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9/3/2010 1 Fish Screening and Guidance at Water Diversions L S PE 1 FSOC Fish Passage Class September 13 -16, 2010 Yakima, WA Larry Swenson, P.E. Hydraulic Engineer, NOAA Fisheries The “Design” Fish Pacific Salmon and Steelhead Downstream-migrating salmonids 2

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Page 1: Fish Screening and Guidance at Water Diversionsfishscreensoc.com/wp-content/uploads/2010/09/Section-7-Juvenile... · Fish Screening and Guidance at Water Diversions LS PE 1 ... Objectives

9/3/2010

1

Fish Screening and Guidance at Water DiversionsL S P E

1

FSOC Fish Passage Class

September 13 -16, 2010

Yakima, WA

Larry Swenson, P.E.

Hydraulic Engineer, NOAA Fisheries

The “Design” Fish

Pacific Salmon and Steelhead

Downstream-migrating salmonids

2

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Chinook Fry

Objectives

1. Hazards for fish2 Biological basis of design

Practical Knowledge of:

2. Biological basis of design3. Educate participants in

project4. Data requirements5. Apply design data6. Screen types7. Screen materials8. Perform calculations9. Draw conceptual layouts10. Expedite permit review

process 4

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Topics

1. The Typical Water Diversion

2. Swimming Capabilities of Juvenile Salmonids

3. Behavior of Juvenile Salmonids

4. Basic Methods of Guiding Juvenile Salmonids

5. Placeholder – Not Used

6. Facility Planning – Data Requirements

7. Design Objectives

5

Topics - continued

8. Selecting the Screen Structure Site

9. Facility Design

Criteria

Velocity

S M t i lScreen Materials

10. Types of Screen Facilities

11. Debris

12. Screen Velocity - Balancing

6

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Topic 1. – Generic Water Diversion

7

On-Channel Screens

8

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Topic 2. Swimming Capability of Juvenile Capability of Juvenile Fish

University of Washington Fisheries Research Institute study (Smith and Carpenter, 1987) was used to develop fishCarpenter, 1987) was used to develop fish screen criteria

USFWS Bull Trout studies

9

Factors Related to Swimming Capability

Approach velocity, sweeping velocity, and canal velocity

Water Temperature

Fish SizeFish Size

Swimming Time Duration

Dissolved Oxygen Level

10

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Swimming Speeds Classification

Cruising

Speed

Sustained

Speed

Darting

Speed

Use MigrationAvoid

Obstacles

Escape

PredatorsObstacles Predators

Duration Hours Minutes Seconds

11

Juvenile Fish Swimming Speeds

12

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Effect of Temperature on Cruising Velocity

13

Effect of Temperature on Critical Velocity

14

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Effect of Fish Size on Critical Velocity

15

Topic 3. Behavior of Juvenile Topic 3. Behavior of Juvenile Salmonids

Physiology and Migration

Design issues

Dams and Water Diversions

R i P t b lReservoir Passage - turbulence

Guidance in dam forebays

Routes

16

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Behavior of Juvenile Fish-contd.

Reluctance to enter small bypasses

Preference for day or night migration past screen structures

Migration corridors in lakes (shoreline?

contd.

g (deep?)

Lateral line function

Dissolved Oxygen Level

17

PhysiologySmolt characteristics compared with parr

Body silvering (+)

Salinity tolerance (+)

Growth rate (+)

Weight per unit length (-)

Body total lipid content (+)

Blood glucose (+)

Gill microsome, Na, K, ATPase enzyme activity (+)

18

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Migration Timing and Fish Size

19

Migration Timing and Fish Size

70

mm

)

sand

s)

50

60 A70

mm

)

sand

s)

