Centre for Environmental Sustainability, University of Technology Sydney, Broadway, New South Wales, Australia.
Environ Toxicol Chem. 2014 May;33(5):1179-86. doi: 10.1002/etc.2545. Epub 2014 Mar 27.
Bicarbonate is often a major ionic constituent associated with produced waters from methane gas extraction and coal mining, yet few studies have determined its specific toxicity. Currently, the environmental risk of bicarbonate anion in water discharges is assessed based on the toxicity of sodium chloride or artificial seawater and is regulated via electrical conductivity. Increased NaHCO(3) added to Ceriodaphnia dubia in synthetic or natural water gave similar 48-h 10% effective concentration (EC10) values of 1750 ± 125 mg NaHCO(3)/L (mean ± standard error) and 1670 ± 180 mg NaHCO(3)/L, respectively. Bicarbonate was toxic to C. dubia in both waters with conductivities above 1900 µS/cm. In contrast, when conductivity was elevated with NaCl, toxicity to C. dubia was observed only above 2800 µS/cm. Bicarbonate also impaired C. dubia reproduction with an EC10 of 340 mg NaHCO(3)/L. Major ion composition also influenced Zn bioavailability, a common co-occurring metal contaminant in coal mine waters, with sublethal concentrations of NaHCO(3) and elevated pH increasing Zn toxicity. Higher pH was the dominant parameter determining a 10-fold increase in the 48-h 50% effective concentration (EC50) for Zn toxicity to C. dubia at pH 8.6 of 34 µg Zn/L (95% confidence limit = 32-37 µg Zn/L) compared with the Zn toxicity at approximately circumneutral pH. Exposure of the freshwater shrimp Paratya australiensis (Atyidae) in natural water to increasing bicarbonate gave a mean 10-d 10% lethal concentration (LC10) of 850 ± 115 mg NaHCO(3)/L, associated with a mean conductivity EC10 of 1145 µS/cm, which is considerably lower than toxicity of NaCl and artificial seawater to this species reported elsewhere. Because toxicity was influenced by salt composition, specific ions should be regulated rather than conductivity alone in mine wastewater discharges.
碳酸氢盐通常是甲烷气体开采和采煤产生的水中的主要离子成分,但很少有研究确定其具体的毒性。目前,水排放中碳酸氢根阴离子的环境风险是根据氯化钠或人工海水的毒性来评估的,并通过电导率进行调节。在合成水或天然水中向哲水蚤添加增加的 NaHCO(3),得到相似的 48 小时 10%有效浓度 (EC10) 值,分别为 1750 ± 125 mg NaHCO(3)/L(平均值 ± 标准误差)和 1670 ± 180 mg NaHCO(3)/L。在电导率高于 1900 µS/cm 的两种水中,碳酸氢盐对哲水蚤均有毒。相比之下,当用电导率升高 NaCl 时,仅在电导率高于 2800 µS/cm 时才观察到对哲水蚤的毒性。碳酸氢盐还降低了哲水蚤的繁殖能力,其 EC10 值为 340 mg NaHCO(3)/L。主要离子组成也影响锌的生物利用度,这是煤矿水中常见的共存金属污染物,亚致死浓度的 NaHCO(3) 和升高的 pH 值增加了锌的毒性。较高的 pH 值是决定在 pH 8.6 时锌对哲水蚤的 48 小时 50%有效浓度 (EC50) 增加 10 倍的主要参数,锌毒性为 34 µg Zn/L(95%置信限 = 32-37 µg Zn/L),而在接近中性 pH 值时,锌毒性约为 34 µg Zn/L。在天然水中,对淡水虾 Paratya australiensis(Atyidae)暴露于增加的碳酸氢盐,得到 10 天的 10%致死浓度(LC10)的平均值为 850 ± 115 mg NaHCO(3)/L,与 1145 µS/cm 的平均电导率 EC10 相关,这明显低于其他地方报道的该物种对 NaCl 和人工海水的毒性。由于毒性受盐组成的影响,在矿山废水排放中,应调节特定离子而不仅仅是电导率。