As a by-product of oil sludge pyrolysis, the stock of pyrolysis residue is increasing, which seriously threatens the ecological environment. Given that the composition of the pyrolysis residue of oily sludge was similar to that of clay minerals, in this study, pyrolysis residue was used to prepare water-permeating bricks instead of clay. The effects of pyrolysis residue addition amount, water amount and extrusion stress on the compressive strength and permeability of the prepared water-permeating bricks were investigated, and the concentration of heavy metals and polycyclic aromatic hydrocarbons (PAHs) in the leaching solution of permeated brick were also studied. The results show that the addition amount of pyrolysis residue, water amount and extrusion stress have significant impact on the compressive strength and permeability of the permeable brick. When the addition amount of pyrolysis residue is 15%, the amount of water is 13% and the extrusion stress is 30MPa, the physical properties of the permeable brick are the best. At this point, the compressive strength is 32.20MPa, reaching the Cc30 standard, and the permeable coefficient is 1.80×10-2cm/s, which is higher than 1.00×10-2cm/s specified in WaterPermeableBrick (JC/T 945—2005). The leaching experiment results of heavy metals and PAHs show that the metals detected in the leaching solution of water permeated brick include Cr, Pb, Cu, Ni and Zn. The concentrations of Cr, Cu and Zn are lower than the Class Ⅱ standard limits stipulated in the EnvironmentalQualityStandardforSurfaceWater (GB 3838—2002) and the class Ⅲ standard limits stipulated in the QualityStandardforGroundwater (GB/T 14848—2017). The amount of residue added, the amount of water added and the extrusion stress have significant impacts on Ni in the leaching solution, but have little influence on Cr. The main PAHs detected in the leachate of permeated brick include naphthalene, acenaphthene, dihydroacenaphthene, fluorene and phenanthrene. The total concentration is in the range of 218.43—408.34μg/L. Acenaphthene is the main component in the leaching solution, and its relative mass distribution ratio is 59.80%—77.55%. This study can provide scientific basis for harmless treatment and resource utilization of oily sludge pyrolysis residue.