50

60 A

70

60

50

40

30

20

50

60

Ave

rage

fork

leng

th o

f mig

rant

s (m

of m

igra

ting

fry

and

sm

olts

(th

ous

30

10

0

20

40

0

20

16

12

BTemporal Pattern of Fry andSub-Yearling Smolts in TwoRivers on Vancouver Island

CHINOOK RUN TIMING

70

60

50

40

30

20

50

60

Ave

rage

fork

leng

th o

f mig

rant

s (m

of m

igra

ting

fry

and

sm

olts

(th

ous

30

10

0

20

40

0

20

16

12

BTemporal Pattern of Fry andSub-Yearling Smolts in TwoRivers on Vancouver Island

CHINOOK RUN TIMING

10 20 2010 2010 2010

40

30

20

A

Num

bers

o

8

4

0

March April May June

A - Cowichan River - 1967B - Nanaimo River - 1980

Source: Groot and Margolis 199110 20 2010 2010 2010

40

30

20

A

Num

bers

o

8

4

0

March April May June

A - Cowichan River - 1967B - Nanaimo River - 1980

Source: Groot and Margolis 1991

20

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Effect of River Flows

21

Effect of River Flows

22

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Topic 4. Basic Methods of Guiding Juvenile Salmonids

A. Physical Barriers—1. Fish screen or rack to prevent fish entry into

diversion

—2. Preferred screen design - guide fish to bypass without contacting screen

B. Behavioral Devices

23

Vertical and Non-Vertical Fixed-Plate S

Examples of Physical Barriers

Screens

Traveling Screens

Cylindrical Screens—Rotating Drum Screens

—Fixed Cylindrical Screen

Eicher Screens and Modular Inclined Screens

Pump Intake Screens

24

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Examples of Behavioral Devices

Sound

Light

Electric Fields

H d li A iHydraulic Action

25

Topic 5. Prioritizing Screen Projects

Number of fish entrained

Existing level of protection

Funding

ESA

Land ownership

Proximity to other projects

Frequency of diversion

T f di iType of diversion

26

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Topic 6. Facility Planning - Data Requirements

See Site Survey Form in Notebook

27

Topic 7. Design Objectives

Guide Fish Past Screens:Guide Fish Past Screens:

—Without contacting screen - impingement

—Without entrainment through seals, mesh, other gaps

—Without delay - guidance—Without delay - guidance

—Without injury or mortality

—Minimizing stress to fish

—Minimizing predation

28

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Topic 8. Selecting the Screen Structure Site

Minimizing delayO&MO&MOn-River siteOff-River siteHydraulics, HydrologyHeadBank characteristicsData Collection See NotebookData Collection – See Notebook

29

Off-Channel Diversion

30

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On-Channel Diversion

31

Channel Configuration –Approach Flow Conditions

32

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Other Site Considerations

Diversion Canal as Fish Habitat

Diversion Operations – Pitfalls

Starting and Stopping of Diversions

33

Topic 9. Facility Design

A. Recommend references included in Notebook

B. Design Features—Flow-Screen Angle

—Uniform Approach VelocityUniform Approach Velocity

—Channel Configuration

—Trashracks

—Seals

—Cleaning System34

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Facility Design - Velocity

Sweeping Component of Velocity—45 degrees or less between flow and screen

—Smaller angles provide higher sweep component

—Fish move towards bypass by swimming and by sweeping componentby sweeping component

35

Discharge, Q, calculations

LJ S

NOAA Fisheries

4-28-03

36

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37

38

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Velocity Components

39

Velocity Components

OV canalV=Osin= VcanalaV s cos

Canal

OV canalV=Osin= VcanalaV s cos

Canal

VV

V

V

V

Vsa

a

canal canal O

O

Canal

VV

V

V

V

Vsa

a

canal canal O

O

Canal

Vs

Screen

Vs

Screen

40

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•Fish Orientation in Front of Screens

41

NOAA Fisheries Velocity Criteria(Northwest Region)

S l id F

Va < 0.4 fps

Vs > Va

Uniform Flow Distribution

(S L h)/(V ) 60 d

Salmonid Fry

(Screen Length)/(Vs) < 60 seconds

42

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Screen Materials Criteria

NOAA Fisheries Screen Criteria included in Notebook

43

Screen Materials

44

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Screen Materials

45

Profile Bar

46

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Profile Bar

47

Vee-Wire Profile Bar - Criteria

Salmonid FrySa o d y

Maximum Bar Spacing = 1.75 mm

48

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Woven Wire

49

Woven Wire

50

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Woven Wire Fabric - Criteria

