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Nipigon Water Pollution Control Plant
       Secondary Treatment
         Aerobic Digestion
Parameter
TSS mg/L

BOD5 mg/L

CBOD5 mg/L

Total P mg/L

Average Day Flow m3

Peak Flow m3

Ecoli MPN/100mL

TKN mg/L

Ammonia mg/L

Nitrate mg/L

pH

COD mg/L

Ortho P mg/L
Design
Parameter
Parameter	
                 Criteria
TSS	
  
TSS mg/L                      140
BOD mg/L
BOD5 5	
                      100
CBOD mg/L
CBOD5 5	
  

Total P P	
  
 Total	
   mg/L               5.50

Average Dayay	
  Flow	
  
Average	
  D Flow m3          1630
Peak	
  Flow	
  
Peak Flow m3                  4780
Ecoli	
  
Ecoli MPN/100mL
TKN	
  
TKN mg/L
Ammonia	
  
Ammonia mg/L
Nitrate	
  
Nitrate mg/L
pH	
  
pH

COD mg/L

Ortho P mg/L
Design       2012
Parameter
Parameter	
             Criteria   Influent
TSS	
  
TSS mg/L                    140      123

BOD mg/L
BOD5 5	
                    100      94.8

CBOD mg/L
CBOD5 5	
  

Total P P	
  
 Total	
   mg/L             5.50     2.98

Average Dayay	
  Flow	
  
Average	
  D Flow           1630    808.4
m3
Peak	
  Flow	
  
Peak Flow m3                4780    2749.3
Ecoli	
  
Ecoli MPN/100mL
TKN	
  
TKN mg/L                             26.4
Ammonia	
  
Ammonia mg/L
Nitrate	
  
Nitrate mg/L
pH	
  
pH

COD mg/L

Ortho P mg/L
Design       2012     C of A
Parameter
Parameter	
             Criteria   Influent   Criteria
TSS	
  
TSS mg/L                    140      123         15

BOD mg/L
BOD5 5	
                    100      94.8

CBOD mg/L
CBOD5 5	
                                        15

Total P P	
  
 Total	
   mg/L             5.50     2.98        0.8

Average Dayay	
  Flow	
  
Average	
  D Flow           1630    808.4
m3
Peak	
  Flow	
  
Peak Flow m3                4780    2749.3
Ecoli	
  
Ecoli MPN/100mL                                 200
TKN	
  
TKN mg/L                             26.4
Ammonia	
  
Ammonia mg/L
Nitrate	
  
Nitrate mg/L
pH	
  
pH                                             6 to 9.5

COD mg/L

Ortho P mg/L
Design       2012     C of A      Primary
Parameter
                      Criteria   Influent   Criteria    Clarifier
TSS mg/L                  140      123         15         365.7

BOD5 mg/L                 100      94.8

CBOD5 mg/L                                     15

Total P mg/L             5.50      2.98        0.8

Average Day Flow m3      1630     808.4

Peak Flow m3             4780     2749.3

Ecoli MPN/100mL                               200

TKN mg/L                           26.4

Ammonia mg/L

Nitrate mg/L

pH                                           6 to 9.5

COD mg/L                                                  416.2

Ortho P mg/L                                              0.138
Design       2012     C of A      Primary     Secondary
Parameter
                      Criteria   Influent   Criteria    Clarifier    Clarifier
TSS mg/L                140        123         15         365.7        19.2

BOD5 mg/L               100        94.8

CBOD5 mg/L                                     15

Total P mg/L            5.50       2.98        0.8

Average Day Flow m3     1630      808.4

Peak Flow m3            4780      2749.3

Ecoli MPN/100mL                               200

TKN mg/L                           26.4

Ammonia mg/L

Nitrate mg/L

pH                                           6 to 9.5

COD mg/L                                                  416.2        48.9

Ortho P mg/L                                              0.138        0.126
Design       2012     C of A      Primary     Secondary     2012
Parameter
                   Criteria   Influent   Criteria    Clarifier    Clarifier   Effluent
TSS mg/L             140        123         15         365.7        19.2          9.0

