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Toxicity of reactive red 141 and basic red 14 to algae and waterfleas

机译:活性红141和碱性红14对藻类和水蚤的毒性

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Textile wastewater normally has a visible color although it has low concentration. This may affect the aquatic ecosystem. Two dyestuffs, Reactive Red 141 (RR141) and Basic Red14 (BR14) were used as compound models. RR 141 is an anionic dye which has a big molecule whereas BR 14 is a cationic dye and has a small molecule. The target organisms for toxicity test were green algae (Chlorella sp.) and waterfleas (Moina macrocopa). The effect of humic acid on the toxicity of dyestuffs to test organisms was also investigated. From the observation of cell counts, Chlorophyll a and dry weight of algae in the dye solutions for 4 days, it was found that all parameters increased as times increased. This revealed that algae could utilize dyestuffs as a carbon source. However, BR14 gave higher absorbance than RR141 at the wavelength of 430 nm which competed to the Chlorophyll a for algal photosynthesis. This resulted in the 96-h EC50 of BR14 and RR141 to Chlorella sp. were 10.88 and 95.55 mg/L, respectively. As for dye toxicity to waterfleas, the 48-h LC50 of BR14 and RR141 to waterfleas were 4.91 and 18.26 mg/L, respectively. The high toxicity of BR14 to waterfleas related to the small molecule of dye could pass into the cell and was absorbed by organelles of waterfleas. Toxicity of BR14 in humic acid solution to Chlorella sp. showed less toxic than RR141 in humic acid solution. This dues to the negative charge of humic acid could bound with a positive charge of BR14, resulted in low amount of BR14 remaining in the bulk solution. The toxicity of BR14 and RR141 in humic acid solution to waterfleas was increased as humic acid increased. Hence, the proper treatment of textile wastewater to yield low concentration of dyes in the effluent before discharging to the natural water is needed.
机译:纺织废水虽然浓度低,但通常具有可见的颜色。这可能会影响水生生态系统。两种染料,活性红141(RR141)和碱性红14(BR14)被用作复合模型。 RR 141是具有大分子的阴离子染料,而BR 14是具有小分子的阳离子染料。毒性测试的目标生物是绿藻(Chlorella sp。)和水蚤(Moina macrocopa)。还研究了腐殖酸对染料对测试生物毒性的影响。从细胞数,叶绿素a和染料溶液中藻类的干重观察4天后,发现所有参数随时间增加而增加。这表明藻类可以利用染料作为碳源。然而,BR14在430 nm波长下具有比RR141更高的吸光度,它与叶绿素a竞争藻类的光合作用。这导致小球藻(Chlorella sp)的BR14和RR141的96小时EC50。分别为10.88和95.55 mg / L。至于染料对水蚤的毒性,BR14和RR141对水蚤的48小时LC50分别为4.91和18.26 mg / L。 BR14对与小分子染料有关的水蚤的高毒性可能会进入细胞并被水蚤的细胞器吸收。腐殖酸溶液中BR14对小球藻的毒性。在腐殖酸溶液中显示出比RR141更低的毒性。这归因于腐殖酸的负电荷可能与BR14的正电荷结合,导致本体溶液中残留少量BR14。随着腐殖酸的增加,腐殖酸溶液中BR14和RR141对水蚤的毒性增加。因此,需要对纺织品废水进行适当处理,以在排放到天然水中之前在废水中产生低浓度的染料。

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