the unexpected consequences of water conservation on water ... · water conservation on water ......

43
The Unexpected Consequences of Water Conservation on Water Reuse Facilities Linda Sawyer 925.210.2536 [email protected] Linda Sawyer WateReuse Northern California | December 8, 2017

Upload: vuonghanh

Post on 18-Jun-2018

217 views

Category:

Documents


0 download

TRANSCRIPT

The Unexpected Consequences of Water Conservation on Water Reuse Facilities

Linda Sawyer

[email protected]

Linda Sawyer

WateReuse Northern California | December 8, 2017

• Decreased Flows and Flow Projections

• Treatment Process Loading Capacity

• Alkalinity Limitations

• Effluent Quality

• Recycled Water Flows

Water Conservation and Water Reuse

Brown and Caldwell 2

REUSE

ADVANCED TREATMENT

DISCHARGE

Decreased Flows and Flow Projections

Brown and Caldwell 3

REUSE

ADVANCED TREATMENT

DISCHARGE

• Water conservation measures include• Drought tolerant landscaping• Outdoor water restrictions• Low-flow toilets• Low-flow shower heads• Faucet aerators• Water conserving appliances• Greywater recycling• Not flushing as often• Shorter showers

Drought Led to Water Conservation

Brown and Caldwell 4

0

1

2

3

4

5

6

7

8

Gal

lons

per

Toi

let F

lush

Before 1980

1980s-1990s

Low-Flow

Water Conservation Results in Lower Wastewater Flows

Brown and Caldwell 5Summer flow is July through September

Water Conservation Results in Lower Wastewater Flows

Brown and Caldwell 6Summer flow is July through September

Water Conservation Results in Lower Wastewater Flows

Brown and Caldwell 7

Water Conservation Results in Lower Wastewater Flows

Brown and Caldwell 8

Water Conservation Results in Lower Wastewater Flows

Brown and Caldwell 9

Letters indicate different plants. Flow range is permitted flow. Ratios based on summer flow (average of July through September).

Water Conservation Results in Lower Wastewater Flows

Brown and Caldwell 10

Letters indicate different plants. Flow range is permitted flow. Ratios based on summer flow (average of July through September).

Flow Projections and Decreased Flows

Brown and Caldwell 11

• Often developed with collection system planning

• Biggest concern is conveying peak flows

REUSE

ADVANCED TREATMENT

DISCHARGE

Flow Projections Conservatively High

Brown and Caldwell 12

Treatment Process Loading Capacity

Brown and Caldwell 13

REUSE

ADVANCED TREATMENT

DISCHARGE

Loadings Have Increased at Some Plants

Brown and Caldwell 14

Loadings Have Increased at Some Plants

Brown and Caldwell 15

Influent Concentrations Have Increased

Brown and Caldwell 16

Average Flow is Typically Used to Rate Capacity

Brown and Caldwell 17

DEWATERING THICKENING

HAULING

SECONDARY CLARIFIERS

FILTRATION CHLORINE CONTACT

ACTIVATED SLUDGEPRIMARY CLARIFIERS

REUSE

DIGESTION

ADVANCED TREATMENT

DISCHARGE

Average Flow

What Really Limits Plant Capacity?

Brown and Caldwell 18

DEWATERING THICKENING

HAULING

SECONDARY CLARIFIERS

FILTRATION CHLORINE CONTACT

ACTIVATED SLUDGEPRIMARY CLARIFIERS

REUSE

DIGESTION

ADVANCED TREATMENT

DISCHARGE

Organics Loading and Peak Flow

Peak FlowPeak Flow

Organics Loading

Example of Plant Capacity Change

Brown and Caldwell 19

Plant designed in the 1970s:

12 mgd at 120 gal/capita-day

20,000 lb BOD/day at 0.2 lb BOD/capita-day

Population: 100,000

Per Capita Flows Have Decreased

Brown and Caldwell 20

Treating design flow in 2015:

12 mgd at 120 60 gal/capita-day

20,000 40,000 lb BOD/day at 0.2 lb BOD/capita-day

Population: 100,000 200,000

Loading Capacity Exceeded at Design Flow

Brown and Caldwell 21

Flow Capacity Reduced at Design Loading

Brown and Caldwell 22

Treating design loading and population in 2015: 12 mgd 6 mgd at 120 60 gal/capita-day

