Chatham Water Pollution Control Plant

16
PUBLIC UTILITIES COMMISSION FOR THE MUNICIPALITY OF CHATHAM-KENT CHATHAM WATER POLLUTION CONTROL PLANT 2019 PERFORMANCE REPORT January 1 to December 31, 2019 Environmental Compliance Approval # 6551-8WXKHC

Transcript of Chatham Water Pollution Control Plant

PUBLIC UTILITIES COMMISSION

FOR THE MUNICIPALITY OF CHATHAM-KENT

CHATHAM WATER POLLUTION CONTROL PLANT

2019 PERFORMANCE REPORT

January 1 to December 31, 2019

Environmental Compliance Approval # 6551-8WXKHC

Plant Description The Chatham Water Pollution Control Plant provides treatment for wastewater for the community of Chatham. Wastewater is collected by 24 sewage pump stations and conveyed by a largely separated sanitary sewer system. Some combined sewers remain. Final effluent is discharged to the Thames River.

The Chatham Water Pollution Control Plant was first constructed in 1964 and underwent expansions in 1992 and 2004. The development of the facility has followed the growth of the municipality and the advancement in technology and regulations. The combined Plant 1 and Plant 2 facility has a rated capacity of 36,000m3/day, with a peak flow of 72,000m3/day.

The treatment system includes the following processes:

Raw sewage pumping

Screening collection and removal

Aerated grit removal using a grit chamber, grit slurry and cyclone

Chemical phosphorus removal

Primary treatment, primary sludge collection and pumping

Biological treatment using the Conventional Activated Sludge process

Final settling

Disinfection using Chlorine Gas and Sulphur Dioxide

Two-stage anaerobic digestion, sludge pumping and digested gas handling

Sludge Dewatering

In addition, recovered methane gas produced from the anaerobic digesters is used to power digester gas/natural gas fired boilers and the heat is consumed within the plant to offset energy costs.

As well, recovered methane gas produced by the anaerobic digesters powers a methane fired Generator which feeds power back to the hydro grid to generate revenue.

REPORTING REQUIREMENTS UNDER ENVIRONMENTAL COMPLIANCE APPROVAL #6551-8WXKHC

Summary and Interpretation of Monitoring and Comparison to the Effluent Limits: Condition 10 (6) (a) Tables 1 & 2 outline the monthly average results of parameters tested compared to the limits outlined in the Environmental Compliance Approval, Table 2 Effluent Limits. Success and Adequacy of the Works

During the reporting period, the annual average daily flow was 22,162 m3/day, which represents approximately 62% of the rated capacity of 36,000 m3/day. The maximum daily flow was 64,100 m3/day, which is 89% of the Peak Flow Rate of 72,000 m3/day.

Table 1: Summary of Monitoring Data and Comparison to Effluent Limits & Objectives – Concentrations

as well as rated capacity to the sewage works

Plant rated capacity of 36,000m3/day Total sewage flow to the works during a calendar year divided by the number of days during which sewage was flowing to the works that year

Month

Total

Monthly

Flow m3

Avg

Daily

Flow

/Month

m3/day

Avg

Daily

Flow/

Year

m3/day

% of

Plant

Capacity

CBOD5

mg/L

Total

S.S.

