Apparatus and methods for control of waste treatment processes
원문보기
IPC분류정보
국가/구분
United States(US) Patent
등록
국제특허분류(IPC7판)
C02F-003/30
C02F-003/00
C02F-003/34
C02F-003/28
C02F-003/12
출원번호
US-0907588
(2013-05-31)
등록번호
US-8845900
(2014-09-30)
발명자
/ 주소
Miklos, Daniel R.
출원인 / 주소
Evoqua Water Technologies LLC
인용정보
피인용 횟수 :
1인용 특허 :
59
초록▼
Waste-treatment processes are enhanced through generation and introduction of specific biological populations customized to perform or favor specific tasks either during the main process, for the formation or precipitation of certain biological nutrients, or to accomplish solids formation reduction
Waste-treatment processes are enhanced through generation and introduction of specific biological populations customized to perform or favor specific tasks either during the main process, for the formation or precipitation of certain biological nutrients, or to accomplish solids formation reduction in a post-treatment process. These bacteria may be grown from specialized mixes of activated sludge and waste influent by exposing these materials to controlled environments (e.g., in an off-line treatment area). They may then be returned to the main process to perform certain tasks such as converting particulate cBOD into soluble cBOD for utilization, to reduce high solids yield organisms by supplementing the population characteristics with low yield organism characteristics, to provide biological nutrients or oxygenation assistance, to improve nitrification/denitrification efficiency, or to disfavor filamentous biology such as Norcardia sp.
대표청구항▼
1. A method of treating wastewater, comprising: conducting wastewater to an on-line treatment vessel;maintaining the on-line treatment vessel under aerobic conditions;combining the wastewater with a first biological population having a first biological population profile in the on-line treatment ves
1. A method of treating wastewater, comprising: conducting wastewater to an on-line treatment vessel;maintaining the on-line treatment vessel under aerobic conditions;combining the wastewater with a first biological population having a first biological population profile in the on-line treatment vessel to produce a mixed liquor including activated sludge;separating the activated sludge from the mixed liquor;drawing off a first portion of the separated activated sludge and returning said first portion to the on-line treatment vessel;drawing off a second portion of the separated activated sludge and introducing the second portion to an off-line treatment tank;controlling the off-line treatment tank so as to produce, in the off-line treatment tank, a second biological population having a second biological population profile that is different from the first biological population profile; andreturning at least a fraction of the produced second biological population to the on-line treatment vessel. 2. The method of claim 1, wherein the produced second biological population profile includes a lower proportion of filamentous biology than the first biological population profile. 3. The method of claim 1, wherein the produced second biological population achieves lower solids levels in the on-line treatment vessel relative to the first biological population. 4. The method of claim 1, wherein controlling the off-line treatment tank involves controlling an ORP level in the off-line treatment tank. 5. The method of claim 4, wherein controlling an ORP level of the off-line treatment tank comprises a step of aerating until the ORP level is greater than 100 mV. 6. The method of claim 5, wherein controlling an ORP level of the off-line treatment tank comprises a step of aerating until the ORP level is greater than 150 mV. 7. The method of claim 6, wherein controlling an ORP level of the off-line treatment tank comprises a step of aerating until the ORP level is greater than 200 mV. 8. The method of claim 4, wherein controlling the ORP level includes sequentially subjecting the off-line treatment tank to one of aerobic conditions, anoxic conditions and anaerobic conditions followed by subjecting the off-line treatment tank to at least one of aerobic conditions, anoxic conditions and anaerobic conditions. 9. The method of claim 1, wherein the second biological population profile is customized to minimize the disposal volume of residual solids produced by the treatment of the wastewater. 10. The method of claim 1, wherein the off-line treatment tank is controlled to produce the second biological population in a first mode of operation, the method further comprising controlling the off-line treatment tank to minimize a disposal volume of residual solids produced by the treatment of the wastewater in a second mode of operation. 11. The method of claim 10, wherein a proportional frequency of operating in the first mode and the second mode is determined based on an amount of non-degradable content in the wastewater to be treated. 12. The method of claim 1, wherein the second biological population profile is customized using a sequencing of growth conditions including controlled mixing, air exposure, residence time and settling sequences. 