Biological treatment of wastewater

Claim 2

A continuous inflow, intermittent flow path, sequential cycle, activated sludge waste water process for treating wastewater, comprising the steps of: (a) continuously receiving wastewater into a first zone (A) into which activated sludge from a subsequent zone is mixed and retaining said wastewater in said first zone for a period of from at least approximately two to 20 minutes sufficient to form a non-bulking sludge and absorb biodegradable dissolved compounds into the activated sludge; (b) passing wastewater from the first zone (A) into a second zone (B) during at least a first aerating time period into which second zone oxygen is transferred into the wastewater, and passing wastewater into said second zone during a second quiescent time period during which settling of sludge is caused by maintaining a quiescent condition in said second zone; (c) passing wastewater from the second zone (B) into a third zone (C) during said first and second time periods, the wastewater passing into the third zone being characterized in that it has less than approximately twenty percent of the biochemical oxygen demand the wastewater originally contained and further characterized in that sludge associated therewith is non-bulking and has a high settling velocity, said third zone (C) being aerated during the first aerating period of time to regenerate the absorption capacity of the sludge and being settled during the second quiescent period of time; (d) decanting the upper portion of the wastewater from the third zone (C) during a third decanting period of time during which there is no inflow into the second zone (B) from the first zone (A); and (e) repeating in cyclic manner steps (b), (c) and (d), the operation of said steps being characterized as a cyclically aerated process, influent wastewater being retained in or before the first zone (A) or directed elsewhere therefrom during the third decanting time period.

Claim 3

The process of claim 1 wherein the second zone (B) and the third zone (C) are in free fluid communication with each other.

Claim 4

The process of claim 2 wherein oxygen is transferred into the wastewater in the third zone (C) regenerating the activated sludge and inducing backflow of regenerated sludge from the third zone (C) to the second zone (B).

Claim 5

The process of claim 3 wherein regenerated activated sludge is returned from the third zone (C) to the first zone (A) and to the second zone (B).

Claim 6

The process of claim 3 wherein the second zone (B) comprises additionally a fixed film growth support matrix which occupies from approximately twenty to approximately 90 percent of the portion of the second zone (B) below the bottom water level.

Claim 7

The process of claim 5 wherein the fixed film growth support matrix is moveable.

Claim 8

The process of claim 3 wherein the second zone (B) comprises a plurality of sub-zones, (B,B') each sub-zone absorptively transporting soluble biochemical oxygen demand of the wastewater entering such sub-zone until the wastewater flowing from the last sub-zone contains no more than twenty percent of the biochemical oxygen demand of the original influent wastewater into the process.

Claim 9

The process of claim 3 wherein the hydraulic retention time at mean flow conditions and the designated bottom water level in the second zone (B) is substantially equal to the second quiescent time.

Claim 10

The process of claim 3 comprising the further step of adding acetic acid to the second zone for thereby improving the phosphorus removal characteristics of the process.

Claim 11

The process of claim 1 wherein regenerated activated sludge is returned from the third zone (C) to the first zone (A) and to the second zone (B).

Claim 12

The process of claim 1 wherein the second zone (B) comprises additionally a fixed film growth support matrix which occupies from approximately twenty to approximately 90 percent of the portion of the second zone (B) below the bottom water level.

Claim 13

The process of claim 11 wherein the fixed film growth support matrix is moveable.

Claim 14

The process of claim 1 wherein the second zone (B) comprises a plurality of sub-zones, (B,B') each sub-zone absorptively transporting soluble biochemical oxygen demand of the wastewater entering such sub-zone until the wastewater flowing from the last sub-zone contains no more than twenty percent of the biochemical oxygen demand of the original influent wastewater into the process.

Claim 15

The process of claim 1 wherein the hydraulic retention time at mean flow conditions and the designated bottom water level in the second zone (B) is substantially equal to the second quiescent time.

Claim 16

The process of claim 1 comprising the further step of adding acetic acid to the second zone for thereby improving the phosphorus removal characteristics of the process.

Claim 17

A process for treating municipal wastewater to reduce biochemical oxygen demand and remove ammonia,nitrate nitrogen and phosphorus, comprising the steps of: (a) in a first zone (A) injecting regenerated activated sludge from a subsequent zone; (b) flowing wastewater from the first zone (A) to a second aerated zone (B) into which additional regenerated activated sludge is introduced; (c) flowing wastewater from the second zone (B) to a third zone (C) which is aerated to regenerate the activated sludge absorption capacity which is injected into the first zone (A) and introduced into the second zone (B); (d) settling the sludge and particulate matter in the second zone (B) and the third zone (C) and thereafter decanting fully wastewater from the upper layers of the third zone (C), there being no inflow from the first zone (A) to the second zone (B) during decantation; and (e) cyclically repeating steps (b), (c) and (d).