mg/L

Total

Ammonia

mg/L

Total P

mg/L pH

E.Coli /

100mL

CFU

Geomean

Total

Chlorine

Residual

mg/L

Limits: Dec 15 – Apr 15

None None 36,000 100 15 15 4.0 0.75 6.0 -

9.5

200 0.01

Limits: Apr 16 – Dec 14

None None 36,000 100 15 15 3.0 0.75 6.0 -

9.5

200 0.01

Objectives: Dec 15 – Apr 15

None None 36,000 100 10 10 3.0 0.60 6.0 -

9.5

150

Objectives: Apr 16 – Dec 14

None None 36,000 100 10 10 2.0 0.60 6.0 -

9.5

150

Jan 654,320 21,107 2.0 3.6 0.54 0.36 7.75 34.59 0.00

Feb 884,530 31,590 2.0 6.8 0.08 0.21 7.64 22.13 0.01

Mar 796,340 25,688 2.0 4.3 0.10 0.29 7.60 37.22 0.00

Apr 1,038,620 34,621 2.0 4.0 0.40 0.26 7.84 27.02 0.00

May 1,002,110 32,326 2.0 4.0 0.31 0.34 8.02 22.13 0.00

Jun 665,890 22,196 2.0 5.5 0.12 0.57 7.67 26.32 0.00

Jul 545,120 17,585 2.0 6.0 0.19 0.38 7.78 63.42 0.00

Aug 472,770 15,251 2.0 4.5 0.17 0.24 7.93 82.71 0.00

Sept 532,680 17,756 2.2 5.0 0.33 0.25 7.92 80.00 0.01

Oct 532,110 17,165 2.8 4.3 1.99 0.10 7.86 24.49 0.00

Nov 474,610 15,820 2.3 5.3 0.11 0.12 7.93 50.91 0.00

Dec 490,110 15,810 2.4 9.0 0.09 0.23 7.77 97.79 0.01

YEAR 22,162 62%

Yearly

Total Flow

m3

Yearly Maximums

8,089,210 34,621 2.8 9.0 1.99 0.57 8.02 97.79 0.01

Table 2: Summary of Monitoring Data and Comparison to Effluent Limits – Loadings Operating Problems and Corrective Action: Condition 10 (6) (b) There were no significant operating problems encountered during this reporting period.

Summary of Maintenance Activities: Condition 10 (6) (c) Routine maintenance was performed throughout the reporting period. Chatham-Kent PUC utilises an electronic preventative maintenance program to track preventative maintenance. In addition to the routine maintenance, the following additional maintenance activities and equipment replacement was completed for the reporting period:

Main Lift Pump #3 Rebuild $ 29,500

Replacement Chains & Flights for Plant #2 28,000

47’ ½” Checkmate Valve Pump Station 5 Storm Outfall 27,000

Lagoon Pump #1 Repair 19,800

Plant & Pump Station Electrical Upgrades 17,400

Piping Remediation (Main Lift) 16,900

Divers for Tidemate Install (Pump Station #5) 16,300

Automatic Composite Samplers (2) 15,400

New Check Valve (Pump Station #3) 12,400

New Transfer Pump Digester #3 11,700

New Pipes (Gas Room Basement) 10,700

Press Belts and Rollers 10,500

New Flow Meters (4) 9,900

Gas Room Maintenance & Inspection 9,300

Year

Avg

Daily

Effluent

Flow

/Year

m3/day

CBOD5

Kg/day

Total

S.S.

Kg/day

Total P

Kg/day

Limits: Receiver

None 540 540 27

Annual Average

2019 22,162 47.3 114.7 6.2

Replacement Press Conveyer Liners 8,500

New Impeller for Main Lift Pump #4 7,400

150 HP Blower Motor Repair 7,200

Runners for Final Chamber (Plant 2) 7,200

SCADA Remediation & New SCADA Computer 7,000

Sewer Plugs for Pipe Repairs (Grand Ave) 6,400

Portable Sampler 6,350

New In-ground Pipes 6,200

Gas RM Plug Valves 5,700

New Main Lift Pump #3 Impeller 5,500

Seal Kits for Vogelsang Pumps 5,350

Plant Blower Laser Alignment 4,100

Annual Flow, Pressure & Level Meter Calibrations 4,000

Press Replacement Equipment 3,900

Pump Station #3 Variable Frequency Drive (VFD) Repair 3,900

Pump Station #2 V.F.D. Repair 3,700

Aeration Valves (3) 3,600

Pump Station 3, Pump #3 VFD Repair 3,300

Rear Substation Reparation 3,300

Flight Chain Linkage and Blocks (Plant #1) 3,300

New Press V.F.D. 3,200

Main Lift Pump #4 Rebuild 3,000

Flight Chain Linkage and Blocks (Plant #2) 2,600

Boiler Inspection & Service 2,500

Backflow Inspection 2,400

Gas Room Electrical Upgrades 2,400

Seal Kit for Netzsch Pump 2,300

Vogelsang Wear Plates (6) 2,300

Tubing for Heat Exchanger #1 2,000

New VFD for Pump Station #22 1,800

Quality Assurance and Control Measures: Condition 10 (6) (d) The Chatham-Kent Public Utilities Commission followed a sampling schedule developed in accordance with the Environmental Compliance Approval and applicable regulations for this reporting period.