BOD5 mg/L            100        94.8

CBOD5 mg/L                                  15                                    2.8

Total P mg/L         5.50       2.98        0.8                                  0.438

Average Day Flow     1630      808.4
m3
Peak Flow m3         4780      2749.3

Ecoli MPN/100mL                            200                                    11

TKN mg/L                        26.4

Ammonia mg/L                                                                     1.132

Nitrate mg/L                                                                     14.8

pH                                        6 to 9.5                            7.22 to 7.96

COD mg/L                                               416.2        48.9

Ortho P mg/L                                           0.138        0.126
Loading kg/day
Parameter    C of A      2012
            Criteria    Actual
TSS         40.75      7.30

CBOD5       40.75      2.29

Total P     1.63       0.35
In	
  2012,	
  the	
  Nipigon	
  WPCP	
  used	
  11,006	
  litres	
  (L)	
  of	
  Poly	
  Aluminum	
  Chloride,	
  with	
  an	
  
average	
  dosage	
  of	
  12.27	
  mg/L.	
  	
  The	
  primary	
  purpose	
  is	
  for	
  phosphorus	
  removal	
  and	
  a	
  
secondary	
  benefit	
  is	
  pH	
  control.	
  

Beginning	
  January	
  1,	
  2013	
  the	
  Wastewater	
  Systems	
  Effluent	
  RegulaXons	
  came	
  into	
  
effect.	
  	
  The	
  only	
  impact	
  on	
  2012	
  was	
  to	
  modify	
  the	
  sampling	
  program	
  for	
  2013.	
  	
  IniXal	
  
review	
  for	
  the	
  federal	
  regulaXon	
  would	
  imply	
  the	
  following	
  needs	
  to	
  occur	
  in	
  2013:	
  

1.	
  Submit	
  an	
  IdenXficaXon	
  Report	
  to	
  the	
  Effluent	
  Regulatory	
  ReporXng	
  InformaXon	
  	
  	
  	
  
System	
  by	
  May	
  15,	
  2013;	
  

2.	
  Prepare	
  a	
  Quarterly	
  Report	
  and	
  submit	
  with	
  45	
  days	
  of	
  the	
  end	
  of	
  the	
  quarter,	
  the	
  
first	
  report	
  is	
  due	
  May	
  15,	
  2013;	
  

3.	
  Prepare	
  a	
  2013	
  Annual	
  Report	
  and	
  submit	
  by	
  February	
  15,	
  2014;	
  and,	
  

4.	
  Revised	
  the	
  sampling	
  plan	
  on	
  January	
  1,	
  2013	
  to	
  include	
  analysis	
  of	
  un-­‐ionized	
  
ammonia,	
  pH	
  and	
  Total	
  Chlorine	
  Residual	
  in	
  the	
  effluent.	
  
Total	
  influent	
  flow	
  	
  to	
  the	
  Nipigon	
  WPCP	
  in	
  2012	
  was	
  295,886	
  m3	
  with	
  an	
  
average	
  day	
  flow	
  	
  of	
  808.4	
  m3.	
  

In	
  2012,	
  the	
  average	
  day	
  raw	
  water	
  flow	
  to	
  the	
  Nipigon	
  WTP	
  from	
  the	
  
Nipigon	
  River	
  	
  was	
  741	
  m3.	
  

The	
  influent	
  flow	
  to	
  the	
  Nipigon	
  WPCP	
  is	
  greater	
  than	
  the	
  raw	
  water	
  flow	
  
from	
  the	
  Nipigon	
  	
  WTP.	
  	
  	
  The	
  influent	
  flow	
  is	
  approximate	
  9.3%	
  greater	
  
than	
  the	
  water	
  taken	
  from	
  the	
  Nipigon	
  	
  River	
  and	
  provided	
  to	
  the	
  WTP.	
  

Generally,	
  all	
  sewage	
  collecXon	
  systems	
  experience	
  inflow	
  and	
  infiltraXon.	
  	
