Disposal of heavy metals contaminated biomass obtained from phytoremediation or biosorption by environmentally benign methods is a big challenge. In this study, we proposed a win-win strategy to recycle the Ag contaminated biomass by fast pyrolysis to obtain renewable bio-oil and catalytic reduction of Cr(VI) with the Ag-embedded biochar. We herein focused on the one-pot preparation of Ag nanoparticles embedded biochar hybrid material (Ag@biochar) by fast pyrolysis of the Ag preloaded biomass and their catalytic effect on Cr(VI) reduction. The results show that Ag@biochar can totally catalytic reduce the Cr(VI) in aqueous solution within 20 min using formic acid as a reducing agent at 323 K. The particle size of AgNPs on biochar was found as pyrolysis-temperature dependent and played an important role in the reduction of Cr(VI). We found the reduction of Cr(VI) catalyzed by Ag@biochar follows a CO (produced from HCOOH decomposition) reduction mechanism which is quite different from H2 reduction mechanism with the catalysis of some noble metal based catalysts (e.g., Pd and Pt). This study offered a sustainable approach for simultaneous disposal of the biomass waste and synthesis of functional materials, and might be expanded in the recycle of other metals contaminated biomass (e.g., Cu, Ni, Co, Zn, and Fe).The catalytic activity of the Ag@biochar was evaluated in the catalytic reduction of Cr(VI) with HCOOH, which was monitored by UV-vis spectroscopy. As shown in Fig. 5a, the intensity of the characteristic absorption peak of Cr(VI) at 353 nm decreases significantly with the increase of reaction time, suggesting that the Cr(VI) can be effectively converted by HCOOH with the catalysis of Ag@biochar. For comparison, the concentrations of Cr(VI) in two control experiments which employed only Ag@biochar or HCOOH (Fig. 5b), suggesting that the reduction of Cr(VI) cannot proceed without catalyst or HCOOH. When the raw biochar without Ag NPs was used for catalyst (Fig. 5b), the concentration of Cr(VI) only slightly decreased within 20 min, indicating that the activity of the Ag@biochar in the reduction of the Cr(VI) was mainly related to the excellent catalytic properties of the Ag NPs.The catalytic activity of the Ag@biochar is related to the particle size of Ag NPs, which is influenced by the pyrolysis temperature. Fig. 5c shows the Cr(VI) reduction with the catalysis of Ag@biochar formed in different temperatures. It can be seen that the catalytic activities of Ag@biochar-500 (average Ag particle size 7.6 nm) and Ag@biochar-600 (average Ag particle size 7.1 nm) are very similar, and both of them are much higher than that of Ag@biochar-400 (average Ag particle size 9.7 nm), suggesting that small Ag particles is favorable for catalyzing the Cr(VI) reduction with HCOOH. It can be explained as follows: firstly, there are more active sites in the Ag NPs with smaller size under the same conditions, offering more catalytic sites for the reactions; secondly, smaller particles may present a higher proportion of