Composite chemistry samples of the raw flow were collected using an auto sampler. Chemistry samples were submitted weekly to an accredited laboratory for analysis of CBOD5, BOD5, Total Suspended Solids, Total Kjeldhal Nitrogen, Total Phosphorus, Total Ammonia Nitrogen, Nitrite and Nitrate, Alkalinity and pH.

Composite chemistry samples of the effluent were collected using an auto sampler. Chemistry samples were submitted weekly to an accredited laboratory for analysis of CBOD5, Total Suspended Solids, Total Kjeldhal Nitrogen, Total Phosphorus and Total Ammonia Nitrogen, Alkalinity, pH, Nitrite and Nitrate and Unionized Ammonia.

Bacteriological samples of the effluent were collected weekly according to the Sampling Program and submitted weekly to an accredited laboratory for analysis.

In house samples were analysed by a licensed operator for pH, temperature and D.O.

Calibration and Maintenance on Effluent Monitoring Equipment Condition 10 (6) (e) All required probes and sensors are cleaned, maintained and/or calibrated on a monthly basis or as required by manufacturers’ specifications. Monitoring equipment calibration/verification report(s) included for the following: • Effluent flow meter • Spectrophotometer • pH meter Effluent Objectives Condition 10 (6) (f)

Table 1 outlines monthly average results of parameters tested compared to the objectives outlined in the Certificate of Approval Table 1 Effluent Objectives.

Sludge Management Condition 10 (6) (g) The sludge generated at the facility is treated and air dried on site for 1 year, then land applied at the Ridge Landfill as top cover.

MONTH

DISPOSAL AREA

SLUDGE QUALITY

SLUDGE QUANTITY

LAND APPLIED m3

June

Ridge Landfill

Within Ministry Guidelines

559.26

July

Ridge Landfill

Within Ministry Guidelines

2,321.57

August

Ridge Landfill

Within Ministry Guidelines

2,954.97

Total 5,835.8

Outline of Anticipated Volumes in Next Reporting Period

The sludge production and sludge handling method for the coming reporting period is anticipated to be the similar to that of this reporting period. Community Complaints: Condition 10 (6) (h) There were no Customer Complaints received during the reporting period. By-pass, Spill, or Abnormal Discharge Events: Condition 10 (6) (i) A Pump Station Bypass event of 4,234 m3 occurred on May 02 for 14 hours immediately downstream from Pump Station #10, 251 Park Ave West, Chatham. The Bypass event resulted from heavy rainfall over the previous two weeks.

Other Information the District Manager Requires: Condition 10 (6) (j) No other information was required from the District Manager during this reporting period.

APPENDIX A Yearly Operational Data Summary for the Reporting Period

Mun

icip

ality

of C

hath

am-K

ent

Publ

ic U

tiliti

es C

omm

issio

nCh

atha

m W

ater

Pol

lutio

n Co

ntro

l Pla

ntW

orks

# 1

1000

0098

Ope

ratio

nal D

ata

Year

ly S

umm

ary 1

20

19

Ja

n.

Fe

b.

Ma

rch

Ap

ril

Ma

yJ

un

eJ

uly

Au

g.

Se

pt.

Oc

t.N

ov.

De

c.

TO

TA

LM

AX

MIN

AV

G

Tota

l Flo

w 1

03m

36

54

.32

08

84

.53

07

96

.34

01038.6

20

1002.1

10

66

5.8

90

54

5.1

20

47

2.7

70

53

2.6

80

53

2.1

10

47

4.6

10

49

0.1

10

80

89

.21

01

03

8.6

20

47

2.7

70

67

4.1

01

Avg.

Dai

ly F

low

103

m3

21

.10

73

1.5

90

25

.68

83

4.6

21

32

.32

62

2.1

96

17

.58

51

5.2

51

17

.75

61

7.1

65

15

.82

01

5.8

10

34

.62

11

5.2

51

22

.16

2

Max

. Dai

ly F

low

103

m3

49

.46

06

0.6

80

43

.24

06

4.1

00

60

.74

03

1.3

20

30

.79

02

1.9

60

32

.97

04

0.2

00

26

.13

02

3.1

80

64

.10

02

1.9

60

40

.39

8

Dirv

erte

d to

Lag

oons

103

m3

20

.04

81

29

.30

51

3.5

53

34

7.1

72

34

.26

51

0.5

69

20

.11

68

.26

82

4.1

65

18

.24

17

.62

08

.43

93

47

.17

27

.62

05

3.4

80

Lago

ons D

ischa

rge

103m

30

.00

00

.00

00

.00

00

.00

00

.00

00

.00

00

.00

00

.00

00

.00

00

.00

00

.00

00

.00

00

.00

00

.00

00

.00

00

.00

0

Avg.

