{"title":"皂荚脂产酵母菌降解吸附蒽","authors":"M. Romero, Juan C. Chiaravalli, E. H. Reinoso","doi":"10.6000/1927-3037.2016.05.01.4","DOIUrl":null,"url":null,"abstract":"The organic pollutan adsorption/desorption process by microbial degradation had been less studied than metal ones. The sorption assays alone did not predict desorption, due to hysteresis, irreversibility, fixed compounds in different sites, with diverse desorption rates. Most of the studies dealt with bacteria rather than filamentous fungi and yeasts. So, our aims were to isolate yeasts from polluted sediments, to quantify its potential to uptake anthracene (An) and to evaluate the bioavailability by a desorption model. Yeasts were isolated from hydrocarbon-polluted samples, 40-isolates grew in anthracene-plates. Molecular characterization was achieved by sequence analysis of the ITS1-5.8S rRNA-ITS4 and 26S rRNA regions; morphological and physiological determination were also done. Candida parasilopsis , Pichia anomala and Rhodothorula mucilaginosa were the prevalent yeasts. An-degradation was assessed in soil-systems with 0, 50, 100, 150, 200 and 250 I¼g An/l, 3 differentes sorbens types, organic carbon, organic nitrogen, PAHs, sand:silt:clay, pH and cation exchange capacity. Sophorolipids excretion were confirmed by HPLC, UV-detector with active fraction at 9.669 min (RT 9.646 min = sophorolipid-standard). A desorption model with equilibrium, nonequilibrium and nondesorption areas, was applied to explain the experimental data, An-transformation was greater in the organic liquid-phase than in the soil-sorbed ones; the desorption-coefficients and soil components were negatively correlated with the kinetic parameters. The An-release depended on the sophorolipid excretion, soil matrix and particles sizes. Desorption parameters significantly fitted the yeast uptake, with R 2 = 0.97, R 2 = 0.90 and R 2 = 0.97 for C. parasilopsis , P. anomala and R. mucilaginosa, respectively.","PeriodicalId":90181,"journal":{"name":"International journal of biotechnology for wellness industries","volume":"5 1","pages":"25-31"},"PeriodicalIF":0.0000,"publicationDate":"2016-03-02","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"2","resultStr":"{\"title\":\"Sorbed Anthracene Degradation by Sophorolipid Producing Yeasts\",\"authors\":\"M. Romero, Juan C. Chiaravalli, E. H. Reinoso\",\"doi\":\"10.6000/1927-3037.2016.05.01.4\",\"DOIUrl\":null,\"url\":null,\"abstract\":\"The organic pollutan adsorption/desorption process by microbial degradation had been less studied than metal ones. The sorption assays alone did not predict desorption, due to hysteresis, irreversibility, fixed compounds in different sites, with diverse desorption rates. Most of the studies dealt with bacteria rather than filamentous fungi and yeasts. So, our aims were to isolate yeasts from polluted sediments, to quantify its potential to uptake anthracene (An) and to evaluate the bioavailability by a desorption model. Yeasts were isolated from hydrocarbon-polluted samples, 40-isolates grew in anthracene-plates. Molecular characterization was achieved by sequence analysis of the ITS1-5.8S rRNA-ITS4 and 26S rRNA regions; morphological and physiological determination were also done. Candida parasilopsis , Pichia anomala and Rhodothorula mucilaginosa were the prevalent yeasts. An-degradation was assessed in soil-systems with 0, 50, 100, 150, 200 and 250 I¼g An/l, 3 differentes sorbens types, organic carbon, organic nitrogen, PAHs, sand:silt:clay, pH and cation exchange capacity. Sophorolipids excretion were confirmed by HPLC, UV-detector with active fraction at 9.669 min (RT 9.646 min = sophorolipid-standard). A desorption model with equilibrium, nonequilibrium and nondesorption areas, was applied to explain the experimental data, An-transformation was greater in the organic liquid-phase than in the soil-sorbed ones; the desorption-coefficients and soil components were negatively correlated with the kinetic parameters. The An-release depended on the sophorolipid excretion, soil matrix and particles sizes. Desorption parameters significantly fitted the yeast uptake, with R 2 = 0.97, R 2 = 0.90 and R 2 = 0.97 for C. parasilopsis , P. anomala and R. mucilaginosa, respectively.