Method for treating atrazine-containing pesticide wastewater
A technology for pesticide wastewater and treatment methods, which is applied in heating water/sewage treatment, adsorption water/sewage treatment, neutralized water/sewage treatment, etc., to achieve the effects of ensuring safety, saving sewage charges and solving difficult wastewater treatment.
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Embodiment 1
[0029] The water quality of pesticide wastewater is shown in Table 1.
[0030] Table 1 Analysis data of pesticide water quality
[0031]
pH
COD (mg / L)
(mmol / L)
Cl - (chlorination
thing)
(mg / kg)
total salt content
(mg / L)
(mg / L)
11~12
2260
24.75
5180
55400
15.23
[0032] The pH of the waste water is 11-12, neutralized with hydrochloric acid to pH 7-8, it can be seen that it is obviously turbid, and flocculent substances are slowly precipitated. Dosing polyaluminum chloride and polyacrylamide, the dosage is 50mg / L and 2mg / L respectively, the coagulation effect is remarkable, obvious large flocs appear within ten minutes after adding the coagulant, passing through 0.5~ 2.0mm zeolite filter material for filtration.
[0033]Water was filtered off and evaporated under reduced pressure. Results of vacuum...
Embodiment 2
[0035] Waste water quality condition is the same as embodiment 1. The waste water is directly evaporated under reduced pressure after being neutralized. Evaporation results under reduced pressure: COD before evaporation: 2207mg / L; COD of evaporated water: 49.1mg / L. Evaporation phenomenon: severe bumping phenomenon, entrainment phenomenon, and obvious white salt precipitation in the evaporation kettle. From the phenomenon of the evaporation process, for the pesticide wastewater with high concentration, there are bumping and entrainment phenomena in the direct evaporation after neutralization, which shows that the existence of suspended matter has an impact on the evaporation process. Atrazine content before distillation: 11.15mg / L; atrazine content in distilled water: 4.78mg / L.
Embodiment 3
[0037] Water evaporated in Example 2 was carried out for adsorption test, and the adsorption medium used granular activated carbon and columnar activated carbon respectively. The adsorption device adopts a glass column with an inner diameter of 50mm and a height of 200mm, and adopts the form of downward flow. Every 200mL, an adsorption effluent is taken, which are respectively recorded as adsorption 1, adsorption 2 and adsorption 3. The results are shown in Table 2.
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