Dai

ly F

low

103

m3

21

.10

73

1.5

90

25

.68

83

4.6

21

32

.32

62

2.1

96

17

.58

51

5.2

51

17

.75

61

7.1

65

15

.82

01

5.8

10

26

6.9

15

34

.62

11

5.2

51

22

.16

2

To

tal V

olu

me

In

m

34

47

53

02

15

30

03

37

25

71

05

56

24

45

23

57

06

10

95

35

77

10

66

85

26

08

85

71

06

30

21

50

74

Avg.

T.S

. %

3.7

4.5

3.7

3.9

4.1

3.5

3.3

0.0

2.9

2.6

3.0

3.3

4.5

0.0

3.2

Avg.

V.S

. %

63

.56

1.0

62

.95

9.5

53

.25

3.2

52

.90

.06

5.0

56

.55

3.4

51

.46

4.9

80

52

.7

Tota

l Vol

ume

Out

m

32

82

92

33

34

00

42

97

14

04

94

06

63

55

03

22

13

90

43

90

95

11

04

42

94

43

75

51

10

23

33

36

98

Avg.

T.S

. %

3.1

3.5

2.3

2.8

10

.53

.02

.72

.42

.62

.62

.62

.91

0.5

2.3

3.4

Avg.

V.S

. %

51

.14

8.6

51

.15

0.2

43

.94

5.9

49

.44

6.5

54

.74

9.7

49

.55

0.2

54

.74

3.9

49

.2

Tota

l Vol

ume

Out

m

33

33

12

66

54

53

43

22

04

94

24

51

03

98

33

54

04

41

34

16

05

12

74

71

84

91

43

51

27

26

65

40

95

Avg.

T.S

. %

1.9

2.1

2.2

2.2

3.0

2.8

2.4

2.2

1.9

2.2

2.4

2.3

3.0

1.9

2.3

Avg.

V.S

. %

50

.14

9.6

50

.15

0.3

44

.34

6.1

48

.94

9.1

54

.24

9.2

50

.15

3.4

54

.24

4.3

49

.6

To

tal H

ou

rs O

pe

rate

d2

12

.81

94

.02

17

.11

64

.61

96

.82

39

.41

86

.32

17

.22

13

.21

87

.81

32

.42

33

.02

39

4.5

23

9.4

13

2.4

19

9.5

Tota

l Slu

dge

Dew

ater

ed m

36

62

86

03

26

53

05

49

77

26

88

72

06

76

17

23

17

47

35

37

74

50

27

47

57

94

95

87

20

45

02

66

25

T.S

. S

lud

ge

%

3.5

3.6

3.4

3.5

3.6

3.1

3.1

3.1

3.1

3.1

2.7

3.1

3.6

2.7

3.2

Po

lym

er

# 7

57

Ib

s/m

on

th7

53

61

58

65

68

08

20

91

26

27

80

88

57

46

85

89

93

48

92

79

34

46

87

44

Ca

ke

To

tal S

olid

s %

15

.31

7.9

17

.91

7.4

19

.11

6.5

17

.51

8.5

17

.51

7.3

16

.41

6.8

20

8.1

19

.11

5.3

17

.3

Iro

n D

osa

ge

mg/L

5.0

53

.49

3.0

73

.11

3.0

35

.80

7.4

97

.20

3.7

05

.42

5.1

54

.89

57

.47

.53

.04

.8

Fe

rro

us C

hlo

rid

e k

g/D

75

.21

75

.70

58

.57

70

.47

68

.03

93

.62

10

8.9

61

08

.97

45

.61

69

.19

62

.10

56

.87

89

31

09

46

74

Ph

os

ph

oro

us

Re

mo

va

l C

he

mic

als

Ra

w S

ew

ag

e

Fin

al E

fflu

en

t

Ra

w S

lud

ge

# 1

Pri

ma

ry D

ige

sti

on

# 3

Pri

ma

ry D

ige

sti

on

Be

lt P

res

s

Mun

icip

ality

of C

hath

am-K

ent

Publ

ic U

tiliti

es C

omm

issio

nCh

atha

m W

ater

Pol

lutio

n Co

ntro

l Pla

ntW

orks

# 1

1000

0098

Ope

ratio

nal D

ata

Year

ly S

umm

ary 2

20

19

Ja

n.

