Perczyk Paulina, Młyńczak Maja, Wydro Paweł, Broniatowski Marcin
Department of Environmental Chemistry, Faculty of Chemistry, Jagiellonian University in Kraków, Gronostajowa 2, 30-387 Kraków, Poland.
Department of Physical Chemistry and Electrochemistry, Faculty of Chemistry, Jagiellonian University in Kraków, Gronostajowa 2, 30-387 Kraków, Poland.
Biochim Biophys Acta Biomembr. 2022 Nov 1;1864(11):184018. doi: 10.1016/j.bbamem.2022.184018. Epub 2022 Aug 1.
Soils are the final sink for multiple organic pollutants emitted to the environment. Some of these chemicals which are toxic, recalcitrant and can bioaccumulate in living organism and biomagnify in trophic chains are classified persistent organic pollutants (POP). Vast areas of arable land have been polluted by POPs and the only economically possible means of decontamination is bioremediation, that is the utilization of POP-degrading microbes. Especially useful can be non-ligninolytic fungi, as their fast-growing mycelia can reach POP molecules strongly bond to soil minerals or humus fraction inaccessible to bacteria. The mobilized POP molecules are incorporated into the fungal plasma membrane where their degradation begins. The presence of POP molecules in the membranes can change their physical properties and trigger toxic effects to the cell. To avoid these phenomena fungi can quickly remodel the phospholipid composition of their membrane with employing different phospholipases and acyltransferases. However, if the presence of POP downregulates the phospholipases, toxic effects and the final death of microbial cells are highly probable. In our studies we applied multicomponent Langmuir monolayers with their composition mimicking fungal plasma membranes and studied their interactions with two different microbial phospholipases: phospholipase C (α-toxin) and phospholipase A1 (Lecitase ultra). The model membranes were doped with selected POPs that are frequently found in contaminated soils. It turned out that most of the employed POPs do not downregulate considerably the activity of phospholipases, which is a good prognostics for the application of non-ligninolytic fungi in bioremediation.
土壤是排放到环境中的多种有机污染物的最终归宿。其中一些化学物质具有毒性、难降解,可在生物体中生物累积并在营养链中生物放大,被归类为持久性有机污染物(POPs)。大面积耕地已被POPs污染,唯一经济可行的净化方法是生物修复,即利用降解POPs的微生物。非木质素分解真菌可能特别有用,因为它们快速生长的菌丝体能够接触到与土壤矿物质或细菌无法触及的腐殖质部分紧密结合的POP分子。被 mobilized 的POP分子被纳入真菌质膜,在那里开始降解。质膜中POP分子的存在会改变其物理性质并引发对细胞的毒性作用。为避免这些现象,真菌可通过使用不同的磷脂酶和酰基转移酶快速重塑其膜的磷脂组成。然而,如果POP的存在下调了磷脂酶的活性,微生物细胞很可能会产生毒性作用并最终死亡。在我们的研究中,我们应用了组成模拟真菌质膜的多组分朗缪尔单分子层,并研究了它们与两种不同的微生物磷脂酶:磷脂酶C(α-毒素)和磷脂酶A1(Lecitase ultra)的相互作用。模型膜中掺杂了在受污染土壤中经常发现的选定POPs。结果表明,大多数使用的POPs不会显著下调磷脂酶的活性,这对于非木质素分解真菌在生物修复中的应用是一个良好的预测指标。