Ectopic remediation method for groundwater polluted by chlorinated nitrobenzenes
A nitrobenzene-based, ectopic remediation technology, applied in the direction of reduced water/sewage treatment, oxidized water/sewage treatment, etc., can solve difficult problems and achieve high pollutant removal rate and obvious repair effect
Patent Information
- Authority / Receiving Office
- CN · China
- Patent Type
- Patents(China)
- Current Assignee / Owner
- Publication Date
- 2016-04-13
Abstract
Description
technical field
[0001] The invention belongs to the technical field of restoration and treatment of polluted groundwater, and relates to an ex-situ restoration method suitable for groundwater polluted by chlorinated nitrobenzenes. Background technique
[0002] Chloronitrotoluene compounds are widely used in national defense, printing and dyeing, plastics, pesticides and pharmaceutical industries. The annual discharge of chloronitrotoluene into the environment in the world exceeds 100 tons, causing great harm to the ecological environment. Many such The compound is listed as a priority pollutant by the U.S. Environmental Protection Agency, and it is of practical significance to strictly control the content of chloronitrotoluene in water. The benzene ring of chloronitrotoluene compounds has a dense electron cloud, and it is difficult to provide electrons. It is difficult to remove chloronitrobenzene compounds by oxidation. Moreover, the oxidation of chloronitrobenzene may pro...
Examples
Embodiment 1
[0018] The present invention is suitable for a small-scale test of an ex-situ remediation method for groundwater polluted by chlorinated nitrobenzenes
[0019] 1. Experimental method
[0020] 1. Experimental materials
[0021] The groundwater polluted by chloronitrotoluene compounds and petroleum hydrocarbons was collected from a site in Shengsi. The concentrations of 4-chloro-2-nitrotoluene and total petroleum hydrocarbons in sewage were 21 and 7.3 mg·L, respectively -1 , COD content is 3620mg·L -1 .
[0022] The reduced iron powder (Fe 0 ), hydrogen peroxide (H 2 o 2 ,30%), ferrous sulfate heptahydrate (FeSO 4 ·7H 2 O) and calcium hydroxide (Ca(OH) 2 ) are analytically pure.
[0023] 2. Experimental operation
[0024] The sewage was filtered with a 45nm microporous membrane before the experiment, and the initial pH was determined to be 3. Add 1g (30% of COD content) of Fe to 1L reaction solution 0 , after 5 days of reaction, add 1g FeSO 4 ·7H 2 O (30% of COD c...
Embodiment 2
[0034] 1. Experimental materials
[0035] Chloronitrotoluene compounds and petroleum hydrocarbons polluted groundwater from a site in Shanghai. The concentrations of 4-chloro-2-methylphenol and total petroleum hydrocarbons in sewage were 34 and 12 mg·L, respectively -1 , COD content is 3950mg·L -1 .
[0036] The reduced iron powder (Fe 0 ), hydrogen peroxide (H 2 o 2 ,30%), ferrous sulfate heptahydrate (FeSO 4 ·7H 2 O) and calcium hydroxide (Ca(OH) 2 ) are analytically pure.
[0037] 2. Experimental operation
[0038] The sewage was filtered with a 45nm microporous membrane before the experiment, and the initial pH was determined to be 3.2. Add 1.5g (40% of COD content) of Fe to 1L reaction solution 0 , after 3 days of reaction, add 1.2g FeSO 4 ·7H 2 O (30% of COD content), stir until miscible, and prepare 12g (10.5mL, 30%; 3 times of COD content) H 2 o 2 And gradually added to the reaction solution, the reaction time is more than 1 day, and the pH value of the ...
Embodiment 3
[0048] 1. Experimental materials
[0049] Chloronitrotoluene compounds and petroleum hydrocarbons polluted groundwater from a site in Shanghai. The concentrations of 5-chloro-2nitrobenzyl alcohol and total petroleum hydrocarbons in sewage were 26 and 10 mg·L, respectively -1 , COD content is 3790mg·L -1 .
[0050] The reduced iron powder (Fe 0 ), hydrogen peroxide (H 2 o 2 ,30%), ferrous sulfate heptahydrate (FeSO 4 ·7H 2 O) and calcium hydroxide (Ca(OH) 2 ) are analytically pure.
[0051] 2. Experimental operation
[0052] The sewage was filtered with a 45nm microporous membrane before the experiment, and the initial pH was determined to be 3.5. Add 1.3g (35% of COD content) of Fe to 1L reaction solution 0 , after 4 days of reaction, add 1.1g (30% of COD content) FeSO 4 ·7H 2 O, stir until miscible, configure 8g (7mL, 30%; 2 times the content of COD) H 2 o 2 and gradually added to the reaction solution, the reaction time is about 1 day, and the pH value of the ...