Fe

b.

Ma

rch

Ap

ril

Ma

yJ

un

eJ

uly

Au

g.

Se

pt.

Oc

t.N

ov.

De

c.

TO

TA

LM

AX

MIN

AV

G

Ch

lorin

e U

se

d k

g/D

14

09

.51

59

9.0

17

71

.51

89

1.5

16

53

.51

48

9.0

10

90

.51

12

8.5

13

33

.01

27

7.0

13

43

.01

11

9.0

17

10

5.0

41

89

1.5

10

90

.51

42

5.4

2

Ch

lorin

e D

osa

ge

mg/L

2.2

31

.90

2.3

02

.05

1.7

52

.29

2.0

92

.43

2.6

32

.53

2.8

72

.31

2.8

71

.75

2.2

8

SO2 U

sed

kg/D

12

71

.51

26

5.0

14

09

.51

25

5.0

13

57

.51

26

4.0

98

5.5

90

3.0

13

06

.01

08

2.0

98

6.5

11

17

.01

42

02

.51

40

9.5

90

31

18

4

SO2 D

osag

e m

g/L

2.0

71

.58

1.8

21

.38

1.4

81

.96

1.9

11

.94

2.5

62

.20

2.1

32

.32

2.5

61

.38

1.9

5

Fina

l Res

idua

l mg/

L0

.00

0.0

10

.00

0.0

00

.00

0.0

00

.00

0.0

00

.01

0.0

00

.00

0.0

10

.01

0.0

00

.01

E.Co

li Av

erag

e /1

00m

L3

4.5

92

2.1

33

7.2

22

7.0

22

2.1

32

6.3

26

3.4

28

2.7

18

0.0

02

4.4

95

0.9

19

7.7

99

7.7

92

2.1

34

7.4

0

Ra

w S

ew

ag

e A

ve

rag

ep

H

7.5

37

.65

7.5

27

.75

7.8

67

.59

7.6

37

.66

7.6

67

.23

7.6

17

.59

7

.86

7.2

25

7.6

1

Am

mo

nia

as N

,

mg/L

21

15

19

19

16

20

25

35

27

26

26

28

35

.31

5.3

23

.0

Nitro

ge

n,

T.

Kje

lda

hl a

s N

, m

g/L

26

19

25

23

20

26

32

39

33

32

33

32

39

18

.52

8.3

Ph

osp

ho

rou

s,

To

tal a

s P

, m

g/L

3.3

2.6

4.1

4.6

5.8

9.2

8.0

9.1

5.9

5.2

8.6

8.3

9.2

2.6

6.2

So

lids,

Su

sp

en

de

d

mg/L

22

61

83

19

32

35

31

54

25

32

03

93

30

63

65

57

04

70

57

01

83

33

3

Alk

alin

ity C

aC

O3

, m

g/L

32

62

90

29

53

34

29

82

93

30

83

43

28

42

68

24

83

08

34

32

47

.52

99

BO

D5

, m

g/L

13

81

15

11

71

02

12

71

50

14

91

50

18

22

80

17

81

60

28

01

02

15

4

pH

7.7

57

.64

7.6

07

.84

8.0

27

.67

7.7

87

.93

7.9

27

.86

7.9

37

.77

8

.02

7.6

07

.81

Am

mo

nia

as N

,

mg/L

0.5

40

.08

0.1

00

.40

0.3

10

.12

0.1

90

.17

0.3

31

.99

0.1

10

.09

1.9

90

.08

0.3

7

NH 3

Un-

Ioni

zed

- Fed

eral

0.0

03

10

.00

06

0.0

00

60

.00

32

0.0

02

10

.00

08

0.0

01

40

.00

24

0.0

03

40

.02

00

0.0

01

00

.00

22

0.0

20

00

.00

06

0.0

03

4

Nitro

ge

n,

T.

