首页> 外文期刊>Environmental toxicology and chemistry >Toxicity, biotransformation, and mode of action of arsenic in two freshwater microalgae (Chlorella sp. and Monoraphidium arcuatum).
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Toxicity, biotransformation, and mode of action of arsenic in two freshwater microalgae (Chlorella sp. and Monoraphidium arcuatum).

机译:两种淡水微藻(小球藻和弓形藻)中砷的毒性,生物转化和作用方式。

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The toxicity of As(V) and As(III) to two axenic tropical freshwater microalgae, Chlorella sp. and Monoraphidium arcuatum, was determined using 72-h growth rate-inhibition bioassays. Both organisms were tolerant to As(III) (72-h concentration to cause 50% inhibition of growth rate [IC50], of 25 and 15 mg As[III]/L, respectively). Chlorella sp. also was tolerant to As(V) with no effect on growth rate over 72 h at concentrations up to 0.8 mg/L (72-h IC50 of 25 mg As[V]/L). Monoraphidium arcuatum was more sensitive to As(V) (72-h IC50 of 0.25 mg As[V]/L). An increase in phosphate in the growth medium (0.15-1.5 mg PO4(3-)/L) decreased toxicity, i.e., the 72-h IC50 value for M. arcuatum increased from 0.25 mg As(V)/L to 4.5 mg As(V)/L, while extracellular As and intracellular As decreased, indicating competition between arsenate and phosphate for cellular uptake. Both microalgae reduced As(V) to As(III) in the cell, with further biological transformation to methylated species (monomethyl arsonic acid and dimethyl arsinic acid) and phosphate arsenoriboside. Less than 0.01% of added As(V) was incorporated into algal cells, suggesting that bioaccumulation and subsequent methylation was not the primary mode of detoxification. When exposed to As(V), both species reduced As(V) to As(III); however, only M. arcuatum excreted As(III) into solution. Intracellular arsenic reduction may be coupled to thiol oxidation in both species. Arsenic toxicity most likely was due to arsenite accumulation in the cell, when the ability to excrete and/or methylate arsenite was overwhelmed at high arsenic concentrations. Arsenite may bind to intracellular thiols, such as glutathione, potentially disrupting the ratio of reduced to oxidized glutathione and, consequently, inhibiting cell division.
机译:As(V)和As(III)对两种无菌的热带淡水微藻Chlorella sp。的毒性。使用72小时生长抑制生物测定法测定弓形虫和弓形虫。两种生物均耐受As(III)(72小时的浓度可分别抑制25%和15 mg As [III] / L的生长速率[IC50] 50%)。小球藻当浓度高达0.8 mg / L(72 h IC50为25 mg As [V] / L)时,在72 h内对As(V)的耐受性也不受影响。弓形菊对As(V)更为敏感(72小时IC50为0.25 mg As [V] / L)。生长培养基中磷酸盐的增加(0.15-1.5 mg PO4(3-)/ L)降低了毒性,即,弓形虫的72小时IC50值从0.25 mg As(V)/ L增加到4.5 mg As (V)/ L,而细胞外As和细胞内As降低,表明砷酸盐和磷酸盐之间为细胞摄取而竞争。两种微藻都将细胞中的As(V)还原为As(III),并进一步生物转化为甲基化物质(单甲基砷酸和二甲基砷酸)和磷酸砷核糖苷。少于0.01%的添加的As(V)被掺入藻类细胞,表明生物富集和随后的甲基化不是解毒的主要方式。当暴露于As(V)时,这两种物质都将As(V)还原为As(III)。但是,只有弧菌将As(III)排泄到溶液中。在两种物种中,细胞内砷的还原都可能与硫醇的氧化有关。砷毒性最可能是由于砷在细胞中的积累,当高砷浓度下排泄和/或甲基化砷的能力被淹没时。亚砷酸盐可能与细胞内硫醇(例如谷胱甘肽)结合,从而可能破坏还原型与氧化型谷胱甘肽的比例,从而抑制细胞分裂。

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