Claim 18

A process for treating municipal wastewater to reduce biochemical oxygen demand and remove ammonia,nitrate nitrogen and phosphorus, comprising the steps of: (a) in a first zone (A) injecting regenerated activated sludge from a subsequent zone; (b) flowing wastewater from the first zone (A) to a second aerated zone (B) into which additional regenerated activated sludge is introduced; (c) flowing wastewater from the second zone (B) to a third zone (C) which is aerated to regenerate the activated sludge absorption capacity which is injected into the first zone (A) and introduced into the second zone (B); (d) settling the sludge and particulate matter in the second zone (B) and the third zone (C) and thereafter decanting fully wastewater from the upper layers of the third zone (C), there being no inflow from the first zone (A) to the second zone (B) during decantation; and (e) cyclically repeating steps (b), (c) and (d).

Claim 19

The process of claim 16 wherein the second zone (B) and the third zone (C) are in free fluid communication with each other.

Claim 20

The process of claim 17 wherein oxygen is transferred into the wastewater in the third zone (C) regenerating the absorptive capacity of the activated sludge and including backflow of regenerated sludge from the third zone (C) to the second zone (B).

Claim 21

The process of claim 16 wherein the second zone (B) comprises additionally a fixed film growth support matrix which occupies from approximately twenty to approximately 90 percent of the portion of the second zone (B) below the bottom water level.

Claim 22

The process of claim 19 wherein the fixed film growth support matrix is moveable.

Claim 23

The process of claim 16 wherein the hydraulic retention time at mean flow conditions and the designated bottom water level in the second zone (B) is substantially equal to the settling time.

Claim 24

The process of claim 16 comprising the further step of adding acetic acid to the second zone for thereby improving the phosphorus removal characteristics of the process.

Claim 25

The process of claim 16 wherein the floc load of the influent into the first zone is less than approximately 250 mg chemical oxygen demand/gm MLVSS.

Claim 26

The process of claim 16 wherein multiple stage absorptive reaction, metabolism of the removed biochemical oxygen demand associated with sludge, regeneration of the absorptive capacity of the sludge, and settling of solids and decanting of wastewater is carried out in a single water retaining structure having partitions dividing said zones from each other.

Claim 27

A process for treating wastewater having a high biochemical oxygen demand of from approximately 250 mg/L to approximately 2,000 mg/L and a high soluble biochemical oxygen demand fraction of approximately 50% or more, comprising the steps of: (a) in a first zone (A) injecting regenerated activated sludge from a subsequent zone; (b) flowing wastewater from the first zone (A) to a second aerated zone (B) into which additional regenerated activated sludge is introduced, said second zone comprising a multiplicity of sub-zones each of which is aerated and into each of which additional regenerated activated sludge is introduced; (c) flowing wastewater from the second zone (B) to a third zone (C) which is aerated to regenerate the activated sludge which is injected into the first zone (A) and introduced into the second zone (B); (d) settling the sludge and particulate matter in the second zone (B) and the third zone (C) and thereafter decanting fully wastewater from the upper layers of the third zone (C), there being no inflow from the first zone (A) to the second zone (B) during decantation; and (e) cyclically repeating steps (b), (c) and (d).

Claim 28

A process for treating wastewater having a high biochemical oxygen demand of from approximately 250 mg/L to approximately 2,000 mg/L and a high soluble biochemical oxygen demand fraction of approximately 50% or more, comprising the steps of: (a) in a first zone (A) injecting regenerated activated sludge from a subsequent zone; (b) flowing wastewater from the first zone (A) to a second aerated zone (B) into which additional regenerated activated sludge is introduced, said second zone comprising a multiplicity of sub-zones each of which is aerated and into each of which additional regenerated activated sludge is introduced; (c) flowing wastewater from the second zone (B) to a third zone (C) which is aerated to regenerate the activated sludge which is injected into the first zone (A) and introduced into the second zone (B); (d) settling the sludge and particulate matter in the second zone (B) and the third zone (C) and thereafter decanting fully wastewater from the upper layers of the third zone (C), there being no inflow from the first zone (A) to the second zone (B) during decantation; and (e) cyclically repeating steps (b), (c) and (d).

