supporting information (Fig. S3). T

supporting information (Fig. S3). Therefore, oil/waterseparation efficiency was investigated.To evaluate the oil/water separation efficiency ofC18-RS-g-PS, a mixture of chloroform/water containing heavy metal ions was poured into separationdevice including 0.5 g of C18-RS-g-PS (Fig. 11a).Because of the low surface tension, the oil is absorbedby C18-RS-g-PS at first, then penetrated and eventually collected in the collection flask (Fig. 11b). Novisible blue liquid was observed in the filtrate,indicating the efficient performance of C18-RS-g-PSfor the separation of chloroform /water mixture(Fig. 11c). After calculation, 11.54 g CHCl3 wascollected (Fig. 11d). The oil/water separationefficiency was 98.2% according to the formula wegive you before. As important criteria for practicalapplications, the recyclability and durability of theobtained superhydrophobic straw were also evaluated.After the oil/water separation experiment, the contaminated straw of C18-RS-g-PS was rinsed thoroughly by ethanol to remove the absorbed oil. Afterdried in an oven at 50 C for several hours, thesuperhydrophobicity of C18-RS-g-PS was easilyrestored (Fig. 11e). It is worth mentioning that forthe oils with lower density than water, the oil/waterseparation can also be realized (Fig. S4).As shown in Fig. 12a, the as-prepared C18-RS-gPS maintained good oil/water separation efficiency fordifferent oils. In view of environmental protection, thereusability is of great significance to meet practicalapplications (Chu et al. 2015). C18-RS-g-PS could berenewed easily by immersing the sample into theethanol solution and drying under air condition beforenext separation cycle. As shown in Fig. 12b, taking themixture of chloroform and water as an example, theC18-RS-g-PS still maintained a high separation efficiency of 98% even after 5 times of recyclingprocesses. Then the adsorption behaviors of residualheavy metal ions in the separated water was evaluatedin the second purification.

0/5000

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目标语言: -

结果 (简体中文) 1: [复制]

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支持信息（图S3）。因此，研究了油/水 分离效率。 为了评估 C18-RS-g-PS 的油/水分离效率，将含重金属离子的氯仿/水混合物倒入 包含0.5 g C18-RS-g-PS的分离装置中（图11a）。 由于表面张力低，油首先被 C18-RS-g-PS 吸收，然后渗透并最终收集在收集瓶中（图11b）。没有 在滤液中观察到可见的蓝色液体， 指示C18-RS-G-PS的高效的性能 为氯仿/水混合物的分离 （图11C）。计算后， 收集到11.54 g CHCl3 （图11d）。油/水分离 根据我们 之前给您的公式，效率为98.2％。作为实际 应用的重要标准， 还评估了所得超疏水性秸秆的可回收性和耐久性。 油/水分离实验后，用乙醇彻底清洗受污染的C18-RS-g-PS秸秆，以除去吸收的油。后 在在50℃烘箱中干燥数小时，所述 C18-RS-G-PS的超疏水性是很容易 恢复（图11E）。值得一提的是，对于 密度比水低的油， 也可以实现油/水分离（图S4）。 如图12a所示，所制备的C18-RS-gPS保持了良好的油/水分离效率。 不同的油。考虑到环境保护， 可重用性对于满足实际 应用具有重要意义（Chu等人，2015）。 通过将样品浸入 乙醇溶液中并 在下一个分离循环之前在空气条件下干燥，可以轻松更新C18-RS-g-PS 。如图12b所示，以 氯仿和水的混合物为例， 即使经过5次循环 处理，C18-RS-g-PS仍保持98％的高分离效率。然后在第二次纯化中 评估了分离水中残留的重金属离子的吸附行为 。

正在翻译中..

结果 (简体中文) 2:[复制]

复制成功！

supporting information (Fig. S3). Therefore, oil/water separation efficiency was investigated. To evaluate the oil/water separation efficiency of C18-RS-g-PS, a mixture of chloroform/water containing heavy metal ions was poured into separation device including 0.5 g of C18-RS-g-PS (Fig. 11a). Because of the low surface tension, the oil is absorbed by C18-RS-g-PS at first, then penetrated and eventually collected in the collection flask (Fig. 11b). No visible blue liquid was observed in the filtrate, indicating the efficient performance of C18-RS-g-PS for the separation of chloroform /water mixture (Fig. 11c). After calculation, 11.54 g CHCl3 was collected (Fig. 11d). The oil/water separation efficiency was 98.2% according to the formula we give you before. As important criteria for practical applications, the recyclability and durability of the obtained superhydrophobic straw were also evaluated. After the oil/water separation experiment, the contaminated straw of C18-RS-g-PS was rinsed thoroughly by ethanol to remove the absorbed oil. After dried in an oven at 50 C for several hours, the superhydrophobicity of C18-RS-g-PS was easily restored (Fig. 11e). It is worth mentioning that for the oils with lower density than water, the oil/water separation can also be realized (Fig. S4). As shown in Fig. 12a, the as-prepared C18-RS-gPS maintained good oil/water separation efficiency for different oils. In view of environmental protection, the reusability is of great significance to meet practical applications (Chu et al. 2015). C18-RS-g-PS could be renewed easily by immersing the sample into the ethanol solution and drying under air condition before next separation cycle. As shown in Fig. 12b, taking the mixture of chloroform and water as an example, the C18-RS-g-PS still maintained a high separation efficiency of 98% even after 5 times of recycling processes. Then the adsorption behaviors of residual heavy metal ions in the separated water was evaluated in the second purification.

正在翻译中..

结果 (简体中文) 3:[复制]

复制成功！

支持信息（图S3）。因此，油/水 考察了分离效率。 评价油水分离效率 将含有重金属离子的氯仿/水的混合物C18-RS-g-PS注入分离 装置包括0.5 g C18-RS-g-PS（图11a）。 由于表面张力低，油被吸收了 首先通过C18-RS-g-PS，然后穿透并最终收集在收集瓶中（图11b）。不 滤液中可见蓝色液体， 表明了C18-RS-g-PS的高效性能 用于氯仿/水混合物的分离 （图11c）。经计算，11.54 g CHCl3为 收集（图11d）。油水分离 按公式计算，效率为98.2% 先给你。作为实践的重要标准 应用，可回收性和耐用性 对获得的超疏水秸秆也进行了评价。 油水分离实验结束后，用乙醇彻底冲洗被污染的C18-RS-g-PS秸秆，去除吸附的油脂。之后 在50摄氏度的烤箱中干燥数小时 C18-RS-g-PS易产生超疏水性 恢复（图11e）。值得一提的是 密度比水低的油，油/水 也可以实现分离（图S4）。 如图12a所示，制备的C18-RS-gPS保持了良好的油水分离效率 不同的油。考虑到环境保护 可重用性对于满足实际应用具有重要意义 应用（Chu等人。2015年）。C18-RS-g-PS可能是 通过将样品浸入 乙醇溶液及空调干燥前 下一个分离周期。如图12b所示，取 以氯仿和水的混合物为例 C18-RS-g-PS经过5次循环后仍保持了98%的高分离效率 过程。然后分析了残余物的吸附行为 对分离水中的重金属离子进行了评价 在第二次净化中。

正在翻译中..

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