Herein, we investigated in detail the relationship between surface properties and extraction performance of virgin and amino-functionalized MIL-101s(Fe) for the extraction of 10 bisphenols (BPs) and their derivatives. These BPs were used as model contaminants due to their different hydroxyl groups and contrasting polarities. The differential sorption efficiencies for relatively polar BPs (BPF, BPE, BPA, BPB, BPZ, BPAP and BPP) lies in the formation of hydrogen-bonding between eOH of target analytes and eNH 2 of two MIL-101s(Fe). However, the surface properties of MIL-101(Fe) and NH 2 -MIL-101s(Fe), such as S BET and pore structure, determined the extraction recoveries for BPs derivatives (BADGE, BADGE•2H 2 O and BFDGE•2H 2 O) due to lack of eOH in their molecular structures. NH 2 -MIL-101s(Fe) nanosorbent was successfully applied to the preconcentration/extraction of trace BPs and their derivatives by dispersive solid-phase extraction (DSPE) method. Following optimization of the main factors, recoveries for BPs ranged from 90.8 to 117.8% and their LODs were 0.016-0.131 μg L −1 in environmental waters. Experimental precisions based on relative standard deviations were 0.9-4.9% for intra-day and 1.3-7.6% for inter-day analyses, respectively. These findings provide important information on how to design and modify nanosorbents for highly efficient extraction of pollutants having contrasting polarities. Moreover, the newly developed NH 2 -MIL-101s(Fe)-based DSPE method has a good application prospect in pretreatment of trace pollutants in real-world waters. toxicity than BPA [2][3][4]. The occurrence and distribution of BPA in various environmental matrices and human samples, such as air, surface water, waste water, sewage sludge, aquatic sediments, house dust, foodstuffs, urine, blood, and human breast milk, have been widely documented in the scientific literature [5][6][7]. Additionally, bisphenol analogues and derivatives in personal care products (PCPs), foodstuffs and a variety of environmental matrices, including indoor dust, sediments, fresh and sea waters, sewage effluent and sludge, have been extensively documented [8]. For example, BPF was the most abundant bisphenol analogue in surface waters from sites in Japan, Korea, and China, contributing > 70% of total BP concentrations [9]. This may reflect high usage of BPF as a BPA replacement in southeastern Asia. Similarly, BPF was found as the second most abundant BP analogue in a