Claim 29

The process of claim 25 wherein the second zone (B) and the third zone (C) are in free fluid communication with each other.

Claim 30

The process of claim 26 wherein oxygen is transferred into the wastewater in the third zone (C) regenerating the absorptive capacity of the activated sludge and inducing backflow of regenerated sludge from the third zone (C) to the second zone (B).

Claim 31

The process of claim 25 wherein the second zone (B) comprises additionally a fixed film growth support matrix which occupies from approximately twenty to approximately 90 percent of the portion of the second zone (B) below the bottom water level.

Claim 32

The process of claim 28 wherein the fixed film growth support matrix is moveable.

Claim 33

The process of claim 25 wherein the hydraulic retention time at mean flow conditions and the designated bottom water level in the second zone (B) is substantially equal to the settling time.

Claim 34

The process of claim 25 wherein multiple stage absorptive reaction, metabolism of the removed biochemical oxygen demand associated with sludge, regeneration of the absorptive capacity of the sludge, and settling of solids and decanting of wastewater is carried out in a single water retaining structure having partitions dividing said zones from each other.

Claim 35

A process for treating wastewater comprising the steps of: (a) continuously receiving wastewater into a initial absorption zone (A) into which activated sludge from a subsequent zone is mixed and retaining said wastewater in said initial absorption zone for a period of from at least approximately two to 20 minutes sufficient to form a non-bulking sludge and absorb biodegradable dissolved compounds into the activated sludge; (b) passing wastewater from the initial absorption zone (A) into at least one of two or more sequenced absorption zones (B 1 , B 2 ) during aeration thereof and passing wastewater into said respective sequenced absorption zones during respective quiescent time periods during which settling of sludge is caused in the respective sequenced absorption zones by maintaining a quiescent condition in said sequenced absorption zones; (c) passing wastewater from one sequenced absorption zone (B 1 ) into one biological degradation zone (C 1 ) and passing wastewater from another sequenced absorption zone (B 2 ) into another biological degradation zone (C 2 ) the wastewater passing into the biological degradation zones being characterized in that it has less than approximately twenty percent of the biochemical oxygen demand the wastewater originally contained and further characterized in that sludge associated there with is non-bulking and has a high settling velocity, said biological degradation zones (C 1 , C 2 ) being aerated to regenerate the absorption capacity of the sludge and being settled during respective quiescent periods; and (d) decanting the upper portion of the wastewater from one biological degradation zone (C 1 ) during one period of time and decanting the upper portion of the wastewater from the other biological degradation zone (C 2 ) during another period of time, there being no inflow from the intial absorption zone (A) into the one sequenced absorption zone (B 1 ) during the decantation of the one biological degradation zone (C 1 ), and there being no inflow into the other sequenced absorption zone (B 2 ) from the initial absorption zone (A) during the decantation of the other biological degradation zone (C 2 ), the decantation of the respective biological absoption zones (C 1 and C 2 ) being at different time periods.

Claim 36

A process for treating wastewater comprising the steps of: (a) continuously receiving wastewater into a initial absorption zone (A) into which activated sludge from a subsequent zone is mixed and retaining said wastewater in said initial absorption zone for a period of from at least approximately two to 20 minutes sufficient to form a non-bulking sludge and absorb biodegradable dissolved compounds into the activated sludge; (b) passing wastewater from the initial absorption zone (A) into at least one of two or more sequenced absorption zones (B 1 , B 2 ) during aeration thereof and passing wastewater into said respective sequenced absorption zones during respective quiescent time periods during which settling of sludge is caused in the respective sequenced absorption zones by maintaining a quiescent condition in said sequenced absorption zones; (c) passing wastewater from one sequenced absorption zone (B 1 ) into one biological degradation zone (C 1 ) and passing wastewater from another sequenced absorption zone (B 2 ) into another biological degradation zone (C 2 ) the wastewater passing into the biological degradation zones being characterized in that it has less than approximately twenty percent of the biochemical oxygen demand the wastewater originally contained and further characterized in that sludge associated there with is non-bulking and has a high settling velocity, said biological degradation zones (C 1 , C 2 ) being aerated to regenerate the absorption capacity of the sludge and being settled during respective quiescent periods; and (d) decanting the upper portion of the wastewater from one biological degradation zone (C 1 ) during one period of time and decanting the upper portion of the wastewater from the other biological degradation zone (C 2 ) during another period of time, there being no inflow from the intial absorption zone (A) into the one sequenced absorption zone (B 1 ) during the decantation of the one biological degradation zone (C 1 ), and there being no inflow into the other sequenced absorption zone (B 2 ) from the initial absorption zone (A) during the decantation of the other biological degradation zone (C 2 ), the decantation of the respective biological absoption zones (C 1 and C 2 ) being at different time periods.

