Method for preparing polyferric chloride flocculant by using steel wire rope sludge and waste hydrochloric acid
A technology for polymerizing ferric chloride and waste hydrochloric acid, which is applied in the fields of ferric halide, flocculation/sedimentation water/sewage treatment, etc., and can solve the problems of innocuous treatment and resource utilization of steel wire rope pickling sludge and waste hydrochloric acid, etc. To achieve the effect of excellent purification performance
- Summary
- Abstract
- Description
- Claims
- Application Information
AI Technical Summary
Problems solved by technology
Method used
Image
Examples
Embodiment 1
[0028] see figure 1, put 2000L waste hydrochloric acid (the mass concentration of hydrochloric acid is 13%, the mass concentration of lead ion is 1620 ppm, the mass concentration of iron ion is 9.7%) into the extraction reaction tank 2, add 1000kg of wire rope pickling sludge (moisture content 76.8 %, the mass concentration of iron ions is 10.8%, the mass concentration of lead ions is 2000 ppm) 1, stirred and reacted for 30 minutes, after the plate and frame filter press 3 removes the sludge residue 4, the filtrate enters the lead removal reaction tank 5, Gradually add 260 L of sodium sulfide solution 6 with a mass concentration of 17%, continue to stir and react for 30 minutes after the dropwise addition, discharge to the static precipitation tank 7, and leave it for 2 hours, then pump the supernatant into ferric chloride The solution storage tank 8 and the bottom sludge 9 of the sedimentation tank are filtered by a plate and frame filter press 10 to obtain a lead sulfide mud...
Embodiment 2
[0032] see figure 1 , put 2000L waste hydrochloric acid (the mass concentration of hydrochloric acid is 5%, the mass concentration of lead ion is 320ppm, the mass concentration of iron ion is 9%) into the extraction reaction tank 2, add 1000kg steel wire rope pickling sludge (moisture content 80% , the mass concentration of iron ions is 11.5%, and the mass concentration of lead ions is 2300 ppm) 1, stirred and reacted for 50 minutes, after the plate and frame filter press 3 removes the sludge residue 4, the filtrate enters the deleading reaction tank 5, gradually Add dropwise 230 L of potassium sulfide solution 6 with a mass concentration of 10%, continue to stir and react for 45 minutes after the dropwise addition, discharge the material to the static precipitation tank 7, and leave it for 3 hours, then pump the supernatant into the ferric chloride solution Storage tank 8 and sedimentation tank bottom sludge 9 are filtered by plate and frame filter press 10 to obtain lead sul...
Embodiment 3
[0035] Example 3: Example of use
[0036] The polyferric chloride flocculant prepared in Example 1 was used for domestic sewage treatment. at 1 m 3 Add 1.5 kg of polyferric chloride flocculant to the domestic sewage, stir for 5 minutes, let it settle for 30 minutes, and take samples to test the treatment effect of domestic sewage. Before treatment, domestic sewage turbidity 240.6 NTU, COD Cr 656.6 mg / L, ammonia nitrogen 30.9 mg / L, total phosphorus 3.6 mg / L, after treatment, turbidity decreased by 97%, COD Cr , ammonia nitrogen and total phosphorus removal rates were 79.5%, 81.2% and 81%.
PUM
Abstract
Description
Claims
Application Information
- R&D Engineer
- R&D Manager
- IP Professional
- Industry Leading Data Capabilities
- Powerful AI technology
- Patent DNA Extraction
Browse by: Latest US Patents, China's latest patents, Technical Efficacy Thesaurus, Application Domain, Technology Topic, Popular Technical Reports.
© 2024 PatSnap. All rights reserved.Legal|Privacy policy|Modern Slavery Act Transparency Statement|Sitemap|About US| Contact US: help@patsnap.com