CAJ | 학술논문

为满足水生态系统重建及水体景观对沉水植物种苗的需求,本文建立了菹草(Potamogeton crispus L.)人工种子的制作方法,并分析了菹草人工种子的萌发条件.结果表明,以海藻酸钠为包埋剂,在包埋剂中添加IBA 1.0mg/L+6-BA 0.5 mg/L制备的菹草人工种子在灭菌自来水中萌发率可达80%,且转株率达20%.在15-25℃之间,温度对菹草人工种子萌发和转株的影响不显著;氮磷水平对菹草人工种子萌发和转株的影响不显著;光强对菹草人工种子的萌发和转株有显著影响,较高的光强有较高的萌发率和转株率,光强为40μmol/m2·s时,菹草人工种子萌发率、转株率可达67.8%、35.6%;底质对菹草人工种子的萌发和转株有显著影响,菹草人工种子在黄沙壤上的萌发率、转株率分别为60%和42.2%,黄沙壤比淤泥和砂石更适合菹草人工种子萌发和转株;菹草人工种子在野外湖水的试验中萌发率、转株率分别达到28%、15%.
위만족수생태계통중건급수체경관대침수식물충묘적수구,본문건립료저초(Potamogeton crispus L.)인공충자적제작방법,병분석료저초인공충자적맹발조건.결과표명,이해조산납위포매제,재포매제중첨가IBA 1.0mg/L+6-BA 0.5 mg/L제비적저초인공충자재멸균자래수중맹발솔가체80%,차전주솔체20%.재15-25℃지간,온도대저초인공충자맹발화전주적영향불현저;담린수평대저초인공충자맹발화전주적영향불현저;광강대저초인공충자적맹발화전주유현저영향,교고적광강유교고적맹발솔화전주솔,광강위40μmol/m2·s시,저초인공충자맹발솔、전주솔가체67.8%、35.6%;저질대저초인공충자적맹발화전주유현저영향,저초인공충자재황사양상적맹발솔、전주솔분별위60%화42.2%,황사양비어니화사석경괄합저초인공충자맹발화전주;저초인공충자재야외호수적시험중맹발솔、전주솔분별체도28%、15%.
Restoration of submerged vegetation is the key step of restoration of aquatic ecosystem in eutrophic lakes. The seed bank was strongly destroyed in many eutrophic lakes of China, it is necessary to get plenty of seedlings for restoration of submerged vegetation because of the difficulty of getting enough macrophyte seeds. Usually, seedlings of submerged macrophytes have to be obtained from other water bodies. Transplantation may destroy the source vegetation and encounter shortage of seedlings in case of lack of vegetation in nearby water bodies. The technique of artificial seeds is a promising method to provide a large number of seedlings in a short time without limitation of season, long distant transportation and harm to the natural macrophyte community.In order to establish the method for the preparation of artificial seeds of submerged macrophytes, a common submerged macrophte Potamogeton crispus L. was selected as experimental material. In this study, the artificial seed of P. crispus was obtained by using node segments as explant, buds were induced in induction medium. The node segments with buds of P. crispus were encapsulated with sodium alginate and calcium chloride to form artificial seeds. The effects of hormone types and concentration in capsule, temperature, light intensity, concentration of nitrogen and phosphorus, sediment types on the germination and conversion of artificial seeds of P. crispus were investigated. An experiment of germination and conversion of the artificial seeds in lake was also conducted. The hormones supplemented in the capsules could promote the germination of artificial seeds. The result showed that the germination and conversion rates of artificial seeds, which embedded in IBA 1.0 mg/L and 6-BA 0. 5 mg/L, were 80% and 20% respectively in autoclaved tap water. No significant effect of temperature was found on the germination and conversion in range of 15-25℃. Similarly nitrogen and phosphorus caused no significant change on the germination and conversion of artificial seeds of P. crispus. Light intensity affected the germination and conversion significantly. Higher light intensity favored the germination of artificial seeds. The germination and conversion rates of the artificial seeds reached to 67.8% and 35.6% respectively at light intensity of 40 μmol/m2· s. Sediment types also affected the germination significantly. Sandy soil was better than sandstone and silt to support the germination. The germination rate of artificial seeds of P. crispus was 60% on the sandy soil, which was higher than that in sandstone and silt sediments. To test the feasibility of artificial seeds of P. crispus in eutrophic lakes, a trial experiment was carried out in the East Lake which is a hyper-eutrophic lake in Wuhan, Huhei the germination and conversion rates of artificial seeds of P. crispus were 28% and 15% under water depth of 0.6 m, and 27% and 12% under water depth of 1.2 m, respectively. The results showed that the artificial seed of P. crispus was applicable in restoration of aquatic vegetation in place of plant transplantation.