Claim 37

The process of claim 32 wherein the sequenced absorption zones (B 1 and B 2 ) and the biological degradation zones (C 1 and C 2 ) respectively are in free fluid communication with each other.

Claim 38

The process of claim 33 wherein aeration is effected by inducing backflow of regenerated sludge from the biological degradation zones (C 1 and C 2 ) to the respective sequenced absorption zones (B 1 and B 2 ).

Claim 39

The process of claim 33 wherein regenerated activated sludge is returned from the biological degradation zones (C 1 and C 2 ) to the initial absorption zone (A) and to the respective sequenced absorption zones (B 1 and B 2 ).

Claim 40

The process of claim 33 wherein the respective sequenced absorption zones (B 1 and B 2 ) comprises additionally a fixed film growth support matrix which occupies from approximately twenty to approximately 90 percent of the portion of the respective sequenced absorption zones (B 1 and B 2 ) below the bottom water level.

Claim 41

The process of claim 36 wherein the fixed film growth support matrix is moveable.

Claim 42

The process of claim 33 wherein the respective sequenced absorption zones (B 1 and B 2 ) comprises a plurality of sub-zones, (B 1 , B' 1 and B 2 , B' 2 respectively) each sub-zone absorptively transporting soluble biochemical oxygen demand of the wastewater entering such sub-zone until the wastewater flowing from the last sub-zone contains no more than twenty percent of the biochemical oxygen demand of the original influent wastewater into the process.

Claim 43

The process of claim 33 wherein the hydraulic retention time at mean flow conditions and the designated bottom water level in the respective sequenced absorption zones (B 1 and B 2 ) is substantially equal to the respective settling times.

Claim 44

The process of claim 33 comprising the further step of adding acetic acid to the respective sequenced absorption zone for thereby improving the phosphorus removal characteristics of the process.

Claim 45

The process of claim 32 wherein regenerated activated sludge is returned from the respective biological degradation zones (C 1 and C 2 ) to the initial absorption zone (A) and to the respective sequenced absorption zones (B 1 and B 2 ).

Claim 46

The process of claim 32 wherein the sequenced absorption zones (B 1 and B 2 ) respectively comprise additionally a fixed film growth support matrix which occupies from approximately twenty to approximately 90 percent of the portion of the respective sequenced absorption zones (B 1 and B 2 ) below the bottom water level.

Claim 47

The process of claim 42 wherein the fixed film growth support matrix is moveable.

Claim 48

The process of claim 32 wherein the respective sequenced absorption zone (B 1 and B 2 ) comprises a plurality of sub-zones, (B 1 , B' 1 and B 2 , B' 2 respectively) each sub-zone absorptively transporting soluble biochemical oxygen demand of the wastewater entering such sub-zone until the wastewater flowing from the last sub-zone contains no more than twenty percent of the biochemical oxygen demand of the original influent wastewater into the process.

Claim 49

The process of claim 32 wherein the retention time of the biomass in the sequenced absorption zone (B 1 and B 2 ) respectively are substantially equal to the quiescent settling time.

Claim 50

The process of claim 32 comprising the further step of adding acetic acid to the second zone near the beginning of the first time period.

Claim 51

The process of claim 1, claim 16, claim 25 or claim 32 further comprising the steps of positioning in the second aeration absorption zone (B) a rotatable fixed film growth support matrix and rotating the matrix in a direction to effectively introduce regenerated activated sludge from the third zone (C) into the second zone (B).

Claim 52

The process of claim 47 wherein the rotatable fixed film growth support matrix is in the form of a rotatable drum-shaped body having a multiplicity of surface forming elements 190 mounted for rotation on a shaft 192 and rotating the body in a direction such that the portion of the body most adjacent the fluid communication means between the second zone (B) and the third zone (C) rotates away from said fluid communication means to effectively pump sludge from the third zone (C) to the second zone (B) and mix the sludge in the second zone (B).

Claim 53

The process of claim 1, claim 16, claim 25 or claim 32 further comprising the step of substantially continuously aerating the first zone A or zone B or both into which regenerated activated sludge is substantially continuously introduced into zone A and additionally into zone B.