Kje

lda

hl a

s N

, m

g/L

1.2

0.8

1.0

1.0

1.0

0.7

1.2

0.7

1.3

2.5

1.2

1.0

2.4

60

.67

1.1

2

Nitra

te a

s N

,

mg/L

13

.17

12

.20

11

.88

11

.55

9.3

31

7.2

81

8.9

11

3.3

32

0.5

86

.20

17

.53

21

.54

21

.54

6.2

01

4.4

6

Nitrite

as N

,

mg/L

0.0

31

0.0

13

0.0

21

0.0

38

0.0

35

0.0

11

0.0

28

0.0

11

0.0

27

0.0

94

0.0

19

0.0

12

0.0

94

0.0

11

0.0

3

Ph

osp

ho

rou

s,

To

tal a

s P

, m

g/L

0.3

60

.21

0.2

90

.26

0.3

40

.57

0.3

80

.24

0.2

50

.10

0.1

20

.23

0.5

70

.10

0.2

8

So

lids,

Su

sp

en

de

d

mg/L

3.6

6.8

4.3

4.0

4.0

5.5

6.0

4.5

5.0

4.3

5.3

9.0

9.0

3.6

5.2

Alk

alin

ity C

aC

O3

, m

g/L

19

41

73

19

31

96

22

01

35

13

41

75

13

21

70

18

01

64

22

01

32

17

2

CB

OD

5, m

g/L

2.0

2.0

2.0

2.0

2.0

2.0

2.0

2.0

2.2

2.8

2.3

2.4

2.8

2.0

2.1

D.O

. A

vg.

m

g/L

7.7

8.4

8.2

8.6

8.5

7.6

6.7

6.0

6.0

6.3

6.9

7.4

8.6

6.0

7.4

Te

mp

era

ture

C1

1.4

79

.59

10

.61

12

.29

14

.93

18

.97

21

.97

23

.10

23

.68

20

.75

17

.23

14

.59

23

.68

9.5

91

6.6

0

Sept

age

Rece

ived

m3/D

ay1

31

.72

54

.92

13

.54

29

.96

79

.63

57

.15

27

.43

83

.82

87

.03

18

.22

35

.72

03

.74

02

2.4

86

79

.58

13

1.7

33

35

.2

Leac

hate

mon

thly

tota

l 100

0m3

32

07

.23

18

3.0

32

37

.33

25

1.7

42

24

.92

30

4.1

26

42

.81

64

0.3

21

13

.03

98

9.6

39

36

.03

44

8.0

37

17

7.8

42

24

.91

64

0.2

73

09

8.2

Tota

l Grit

Rem

oved

m3

12

12

12

12

15

12

12

15

12

12

01

21

38

15

01

2

Dis

infe

cti

on

Fin

al E

fflu

en

t A

ve

rag

e

Le

ac

ha

te, S

ep

tag

e &

Gri

t

APPENDIX B Calibration Reports for the Reporting Period

Multi-Wavelength ColorimeterVerification Report

88CD2508D5CE3EEF068BDC2B5D0B3261.xls "If we don't measure it, how do you manage it?"

CUSTOMER Municipality of Chatham-Kent [MUT] MANUFACTURER HACHCONTACT Tim Dickinson MODEL DR3900

Chief Operator, Chatham STP SERIAL NUMBER 1613114325 Grand Ave CLIENT TAG Chatham STPChatham Ontario LOCATION Chatham STPT: 519-359-3811 OTHER n/aE. [email protected]

VER. BY Randy Nichol TOLERANCE [mg/L] 0.05STANDARD RECOVERY [%] 90

VERIFICATION DATE Mar 12, 2019CAL. FREQUENCYCAL. DUE DATE

CHLORINE [Cl2] SECONDARY STANDARDS

CHLORINE [Cl2] PRIMARY STANDARDS

STANDARD VALUE [mg/L] 27.3 BLANK SAMPLE SIZE [mL]STANDARD ADDITIONS SIZE [mL] 0.200

DPD LOT#EXPIRY DATE

COMMENTS [QMS] INFORMATION ITEM ID #[REFERENCE] HACH PCII 110.0 mL PIPETTE 10.2 mL PIPETTE 1SECONDARY STANDARDS 1PRIMARY STANDARDS 1ABSORBANCE STANDARDS 1

