Institute for Microbial and Biochemical Technology, Forest Products Laboratory, Forest Service, U.S. Department of Agriculture, One Gifford Pinchot Drive, Madison, Wisconsin 53705-2398.
Appl Environ Microbiol. 1990 Nov;56(11):3519-26. doi: 10.1128/aem.56.11.3519-3526.1990.
This research measured mycelial extension rates of selected strains of Phanerochaete chrysorhiza, Phanerochaete laevis, Phanerochaete sanguinea, Phanerochaete filamentosa, Phanerochaete sordida, Inonotus circinatus, and Phanerochaete chrysosporium and the ability of these organisms to tolerate and degrade the wood preservative pentachlorophenol (PCP) in an aqueous medium and in soil. Most of the tested species had mycelial extension rates in the range of </=0.5 to 1.5 cm day, but there were large interspecific differences. A notable exception, P. sordida, grew very rapidly, with an average mycelial extension rate of 2.68 cm day at 28 degrees C. Rank of species by growth rate was as follows: P. chrysosporium > P. sordida > P. laevis > P. chrysorhiza = P. sanguinea > I. circinatus = P. filamentosa. There were also significant intraspecific differences in mycelial extension rates. For example, mycelial extension rates among strains of P. sordida ranged from 1.78 to 4.81 cm day. Phanerochaete spp. were very sensitive to PCP. Growth of several species was prevented by the presence of 5 ppm (5 mug/g) PCP. However, P. chrysosporium and P. sordida grew at 25 ppm PCP, albeit at greatly decreased mycelial extension rates. In an aqueous medium, mineralization of PCP by P. sordida 13 (ca. 12% after 30 days) was significantly greater than that by all other tested P. sordida strains and P. chrysosporium. After 64 days, the level of PCP had decreased by 96 and 82% in soil inoculated with P. chrysosporium and P. sordida, respectively. Depletion of PCP by these fungi occurred in a two-stage process. The first stage was characterized by a rapid depletion of PCP that coincided with an accumulation of pentachloroanisole (PCA). At the end of the first stage, ca. 64 and 71% of the PCP was converted to PCA in P. chrysosporium and P. sordida cultures, respectively. In the second stage, levels of PCP and PCA were reduced by 9.6 and 18%, respectively, in soil inoculated with P. chrysosporium and by 3 and 23%, respectively, in soil inoculated with P. sordida. PCA was mineralized by both P. chrysosporium and P. sordida in an aqueous medium.
这项研究测定了选定的糙皮侧耳(Phanerochaete chrysorhiza)、白腐菌(Phanerochaete laevis)、血红密孔菌(Phanerochaete sanguinea)、绒盖牛肝菌(Phanerochaete filamentosa)、硫色多孔菌(Phanerochaete sordida)、鲍氏层孔菌(Inonotus circinatus)和黄孢原毛平革菌(Phanerochaete chrysosporium)的菌丝生长速度,并研究了这些生物在水介质和土壤中耐受和降解木材防腐剂五氯苯酚(PCP)的能力。大多数测试的物种的菌丝生长速度范围在</=0.5 至 1.5 厘米/天,但存在很大的种间差异。一个显著的例外是硫色多孔菌,其生长速度非常快,在 28°C 时的平均菌丝生长速度为 2.68 厘米/天。按生长速度排列的物种顺序如下:黄孢原毛平革菌>硫色多孔菌>白腐菌>糙皮侧耳=血红密孔菌>鲍氏层孔菌=绒盖牛肝菌。在菌丝生长速度方面,种内也存在显著差异。例如,硫色多孔菌菌株之间的菌丝生长速度范围为 1.78 至 4.81 厘米/天。糙皮侧耳属对 PCP 非常敏感。几种物种的生长被 5ppm(5 微克/克)PCP 所阻止。然而,黄孢原毛平革菌和硫色多孔菌在 25ppm PCP 下生长,尽管菌丝生长速度大大降低。在水介质中,硫色多孔菌 13 号菌(30 天后约 12%)对 PCP 的矿化作用明显大于其他所有测试的硫色多孔菌菌株和黄孢原毛平革菌。64 天后,分别用黄孢原毛平革菌和硫色多孔菌接种的土壤中 PCP 的水平下降了 96%和 82%。这些真菌对 PCP 的消耗是一个分两个阶段的过程。第一阶段是 PCP 的快速消耗,与五氯苯甲醚(PCA)的积累同时发生。在第一阶段结束时,黄孢原毛平革菌和硫色多孔菌培养物中分别约有 64%和 71%的 PCP 转化为 PCA。在第二阶段,用黄孢原毛平革菌接种的土壤中 PCP 和 PCA 的水平分别降低了 9.6%和 18%,用硫色多孔菌接种的土壤中分别降低了 3%和 23%。PCA 在水介质中被黄孢原毛平革菌和硫色多孔菌都矿化了。