  
Typical	
  design	
  criteria	
  for	
  inflow	
  and	
  infiltraXon	
  is	
  10%	
  of	
  water	
  flow.	
  	
  This	
  is	
  
of	
  significance	
  because	
  it	
  would	
  indicate	
  that	
  there	
  are	
  minimal,	
  if	
  any,	
  
combined	
  sewers	
  which	
  was	
  confirmed	
  when	
  the	
  sanitary	
  sewer	
  collecXon	
  
system	
  was	
  video	
  inspected	
  in	
  2009	
  and	
  2010.	
  

The	
  new	
  sludge	
  storage	
  lagoon	
  is	
  39	
  m	
  long	
  by	
  33	
  m	
  wide	
  with	
  a	
  working	
  
depth	
  of	
  2.8	
  m	
  with	
  a	
  total	
  sludge	
  storage	
  capacity	
  of	
  1500	
  m3	
  .	
  
Nipigon Secondary Wastewater Treatment Plant Report - March, 2013
Nipigon Secondary Wastewater Treatment Plant Report - March, 2013

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Nipigon Secondary Wastewater Treatment Plant Report - March, 2013

  • 1.
  • 2. Nipigon Water Pollution Control Plant Secondary Treatment Aerobic Digestion
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  • 14.
  • 15.
  • 16.
  • 17.
  • 18.
  • 19.
  • 20.
  • 21.
  • 22. Parameter TSS mg/L BOD5 mg/L CBOD5 mg/L Total P mg/L Average Day Flow m3 Peak Flow m3 Ecoli MPN/100mL TKN mg/L Ammonia mg/L Nitrate mg/L pH COD mg/L Ortho P mg/L
  • 23. Design Parameter Parameter   Criteria TSS   TSS mg/L 140 BOD mg/L BOD5 5   100 CBOD mg/L CBOD5 5   Total P P   Total   mg/L 5.50 Average Dayay  Flow   Average  D Flow m3 1630 Peak  Flow   Peak Flow m3 4780 Ecoli   Ecoli MPN/100mL TKN   TKN mg/L Ammonia   Ammonia mg/L Nitrate   Nitrate mg/L pH   pH COD mg/L Ortho P mg/L
  • 24. Design 2012 Parameter Parameter   Criteria Influent TSS   TSS mg/L 140 123 BOD mg/L BOD5 5   100 94.8 CBOD mg/L CBOD5 5   Total P P   Total   mg/L 5.50 2.98 Average Dayay  Flow   Average  D Flow 1630 808.4 m3 Peak  Flow   Peak Flow m3 4780 2749.3 Ecoli   Ecoli MPN/100mL TKN   TKN mg/L 26.4 Ammonia   Ammonia mg/L Nitrate   Nitrate mg/L pH   pH COD mg/L Ortho P mg/L
  • 25. Design 2012 C of A Parameter Parameter   Criteria Influent Criteria TSS   TSS mg/L 140 123 15 BOD mg/L BOD5 5   100 94.8 CBOD mg/L CBOD5 5   15 Total P P   Total   mg/L 5.50 2.98 0.8 Average Dayay  Flow   Average  D Flow 1630 808.4 m3 Peak  Flow   Peak Flow m3 4780 2749.3 Ecoli   Ecoli MPN/100mL 200 TKN   TKN mg/L 26.4 Ammonia   Ammonia mg/L Nitrate   Nitrate mg/L pH   pH 6 to 9.5 COD mg/L Ortho P mg/L
  • 26. Design 2012 C of A Primary Parameter Criteria Influent Criteria Clarifier TSS mg/L 140 123 15 365.7 BOD5 mg/L 100 94.8 CBOD5 mg/L 15 Total P mg/L 5.50 2.98 0.8 Average Day Flow m3 1630 808.4 Peak Flow m3 4780 2749.3 Ecoli MPN/100mL 200 TKN mg/L 26.4 Ammonia mg/L Nitrate mg/L pH 6 to 9.5 COD mg/L 416.2 Ortho P mg/L 0.138