• Loading is key to capacity

• Equivalent flow capacity now is probably less than it used to be

• Less flow does NOT mean spare capacity

Flow and Capacity

Brown and Caldwell 23

Alkalinity Limitations

Brown and Caldwell 24

REUSE

ADVANCED TREATMENT

DISCHARGE

Alkalinity is needed for nitrification

Brown and Caldwell 25

Nitrification consumes alkalinity (7.2 g Alkalinity (as CaCO3) destroyed/g N)

1 g Ammonia-N (NH3/NH4

+)

1 g Nitrite-N (NO2

-)

1 g Nitrate-N (NO3

-)

Alkalinity

O2

O2

Nitrogen Gas (N2)

1 g Nitrite -N(NO2

-)

Carbon

Carbon

Alkalinity

Alkalinity

Denitrification recovers some alkalinity

• Process includes primary clarifiers and activated sludge

• Flow decreased 12%

• Converting to nitrification

Case Study – El Estero Plant in Santa Barbara

Brown and Caldwell 26

Reference: Sawyer et al, “Planning for Future Droughts – Lessons Learned at Water Resource Recovery Facilities, WEFTEC 2016,

El Estero Influent Ammonia Increased 35%

Brown and Caldwell 27

Alkalinity Concentration Only Increased 6%

Brown and Caldwell 28

Changes in Potable Water Source May Exacerbate the Problem

Brown and Caldwell 29

• Before drought, alkalinity was sufficient

• Based on 2014 data, alkalinity supplementation was needed

• Source water changes can exacerbate the problem

• Monitor alkalinity and add chemical if needed

Alkalinity Supplementation Needed

Brown and Caldwell 30

2012 2014 Projected with desalination

Average alkalinity, mg CaCO3/L 385 402 309

Average Ammonia, mg N/L 39 52 52

Effluent Quality

Brown and Caldwell 31

REUSE

ADVANCED TREATMENT

DISCHARGE

Plant C Effluent Nitrate has Increased

Brown and Caldwell 32

Plant C

Plant C Effluent Phosphorus has Increased

Brown and Caldwell 33

Plant C

Process Models Predict Nutrient Concentration Increases

Brown and Caldwell 34

Influent NH3-N, mg/L

Effluent TN, mg/L

Effluent TN, lb/day

46.0 12.3 5,700

33.8 10.6 6,900

25.3 9.7 8,500

• Additional chemicals or improved processes may be needed

• Consider loading-based limits instead of concentration-based limits in permit negotiation• Attractive if strict discharge limit, but expect reduced

discharge flow due to recycling.

Planning for Effluent Concentration Increases

Brown and Caldwell 35

Recycled Water

Brown and Caldwell 36

REUSE

ADVANCED TREATMENT

DISCHARGE

• Excess capacity (stranded assets)

• Insufficient water to meet demands

• Revenue impacts

Less Water Available Due to Conservation

Brown and Caldwell 37

Planning Conservatism

Brown and Caldwell 38

DEWATERING THICKENING

HAULING

SECONDARY CLARIFIERS

FILTRATION CHLORINE CONTACT

ACTIVATED SLUDGEPRIMARY CLARIFIERS

REUSE

DIGESTION

ADVANCED TREATMENT

DISCHARGE

Lowest average flow may be conservative

Highest flow is conservative

Complete Reuse is Challenging

Brown and Caldwell 39

• Less water available for recycling

• Peak reuse demand is often in a different season and year than peak influent flow

• IPR and DPR demands are year-round, but brine disposal is required

Recycled Water – Challenges

Brown and Caldwell 40

Planning for Water Conservation

Brown and Caldwell 41

• Expect less flow that is more concentrated

• Understand the conservatism of flow projections

• Less flow may not mean spare treatment capacity

• Anticipate possible alkalinity limitations

• Expect increased effluent concentrations

• Plan for variations in recycled water supply and demand

Planning for Future Water Conservation

Brown and Caldwell 42

REUSE

ADVANCED TREATMENT

DISCHARGE

Thank You