METHOD FOR TREATING WASTEWATER AND WASTEWATER SLUDGE USING A PERCARBOXYLIC ACID

Abstract

The present invention provides a method for treating wastewater or wastewater sludge, in which method percarboxylic acid is used as an odor controlling agent and/or corrosion controlling agent.

Claims

1. A method for treating wastewater and/or wastewater sludge, comprising using a treating chemical comprising percarboxylic acid as an odor controlling agent and/or corrosion controlling agent.

2. The method according to claim 1, wherein the percarboxylic acid is selected from the group consisting of performic acid, peracetic acid and a combination of thereof.

3. The method according to claim 1, wherein performic acid is used as the treating chemical.

4. The method according to claim 4, wherein an active concentration of the performic acid is at least 8%, at least 9%, at least 10%, or in a range of 8-14%, calculated as weight to volume.

5. The method according to claim 1, wherein the method comprising: obtaining a wastewater or wastewater sludge stream, and adding the treating chemical comprising percarboxylic acid to the wastewater or wastewater sludge stream.

6. The method according to claim 5, wherein the wastewater or the wastewater sludge stream is a stream in municipal wastewater collection or treatment application, municipal sludge collection or treatment application or industrial wastewater application.

7. The method according to claim 5, further comprising: measuring a concentration of dissolved sulfides in the wastewater or wastewater sludge stream prior to the addition of the treating chemical; and adjusting the addition of the treating chemical according to the information obtained about the concentration of the dissolved sulfides.

8. The method according to claim 7, wherein a concentration of dissolved sulfides in the wastewater or wastewater sludge stream is measured at a point, to which, the wastewater or wastewater sludge stream is flowed after the addition of the treating chemical.

9. The method according to claim 7, further comprising modifying a rate of the addition of the treating chemical to the wastewater or wastewater sludge stream based on the measurement of the concentration of dissolved sulfides.

10. The method according to 5, wherein the treating chemical is added continuously to the wastewater or wastewater sludge stream in at least one process location.

11. The method according to claim 5, wherein the treating chemical is added into the wastewater or wastewater sludge stream, so as to, bring the level of dissolved sulfides, in particular H.sub.2S, to a level of less than 5 ppm, less than 2 ppm, or less than 1 ppm in the wastewater stream.

12. Use of a treating chemical comprising percarboxylic acid, performic acid, peracetic acid or a combination thereof, in odor control of the wastewater or wastewater sludge.

13. The use of the treating chemical comprising percarboxylic acid, performic acid, peracetic acid or a combination thereof, in corrosion control of wastewater or wastewater sludge collection and treatment processes.

14. The use according to claim 12, wherein the treating chemical is performic acid.

15. The use according to claim 13, wherein an active concentration of the performic acid is at least 8%, at least 9%, at least 10%, or in a range of 8-14%, calculated as weight to volume.

Description

EXPERIMENTAL

EXAMPLE

Odor Control Laboratory Testing Utilizing

[0031] A sample from influent wastewater is grabbed at an influent channel of a municipal wastewater treatment plant. The samples are grabbed in a 1000 ml polypropylene bottle and filled completely to the top to prevent any volatilization of sulfide out of the sample.

[0032] A treating chemical formulation comprising performic acid (PFA) as an active odor controlling agent and all other reagents are prepared just prior to be used.

[0033] PFA 13.5% formulation is made of mixing stabilized formic acid with 50 weight-% hydrogen peroxide.

[0034] Separation of Soluble Sulfide From Insoluble Sulfide

[0035] The Standard Methods 4500-S.sup.2 for waters and wastewaters: Section B procedure is used to determine soluble sulfides with a DR2800 spectrophotometer for the Methylene Blue analysis. The procedure comprises the following steps: [0036] 1. In a 15 ml glass tube, place approximately 10 drops of 6N Sodium Hydroxide (NaOH). [0037] 2. Obtain 15 ml of sample from the middle of the water column in the sample bottle and place the pipetter in the glass tube and gently dispense the sample into the NaOH solution. [0038] 3. Add approximately 7 drops of Aluminum Chloride (AlCl.sub.3) into the glass tube ensuring that the tube is full to the top at this point. [0039] 4. Mix the tube 4 times by inverting and let stand until the flocculant settles out yielding a fairly clear supernatant at the top of the glass tube. [0040] 5. Analyze immediately using DR2800 spectrophotometer for the Methylene Blue analysis.

[0041] PFA Tests to Determine Soluble Sulfides

[0042] Multiple samples were taken as describe above. For the test, 3 sample bottles are taken and labelled accordingly to: Control, 5 ppm PFA, and 10 ppm PFA. These test concentrations are within a recommended range of 1-10 ppm PFA active concentration. Samples are taken from the test bottles to establish a time 0 sulfide concentration within the bottles. No PFA was added to the test bottle labelled as control. To the 5 ppm PFA test bottle, 37 ppm of 13.5% PFA is added to the bottle. To the 10 ppm PFA test bottle, 74 ppm of 13.5% PFA is added to the bottle. All the bottles are gently mixed over 5 min. After 5 min, a 15 ml sample from each test bottle is collected as described standard method from mid-water column and placed gently in glass tubes respectively labeled as described above to separate the soluble sulfides from insoluble sulfides. After 10 min, another 15 ml sample is collected from the test bottles as collected from mid-water column and placed gently in glass tubes respectively labeled as described above.

[0043] Results

[0044] Test results are presented in Table 1. Time 0 samples taken just prior to the addition of PFA chemical. The time 0 Samples were taken to set the baseline of soluble sulfide in the samples collected.

TABLE-US-00001 TABLE 1 An amount of soluble sulfides (ppm) in different treatment times of the samples and different dosage amounts of PFA. Treatment Time (min.) PFA (as active conc.) 0* 5 10 Control (0 ppm PFA) 6.44 7.66 8.88** 5 ppm PFA 6.44 2.66 2.03 10 ppm PFA 6.44 2.12 1.72

[0045] The increase in sulphide in the control could be a result of non-soluble sulfides being converted to soluble sulfides due to mixing and sampling.

[0046] As shown in the results, the addition of PFA reduces the soluble sulfides and so dissolved sulfides in wastewater treatment plant influent significantly with dosages from 5 ppm to 10 ppm. At 2 ppm or less, sulfide is below the nuisance level. Therefore, as PFA reduces the sulfide below the nuisance level, PFA may be used to control odor in wastewater and wastewater sludge. The 5 minutes and 10 minutes residence times are evaluated for this study as the PFA chemistry is very effective at short times, and the time required to neutralize sulfide would occur very quickly. The results of this study demonstrate that greater than 90% reduction of the soluble sulfide concentration occurred within 5 minutes as compared to the untreated control which demonstrated no loss of soluble sulfide over the 5 minutes residence time or the 10 minutes residence time. This study also demonstrates that PFA is capable of removing soluble sulfide from wastewaters with suspended solids proved to reduce soluble sulfides further in contrast to the control with increased sulfide generation.