Institute for Comparative and Environmental Toxicology and Laboratory of Soil Microbiology, Department of Soil, Crop, and Atmospheric Sciences, Cornell University, Ithaca, New York 14853.
Appl Environ Microbiol. 1991 May;57(5):1441-7. doi: 10.1128/aem.57.5.1441-1447.1991.
An Arthrobacter strain mineralized naphthalene and n-hexadecane dissolved in 2,2,4,4,6,8,8-heptamethylnonane. The extent of mineralization increased with greater volumes of solvent. Measurements under aseptic conditions of the partitioning of naphthalene into the aqueous phase from the solid phase or from heptamethylnonane showed that the rates were rapid and did not limit mineralization. The rate of mineralization of hexadecane was rapid, although partitioning of the compound into aqueous solution was not detected. The Arthrobacter sp. grown in media with or without heptamethylnonane did not excrete products that increased the aqueous solubility of naphthalene and hexadecane. Measurements of the number of cells in the aqueous phase showed that the Arthrobacter sp. attached to the heptamethylnonane-water interface, but attachment was evident even without a substrate in the heptamethylnonane. Tests with small inocula of the Arthrobacter sp. demonstrated that at least a portion of naphthalene or hexadecane dissolved in heptamethylnonane was degraded by cells attached to the solvent-water interface. The cells did not adhere in the presence of 0.1% Triton X-100. The surfactant prevented mineralization of the hexadecane initially dissolved in heptamethylnonane, but it increased the rate and extent of mineralization of naphthalene initially dissolved in heptamethylnonane. The data show that organic solvents into which hydrophobic compounds partition affect the biodegradation of those compounds and that attachment of microorganisms to the organic solvent-water interface may be important in the transformation.
一株节杆菌能够矿化溶解在 2,2,4,4,6,8,8-七甲基壬烷中的萘和正十六烷。随着溶剂体积的增加,矿化程度也随之增加。在无菌条件下测量萘从固相或从七甲基壬烷分配到水相的情况表明,这一过程非常迅速,不会限制矿化的进行。正十六烷的矿化速度很快,尽管未检测到该化合物分配到水溶液中。在含有或不含有七甲基壬烷的培养基中生长的节杆菌不会分泌出增加萘和正十六烷在水中溶解度的产物。在水相中的细胞数量测量表明,节杆菌附着在七甲基壬烷-水界面上,即使在七甲基壬烷中没有基质存在,也能明显附着。用少量接种物进行的节杆菌试验表明,至少一部分溶解在七甲基壬烷中的萘或正十六烷被附着在溶剂-水界面上的细胞降解。在存在 0.1% Triton X-100 的情况下,细胞不会附着。表面活性剂最初阻止了溶解在七甲基壬烷中的正十六烷的矿化,但它增加了最初溶解在七甲基壬烷中的萘的矿化速度和程度。这些数据表明,疏水化合物分配到的有机溶剂会影响这些化合物的生物降解,微生物附着在有机溶剂-水界面上可能是转化的重要因素。