. Typical morphological<br />

characteristic <str<strong>on</strong>g>and</str<strong>on</strong>g> physiological changes of apop<str<strong>on</strong>g>to</str<strong>on</strong>g>sis<br />

were observed using a variety of methods (HE staining,<br />

AO/EB doule fluorescent staining, Transmissi<strong>on</strong> Electr<strong>on</strong><br />

Microscope observati<strong>on</strong> <str<strong>on</strong>g>and</str<strong>on</strong>g> DNA fragmentati<strong>on</strong><br />

analysis), <str<strong>on</strong>g>and</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> activities of caspase‐3 <str<strong>on</strong>g>and</str<strong>on</strong>g> caspase‐9<br />

were assayed. The results showed Cd‐induced oxidative<br />

stress can subsequently result in cell apop<str<strong>on</strong>g>to</str<strong>on</strong>g>sis. In<br />

summary, during Cd exposure, MT inducti<strong>on</strong> <str<strong>on</strong>g>and</str<strong>on</strong>g><br />

antioxidant system play an important role as defensive<br />

mechanism. With <str<strong>on</strong>g>the</str<strong>on</strong>g> increasing Cd accumulati<strong>on</strong> <str<strong>on</strong>g>and</str<strong>on</strong>g><br />

<str<strong>on</strong>g>the</str<strong>on</strong>g> saturati<strong>on</strong> of MT inducti<strong>on</strong>, <str<strong>on</strong>g>the</str<strong>on</strong>g> generati<strong>on</strong> rate of<br />

Cd‐induced cy<str<strong>on</strong>g>to</str<strong>on</strong>g><str<strong>on</strong>g>to</str<strong>on</strong>g>xic reactive oxygen species (ROS)<br />

exceeds <str<strong>on</strong>g>the</str<strong>on</strong>g> antioxidative capacity, ROS could fur<str<strong>on</strong>g>the</str<strong>on</strong>g>r<br />

activate apop<str<strong>on</strong>g>to</str<strong>on</strong>g>tic processes that may be mediated via<br />

mi<str<strong>on</strong>g>to</str<strong>on</strong>g>ch<strong>on</strong>dria‐dependent apop<str<strong>on</strong>g>to</str<strong>on</strong>g>sis pathway by<br />

regulating <str<strong>on</strong>g>the</str<strong>on</strong>g> activities of caspase‐3 <str<strong>on</strong>g>and</str<strong>on</strong>g> caspase‐9.<br />

How does cadmium affect <str<strong>on</strong>g>the</str<strong>on</strong>g> oxygen<br />

c<strong>on</strong>sumpti<strong>on</strong> of freshwater crab<br />

Sinopotam<strong>on</strong> henanense<br />

Ruijing XUAN, Hao WU <str<strong>on</strong>g>and</str<strong>on</strong>g> Lan WANG<br />

School of Life Science, Shanxi University, 92 Wucheng Road,<br />

Taiyuan 030006, China. Email: angel198408@126.com<br />

Cadmium (Cd) is <strong>on</strong>e of <str<strong>on</strong>g>the</str<strong>on</strong>g> <str<strong>on</strong>g>to</str<strong>on</strong>g>xic heavy metals in<br />

aquatic systems that could interfere with <str<strong>on</strong>g>the</str<strong>on</strong>g> oxygen<br />

56

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