HACH-PP-10

AS-CLPSAS-CLSSG-PP-2

0.00

98.10.00 PASS

0.00 PASS

PASS

HACH PC II

May-23

N/A

STANDARD

PASS 94.2

PASS

AS FOUND CERTIFICATION

0.00

96.2

A8134

RECOVERY

PASS

DIFF.ERROR

0.53

STD 3

10.0

96.2

0

0.14 PASS

STD 1STD 2

%

AVERAGE RESULTS

0.600 10.600 1.55 1.46 1.461.01

STD 3

0.200 10.200 0.54 0.530.400 10.400

BLANK 0 10.000 0 0 0

COMBINED

mg/Lmg/LREADING FAIL

PASSREFERENCESTANDARD

MUT

+/-

0.230.921.71

PASS0.10

SAMPLETEST

#

Cl2STANDARD

mLSAMPLE

mL

1.01

1.71

+/-

STANDARD BLANK [mg/L]

0.250.94

0.09

READINGmg/L

PASS

REFERENCEREADING

mg/L

FAIL

mg/L

1.05

STD 1STD 2 +/-

AnnualMarch , 2020

WAVELENGTH PASS/FAIL

AS-ABS

ABSORBANCE CHECKS

PASS

Yes PASSYes PASSYes PASSYes PASS

560 nm610 nm

520 nm420 nm

TESTED

Primary and Secondary standards were used to confirm the overall accuracy of this instrument along with conducting an analytical comparative technique against a reference meter. All values are considered "AS FOUND" readings. If the "AS FOUND" readings were not within acceptable limits, an "AS LEFT" report will be issued if the instrument was able to be calibrated to indicate the overall accuracy of the meter. If the meter was not calibrated for any reason, a comment will be issued for this instrument.

Quality Management Standards Information - Standards, reference equipment, and instrumentation used to conduct this test outlining the lot#, and expiry date is found in our current QMS document.

Cl 2 ColorimeterVerification Report

A317D8761A3E136A330475CCEFBB1311.xls "If we don't measure it, how do you manage it?"

CUSTOMER Municipality of Chatham-Kent [MUT] MANUFACTURER HACHCONTACT Tim Dickinson MODEL Pocket Colorimeter II

Chief Operator, Chatham STP SERIAL NUMBER 08070E105502325 Grand Ave CLIENT TAG n/aChatham Ontario LOCATION Chatham STPT: 519-359-3811 OTHER n/aE. [email protected]

VER. BY Randy Nichol TOLERANCE [mg/L] 0.05STANDARD RECOVERY [%] 90

VERIFICATION DATE Mar 12, 2019CAL. FREQUENCYCAL. DUE DATE

CHLORINE [Cl2] SECONDARY STANDARDS

CHLORINE [Cl2] PRIMARY STANDARDS

STANDARD VALUE [mg/L] 27.3 BLANK SAMPLE SIZE [mL]STANDARD ADDITIONS SIZE [mL] 0.200

DPD LOT#EXPIRY DATE

COMMENTS

[QMS] INFORMATION ITEM ID #[REFERENCE] HACH PCII 110.0 mL PIPETTE 10.2 mL PIPETTE 1SECONDARY STANDARDS 1PRIMARY STANDARDS 1

PASS

HACH-PP-10

AS-CLPSAS-CLSSG-PP-2

0.00

98.10.01 PASS

PASS

HACH PC II

May-23

N/A

STANDARD

PASS 94.2

PASS

AS FOUND CERTIFICATION

0.01

0.911.68

AnnualMarch, 2020

0.01 PASS 96.2

A8134

PASS

RECOVERY

0.54

STD 3

10.0

96.2

0

0.14 PASS

STD 1STD 2

%

AVERAGE RESULTS

0.600 10.600 1.55 1.46 1.461.05 1.01

STD 3

0.200 10.200 0.54 0.530.400 10.400

BLANK 0 10.000 0 0 0

DIFF.ERROR

mg/Lmg/LREADING FAIL

PASSCOMBINEDSAMPLE

mL

REFERENCESTANDARD

FAIL

mg/L

+/-+/-

0.22

SAMPLETEST

#

Cl2STANDARD

mL

1.68

+/-

STANDARD NIST STD [mg/L]

0.260.92

0.09STD 1STD 2 0.10

READINGmg/L

PASS

REFERENCEREADING

mg/L

MUT

PASS

1.02

Primary and Secondary standards were used to confirm the overall accuracy of this instrument along with conducting an analytical comparative technique against a reference meter. All values are considered "AS FOUND" readings. If the "AS FOUND" readings were not within acceptable limits, an "AS LEFT" report will be issued if the instrument was able to be calibrated to indicate the overall accuracy of the meter. If the meter was not calibrated for any reason, a comment will be issued for this instrument.

