†Laboratoire Interdisciplinaire des Environnements Continentaux (LIEC), CNRS, UMR7360, Vandoeuvre-lès-Nancy, F-54501, France.
‡Laboratoire Interdisciplinaire des Environnements Continentaux (LIEC), Université de Lorraine, UMR7360, Vandoeuvre-lès-Nancy, F-54501, France.
Environ Sci Technol. 2015 Jun 2;49(11):6625-36. doi: 10.1021/acs.est.5b00594. Epub 2015 May 20.
Metal toxicity toward microorganisms is usually evaluated by determining growth inhibition. To achieve a mechanistic interpretation of such toxic effects, the intricate coupling between cell growth kinetics and metal partitioning dynamics at the cell-solution interface over time must be considered on a quantitative level. A formalism is elaborated to evaluate cell-surface-bound, internalized, and extracellular metal fractions in the limit where metal uptake kinetics is controlled by internalization under noncomplexing medium conditions. Cell growth kinetics is tackled using the continuous logistic equation modified to include growth inhibition by metal accumulation to intracellular or cell surface sites. The theory further includes metal-proton competition for adsorption at cell-surface binding sites, as well as possible variation of cell size during exposure to metal ions. The formalism elucidates the dramatic impacts of initial cell concentration on metal bioavailability and toxicity over time, in agreement with reported algae bioassays. It further highlights that appropriate definition of toxicity endpoints requires careful inspection of the ratio between exposure time scale and time scale of metal depletion from bulk solution. The latter depends on metal internalization-excretion rate constants, microorganism growth, and the extent of metal adsorption on nonspecific, transporter, and growth inhibitory sites. As an application of the theory, Cd toxicity in the algae Pseudokirchneriella subcapitata is interpreted from constrained modeling of cell growth kinetics and of interfacial Cd-partitioning dynamics measured under various exposure conditions.
金属对微生物的毒性通常通过测定生长抑制来评估。为了从机制上解释这种毒性效应,必须在定量水平上考虑细胞生长动力学与细胞-溶液界面上金属分配动力学随时间的复杂耦合。本文详细阐述了一种形式主义方法,用于评估细胞表面结合、内化和细胞外金属分数,其前提是金属摄取动力学受非络合介质条件下内化控制。采用连续逻辑方程来处理细胞生长动力学,该方程经过修改,将金属积累对细胞内或细胞表面部位的生长抑制纳入其中。该理论进一步包括金属-质子在细胞表面结合位点上的竞争吸附,以及在暴露于金属离子期间细胞大小可能发生的变化。该形式主义阐明了初始细胞浓度对金属生物利用度和毒性随时间的显著影响,与已报道的藻类生物测定结果一致。它进一步强调,适当定义毒性终点需要仔细检查暴露时间尺度与从主体溶液中耗尽金属的时间尺度之间的比值。后者取决于金属的内化-排泄速率常数、微生物生长以及非特异性、转运体和生长抑制部位上金属的吸附程度。作为该理论的应用,从受约束的建模中解释了藻类 Pseudokirchneriella subcapitata 中的 Cd 毒性,该建模包括细胞生长动力学和在各种暴露条件下测量的界面 Cd 分配动力学。