13. The method of claim 12, wherein the second biological population profile is customized based on peak demand requirements of the treatment vessel. 14. The method of claim 1, wherein the second biological population profile includes a higher proportion of facultative aerobes, facultative anaerobes or nitrifiers than the first biological population profile. 15. The method of claim 1, wherein the returned fraction of the produced second biological population contains a higher level of soluble cBOD, nitrate or biological nutrients than the wastewater. 16. The method of claim 1, further comprising subjecting the wastewater to a coarse removal process prior to conducting the wastewater to the on-line treatment vessel. 17. The method of claim 16, wherein the coarse removal process involves screening or degritting the wastewater. 18. A method of treating wastewater, comprising: conducting wastewater to a treatment vessel;combining the wastewater with a first biological population having a first biological population profile in the treatment vessel to produce a mixed liquor including activated sludge;separating the activated sludge from the mixed liquor;drawing off a first portion of the separated activated sludge and returning the first drawn-off portion to the treatment vessel;drawing off a second portion of the separated activated sludge and introducing the second drawn-off portion to an off-line treatment tank comprising a unitary uncompartmented tank;controlling the off-line treatment tank so as to produce, in the off-line treatment tank, a second biological population having a second biological population profile that is different from the first biological population profile, wherein during the controlling step, there is no flow from the off-line treatment tank to the treatment vessel, and wherein the controlling step comprises subjecting the contents of the unitary uncompartmented tank to a temporal sequence of one of aerobic conditions, anoxic conditions and anaerobic conditions followed by at least one of aerobic conditions, anoxic conditions and anaerobic conditions; andreturning a fraction of the produced second biological population to the treatment vessel. 19. The method of claim 18, wherein controlling the off-line treatment tank further comprises: i. mixing the second drawn-off portion without aeration to achieve anaerobic conditions without substantial sulfide generation;ii. mixing with aeration to achieve biological growth conditions without substantial production of obligate aerobes; andiii. mixing without aeration to achieve anaerobic conditions. 20. The method of claim 18, wherein controlling the off-line treatment tank further comprises: i. mixing the second drawn-off portion without aeration to achieve anaerobic conditions without substantial sulfide generation;ii. mixing with aeration to achieve biological growth conditions without substantial production of obligate aerobes;iii. mixing without aeration to achieve anaerobic conditions;iv. allowing settling to produce a decantable volume; andv. mixing with aeration to achieve biological growth conditions without substantial production of obligate aerobes. 21. The method of claim 18, wherein controlling the off-line treatment tank further comprises: i. mixing the second drawn-off portion without aeration to achieve anaerobic conditions without substantial sulfide generation;ii. stopping the mixing for a period of time;iii. mixing; andiv. mixing with aeration to achieve biological growth conditions without substantial production of obligate aerobes. 22. The method of claim 18, wherein controlling the off-line treatment tank further comprises: i. mixing the second drawn-off portion without aeration to achieve anaerobic conditions without substantial sulfide generation;ii. mixing with aeration to achieve biological growth conditions without substantial production of obligate aerobes; andiii. stopping the aeration but continuing the mixing. 23. The method of claim 18, wherein controlling the off-line treatment tank further comprises: i. mixing the second drawn-off portion without aeration to achieve anaerobic conditions without substantial sulfide generation;ii. mixing with aeration to achieve biological growth conditions without substantial production of obligate aerobes;iii. stopping the aeration but continuing the mixing;iv. allowing settling; andv. mixing with aeration to achieve biological growth conditions without substantial production of obligate aerobes. 24. The method of claim 18, wherein controlling the off-line treatment tank involves maintaining a target specific nitrate uptake rate range or a target specific oxygen uptake rate range. 25. The method of claim 18, wherein the returned fraction of the produced second biological population contains a higher level of soluble cBOD, nitrate or biological nutrients than the wastewater. 26. The method of claim 18, wherein controlling the off-line treatment tank further comprises subjecting the contents of the unitary uncompartmented tank to an ORP level that is greater than 100 mV immediately prior to returning the fraction of the produced second biological population to the treatment vessel.
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