Mediterranean Institute of Oceanography, Equipe Microbiologie Environnementale et Biotechnologie, UM 110 CNRS/IRD Aix-Marseille Université, Université de Toulon, CS 60584, 83 041 Toulon Cedex 9, France.
Marbec, University of Montpellier, IRD, Ifremer, CNRS, 34 095 Montpellier Cedex 5, France.
Sci Total Environ. 2020 May 1;715:136834. doi: 10.1016/j.scitotenv.2020.136834. Epub 2020 Jan 25.
Over the past decades, the occurrence, distribution and intensity of harmful algal blooms involving the dinoflagellate Alexandrium pacificum have increased in marine coastal areas disturbed by anthropogenic inputs. This invasive species produces saxitoxin, which causes the paralytic shellfish poisoning syndrome in humans upon consumption of contaminated seafood. Blooms of A. pacificum have been reported in metal-contaminated coastal ecosystems, suggesting some ability of these microorganisms to adapt to and/or resist in metal stress conditions. This study seeks to characterize the modifications in membrane proteomes (by 2-D electrophoresis coupled to LC-MS/MS), cell growth and morphometry (measured with an inverted microscope), in response to metal stress (addition of Zn, Pb, Cu and Cd), in two Mediterranean A. pacificum strains: SG C10-3 and TAR C5-4F, respectively isolated from the Santa Giusta Lagoon (Sardinia, Italy) and from the Tarragona seaport (Spain), both metal-contaminated ecosystems. In the SG C10-3 cultures grown in a metal cocktail, cell growth was significantly delayed, and cell size increased (22% of 37.5 μm cells after 25 days of growth). Conversely, no substantial change was observed for cell growth or cell size in the TAR C5-4F cultures grown in a metal cocktail (P > 0.10), thus indicating intraspecific variability in the responses of A. pacificum strains to metal contamination. Regardless of the conditions tested, the total number of proteins constituting the membrane proteome was significantly higher for TAR C5-4F than for SG C10-3, which may help TAR C5-4F to thrive better in contaminated conditions. For both strains, the total number of proteins constituting the membrane proteomes was significantly lower in response to metal stress (29% decrease in the SG C10-3 proteome: 82 ± 12 proteins for controls, and 58 ± 12 in metal-contaminated cultures; 17% decrease in the TAR C5-4F proteome: 101 ± 8 proteins for controls, and 84 ± 5 in metal-contaminated cultures). Moreover, regardless of the strain, proteins with significantly modified expression in response to stress were mainly down-regulated (representing 45% of the proteome for SG C10-3 and 38% for TAR C5-4F), clearly showing the harmful effects of the metals. Protein down-regulation may affect cell transport (actin and phospholipid scramblase in SG C10-3), photosynthesis (RUBISCO in SG C10-3, light-harvesting protein in TAR C5-4F, and high-CO-inducing periplasmic protein in both strains), and finally energy metabolism (ATP synthase in both strains). However, other modifications in protein expression may confer to these A. pacificum strains a capacity for adaptation and/or resistance to metal stress conditions, for example by (i) limiting the metal entry through the plasma membrane of the SG C10-3 cells (via the down-regulation of scramblase) and/or (ii) reducing the oxidative stress generated by metals in SG C10-3 and TAR C5-4F cells (due to down-regulation of ATP-synthase).
在过去的几十年中,在受到人为输入干扰的海洋沿海地区,涉及甲藻属亚历山大藻的有害藻类大量繁殖的现象、分布和强度都有所增加。这种入侵物种会产生石房蛤毒素,人类食用受污染的海鲜后会导致麻痹性贝类中毒综合征。在金属污染的沿海生态系统中已经报道了亚历山大藻的大量繁殖,这表明这些微生物有一定的适应和/或抵抗金属胁迫的能力。本研究旨在通过二维电泳(与 LC-MS/MS 相结合)来描述细胞膜蛋白质组的变化,通过倒置显微镜来描述细胞生长和形态计量的变化,以响应金属胁迫(添加 Zn、Pb、Cu 和 Cd),在两个地中海亚历山大藻株中:SG C10-3 和 TAR C5-4F,分别从圣吉斯塔泻湖(意大利撒丁岛)和塔拉戈纳海港(西班牙)分离出来,这两个地方都是金属污染的生态系统。在金属鸡尾酒中生长的 SG C10-3 培养物中,细胞生长明显延迟,细胞大小增加(生长 25 天后,37.5 μm 的细胞大小增加 22%)。相反,在金属鸡尾酒中生长的 TAR C5-4F 培养物中,细胞生长或细胞大小没有明显变化(P > 0.10),这表明亚历山大藻株对金属污染的反应存在种内变异性。无论测试的条件如何,TAR C5-4F 构成膜蛋白质组的蛋白质总数明显高于 SG C10-3,这可能有助于 TAR C5-4F 在污染条件下更好地生长。对于两种菌株,响应金属胁迫时构成膜蛋白质组的蛋白质总数显著降低(SG C10-3 蛋白质组减少 29%:对照 82±12 个蛋白,受污染的培养物中 58±12 个蛋白;TAR C5-4F 蛋白质组减少 17%:对照 101±8 个蛋白,受污染的培养物中 84±5 个蛋白)。此外,无论菌株如何,响应胁迫而表达发生显著改变的蛋白质主要被下调(SG C10-3 占蛋白质组的 45%,TAR C5-4F 占 38%),这清楚地表明了金属的有害影响。蛋白质下调可能会影响细胞运输(SG C10-3 中的肌动蛋白和磷脂 scramblase)、光合作用(SG C10-3 中的 RuBisCO、TAR C5-4F 中的光捕获蛋白和两种菌株中的高 CO 诱导周质蛋白)以及最终的能量代谢(两种菌株中的 ATP 合酶)。然而,蛋白质表达的其他变化可能会使这些亚历山大藻菌株具有适应和/或抵抗金属胁迫的能力,例如通过(i)通过 SG C10-3 细胞的质膜限制金属的进入(通过 scramblase 的下调)和/或(ii)减少 SG C10-3 和 TAR C5-4F 细胞中金属产生的氧化应激(由于 ATP 合酶的下调)。