\",\"PeriodicalId\":90181,\"journal\":{\"name\":\"International journal of biotechnology for wellness industries\",\"volume\":\"5 1\",\"pages\":\"25-31\"},\"PeriodicalIF\":0.0000,\"publicationDate\":\"2016-03-02\",\"publicationTypes\":\"Journal Article\",\"fieldsOfStudy\":null,\"isOpenAccess\":false,\"openAccessPdf\":\"\",\"citationCount\":\"2\",\"resultStr\":null,\"platform\":\"Semanticscholar\",\"paperid\":null,\"PeriodicalName\":\"International journal of biotechnology for wellness industries\",\"FirstCategoryId\":\"1085\",\"ListUrlMain\":\"https://doi.org/10.6000/1927-3037.2016.05.01.4\",\"RegionNum\":0,\"RegionCategory\":null,\"ArticlePicture\":[],\"TitleCN\":null,\"AbstractTextCN\":null,\"PMCID\":null,\"EPubDate\":\"\",\"PubModel\":\"\",\"JCR\":\"\",\"JCRName\":\"\",\"Score\":null,\"Total\":0}","platform":"Semanticscholar","paperid":null,"PeriodicalName":"International journal of biotechnology for wellness industries","FirstCategoryId":"1085","ListUrlMain":"https://doi.org/10.6000/1927-3037.2016.05.01.4","RegionNum":0,"RegionCategory":null,"ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"","JCRName":"","Score":null,"Total":0}
引用次数: 2
摘要
微生物降解对有机污染物的吸附/解吸过程的研究相对较少。由于滞后性、不可逆性、不同位置的固定化合物、不同的脱附速率,单独的吸附试验不能预测脱附。大多数研究涉及的是细菌,而不是丝状真菌和酵母。因此,我们的目标是从受污染的沉积物中分离酵母,量化其吸收蒽(An)的潜力,并通过解吸模型评估生物利用度。从烃类污染的样品中分离到酵母菌,在蒽培养皿中生长了40株。通过对ITS1-5.8S rRNA- its4和26S rRNA区域的序列分析实现分子鉴定;并进行了形态学和生理学的测定。寄生假丝酵母菌、异常毕赤酵母和黏液红梭菌是主要的酵母菌。在0、50、100、150、200和250 μ g An/l、3种土壤类型、有机碳、有机氮、多环芳烃、砂:粉土:粘土、pH和阳离子交换容量的土壤系统中,评价了氮的降解。采用高效液相色谱(HPLC)、紫外检测器(uv -检测器)测定苦参脂的排泄量,有效组分时间为9.669 min (RT = 9.646 min)。采用平衡区、非平衡区和非脱附区三种脱附区模型对实验数据进行了解释,结果表明:有机液相中的an转化大于土壤吸附液相;解吸系数和土壤组分与动力学参数呈负相关。其释放与槐脂排泄量、土壤基质和颗粒大小有关。对拟parasilopsis、P. anomala和R. mucilaginosa的解吸参数r2分别为0.97、0.90和0.97。
Sorbed Anthracene Degradation by Sophorolipid Producing Yeasts
The organic pollutan adsorption/desorption process by microbial degradation had been less studied than metal ones. The sorption assays alone did not predict desorption, due to hysteresis, irreversibility, fixed compounds in different sites, with diverse desorption rates. Most of the studies dealt with bacteria rather than filamentous fungi and yeasts. So, our aims were to isolate yeasts from polluted sediments, to quantify its potential to uptake anthracene (An) and to evaluate the bioavailability by a desorption model. Yeasts were isolated from hydrocarbon-polluted samples, 40-isolates grew in anthracene-plates. Molecular characterization was achieved by sequence analysis of the ITS1-5.8S rRNA-ITS4 and 26S rRNA regions; morphological and physiological determination were also done. Candida parasilopsis , Pichia anomala and Rhodothorula mucilaginosa were the prevalent yeasts. An-degradation was assessed in soil-systems with 0, 50, 100, 150, 200 and 250 I¼g An/l, 3 differentes sorbens types, organic carbon, organic nitrogen, PAHs, sand:silt:clay, pH and cation exchange capacity. Sophorolipids excretion were confirmed by HPLC, UV-detector with active fraction at 9.669 min (RT 9.646 min = sophorolipid-standard). A desorption model with equilibrium, nonequilibrium and nondesorption areas, was applied to explain the experimental data, An-transformation was greater in the organic liquid-phase than in the soil-sorbed ones; the desorption-coefficients and soil components were negatively correlated with the kinetic parameters. The An-release depended on the sophorolipid excretion, soil matrix and particles sizes. Desorption parameters significantly fitted the yeast uptake, with R 2 = 0.97, R 2 = 0.90 and R 2 = 0.97 for C. parasilopsis , P. anomala and R. mucilaginosa, respectively.