  • 27. Design 2012 C of A Primary Secondary Parameter Criteria Influent Criteria Clarifier Clarifier TSS mg/L 140 123 15 365.7 19.2 BOD5 mg/L 100 94.8 CBOD5 mg/L 15 Total P mg/L 5.50 2.98 0.8 Average Day Flow m3 1630 808.4 Peak Flow m3 4780 2749.3 Ecoli MPN/100mL 200 TKN mg/L 26.4 Ammonia mg/L Nitrate mg/L pH 6 to 9.5 COD mg/L 416.2 48.9 Ortho P mg/L 0.138 0.126
  • 28. Design 2012 C of A Primary Secondary 2012 Parameter Criteria Influent Criteria Clarifier Clarifier Effluent TSS mg/L 140 123 15 365.7 19.2 9.0 BOD5 mg/L 100 94.8 CBOD5 mg/L 15 2.8 Total P mg/L 5.50 2.98 0.8 0.438 Average Day Flow 1630 808.4 m3 Peak Flow m3 4780 2749.3 Ecoli MPN/100mL 200 11 TKN mg/L 26.4 Ammonia mg/L 1.132 Nitrate mg/L 14.8 pH 6 to 9.5 7.22 to 7.96 COD mg/L 416.2 48.9 Ortho P mg/L 0.138 0.126
  • 29. Loading kg/day Parameter C of A 2012 Criteria Actual TSS 40.75 7.30 CBOD5 40.75 2.29 Total P 1.63 0.35
  • 30. In  2012,  the  Nipigon  WPCP  used  11,006  litres  (L)  of  Poly  Aluminum  Chloride,  with  an   average  dosage  of  12.27  mg/L.    The  primary  purpose  is  for  phosphorus  removal  and  a   secondary  benefit  is  pH  control.   Beginning  January  1,  2013  the  Wastewater  Systems  Effluent  RegulaXons  came  into   effect.    The  only  impact  on  2012  was  to  modify  the  sampling  program  for  2013.    IniXal   review  for  the  federal  regulaXon  would  imply  the  following  needs  to  occur  in  2013:   1.  Submit  an  IdenXficaXon  Report  to  the  Effluent  Regulatory  ReporXng  InformaXon         System  by  May  15,  2013;   2.  Prepare  a  Quarterly  Report  and  submit  with  45  days  of  the  end  of  the  quarter,  the   first  report  is  due  May  15,  2013;   3.  Prepare  a  2013  Annual  Report  and  submit  by  February  15,  2014;  and,   4.  Revised  the  sampling  plan  on  January  1,  2013  to  include  analysis  of  un-­‐ionized   ammonia,  pH  and  Total  Chlorine  Residual  in  the  effluent.  
  • 31.
  • 32. Total  influent  flow    to  the  Nipigon  WPCP  in  2012  was  295,886  m3  with  an   average  day  flow    of  808.4  m3.   In  2012,  the  average  day  raw  water  flow  to  the  Nipigon  WTP  from  the   Nipigon  River    was  741  m3.   The  influent  flow  to  the  Nipigon  WPCP  is  greater  than  the  raw  water  flow   from  the  Nipigon    WTP.      The  influent  flow  is  approximate  9.3%  greater   than  the  water  taken  from  the  Nipigon    River  and  provided  to  the  WTP.   Generally,  all  sewage  collecXon  systems  experience  inflow  and  infiltraXon.     Typical  design  criteria  for  inflow  and  infiltraXon  is  10%  of  water  flow.    This  is   of  significance  because  it  would  indicate  that  there  are  minimal,  if  any,   combined  sewers  which  was  confirmed  when  the  sanitary  sewer  collecXon   system  was  video  inspected  in  2009  and  2010.   The  new  sludge  storage  lagoon  is  39  m  long  by  33  m  wide  with  a  working   depth  of  2.8  m  with  a  total  sludge  storage  capacity  of  1500  m3  .