Quality Management Standards Information - Standards, reference equipment, and instrumentation used to conduct this test outlining the lot#, and expiry date is found in our current QMS document.

pHVerification/Calibration Report

C3729813EC86D46A2354CD082E514885.xls "If we don't measure it, how do you manage it?"

CUSTOMER Municipality of Chatham-Kent [MUT] MANUFACTURER HACHCONTACT Tim Dickinson MODEL Sension +ph

Chief Operator, Chatham STP SERIAL NUMBER 608073325 Grand Ave CLIENT TAG n/aChatham Ontario LOCATION Chatham STPT: 519-359-3811 OTHER E. [email protected]

VER. BY Randy Nichol TOLERANCE [pH] 0.05

VERIFICATION DATE Mar 5, 2019CAL. FREQUENCYCAL. DUE DATE

pH VERIFICATIONNIST TRACEABLE (BUFFERS)

BEFORE CALIBRATION

CORRECTED

AFTER CALIBRATION

CORRECTED

mv offset/AssymetrySlope

COMMENTS [QMS] INFORMATION ITEM ID #

no calibration needed[REFERENCE]4.01 BUFFER 17.01 BUFFER 110.01 BUFFER 1TEMPERATURE REF. 1

pHBUFF4

DDTEMPpHBUFF10pHBUFF7

pH TEMP. pH pH

RESULT PASS

PASS° C DIFF.

7.0210.09

15.7

PASSPASS

pH TEMP. pH pH TEMP. pH - ERROR

15.815.815.8

AnnualMar-2020

REFERENCE BUFFER

FAIL

PASSPASS

TEMP. pH - ERROR PASS

RESULT PASS

BUFFER4.017.01

10.01

° C

-0.02-0.01

4.00 4.02 15.6 0.027.04

PASS

BUFFER

[MUT] READINGS

° C ° C DIFF. FAIL

[MUT] READINGSREFERENCE BUFFER

4.01 15.8 4.00 4.02 15.6 0.027.01 15.8 7.04 7.02 15.7 -0.02

10.01 15.8 10.10 10.09 15.8 -0.01 PASS

n/an/a

PASSPASS[MUT] AS FOUND

[MUT] AS LEFT

10.10 15.8

NIST Traceable Buffers were used to confirm the overall accuracy of this instrument. "AS FOUND" readings and "AS FOUND" readings are reported within this report. A temperature device was used to measure and record the buffer temperature to correct for pH values due to the effects related to buffer temperature.

Quality Management Standards Information - Standards, reference equipment, and instrumentation used to conduct this test outlining the lot#, and expiry date is found in our current QMS document.

Dissolved OxygenVerification/Calibration Report

BA187A63B7AD88B047C4AB4C4A8D72F4.xls "If we don't measure it, how do you manage it?"

CUSTOMER Municipality of Chatham-Kent [MUT] MANUFACTURER AysixCONTACT Tim Dickinson MODEL 3100

Chief Operator, Chatham STP SERIAL NUMBER 30S4949325 Grand Ave CLIENT TAGChatham Ontario LOCATION Chatham STPT: 519-359-3811 OTHER n/aE. [email protected]

VER. BY Randy Nichol TOLERANCE [pH] 0.05

VERIFICATION DATE Mar 12, 2019CAL. FREQUENCYCAL. DUE DATE

AS FOUND

AS LEFT

COMMENTS[QMS] INFORMATION ITEM ID #

Comparision Match to HQ30D 080200018124

Performed calibration as per manufacturers suggested technique

Chatham STP

8.7n/a

DO Concentration [mg/L] 9.3DO Concentration [%] n/a

DO Concentration [mg/L]DO Concentration [%]Barometric Pressure [hpa]

Barometric Pressure [hpa] n/aTemperature 19.1

19

AnnualMar-2020

n/aTemperature

NIST Traceable Buffers were used to confirm the overall accuracy of this instrument. "AS FOUND" readings and "AS FOUND" readings are reported within this report. A temperature device was used to measure and record the buffer temperature to correct for pH values due to the effects related to buffer temperature.

Quality Management Standards Information - Standards, reference equipment, and instrumentation used to conduct this test outlining the lot#, and expiry date is found in our current QMS document.