Salmonid FrySalmonid Fry

Max. Mesh Opening = 3/32 inch (2.38 mm)

Minimum Porosity = 27% Open AreaMinimum Porosity 27% Open Area

51

Perforated Plate

52

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Perforated Plate - Criteria

Salmonid FrySalmonid Fry

Maximum Opening = 3/32 inch (2.38 mm)

Minimum Porosity = 27% Open AreaMinimum Porosity 27% Open Area

53

Other Materials - Intralox

54

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Topic 10. Types of Positive Barrier Screens

Rotary Drum

Fixed Vertical Plate

Vertical Traveling belt and panelVertical Traveling – belt and panel

Non-Vertical Fixed Plate

Horizontal Fixed Plate

Eicher Screen

Modular Inclined Screens

End-Of-Pipe (Pump) Intake ScreensEnd Of Pipe (Pump) Intake Screens

55

Rotating Drum Screens

56

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Rotary Drum Screens

57

Rotating Drum Screens

58

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Rotating Drum Screens

59

Seals

60

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Seals

61

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Rotating Drum Screens Rotating Drum Screens -Advantages

Proven fish protection

Self-cleaning by rotation

Passes debris downstreamPasses debris downstream

63

Rotating Drum Screens -Disadvantages

Susceptible to direct hits from large debris

Large civil works are required.

Seals require much maintanance.

Susceptible to abrasions by sand -p ymesh requires periodic replacement.

64

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Vertical Fixed Plate Screens

65

Vertical Fixed PlateScreens

66

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Vertical Fixed Plate Screens

67

Vertical Fixed Plate Screens

68

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Vertical Fixed Plate Screens

69

Vertical Fixed Plate Screens - Advantages

Easy to seal

Mechanically simple

Can be installed on river’s edge - small screens—No bypass required

—Can use profile wire (very strong)

Mechanical/brush cleaning usually effective

Air burst cleaning system is on back side of screen.

Cleaning is started by timer or head loss.70

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Vertical Fixed Plate Screens - Disadvantages

Must be cleaned mechanically

Large bypass flows required

Brush arms can be damaged by large debris.

Circular air burst cleaners do not clean tientire screen.

71

Vertical Traveling Screens

72

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Traveling Screens

73

Traveling Screens

74

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Traveling Screens

75

Traveling Screens

76

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Traveling Screens - Advantages

Small screens can be installed on river.

Compact civil works

Self cleaned by rotation

Jet sprays provide additional p y pcleaning.

77

Traveling Screens -Disadvantages

Mechanically complex

Seals can be a problem.

Make sure meets all NMFS criteria.

78

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Non-Vertical Fixed Plate Screen

79

Non-Vertical Fixed Plate Screen

80

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Non-Vertical Fixed Plate Screens

81

Non-Vertical Fixed Plate Screens

82

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Non-Vertical Fixed Plate Screens

83

Non-Vertical Flat Plate Screens

84

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Non-Vertical Fixed Plate Screens

85

Non-Vertical Fixed Plate Screens

86

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Non-Vertical Fixed Plate Screens - Advantages

No moving partsNo moving parts

No bypass required if built in-river

87

Non-Vertical Fixed Plate Screens - Disadvantages

Self-cleaning may not be reliable

Risk of injury on screen during low flow

Must raise water surface

Tricky, unreliable flow rate controly,

Adult concerns

88

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Eicher Screens and Modular Inclined Screens

89

End-Of-Pipe Screens

90

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Fixed Cylinder Screens

Source: Johnson Screens, Inc..

91

Pump Screens (Active)

92

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Pump Screens(Active)

93

Pump Screens (Active)

94

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Fixed Cylindrical Screens -Advantages

Good option for deep intakes

Air burst cleaning system can be made to be effective

Some off-the-shelf models with water backwash systems meet NMFS criteria for active screens.

95

Fixed Cylindrical Screens -Disadvantages

Out of sight, out of mind

Need current to transport debris from screen site.

Air burst systems on large installations don’t always clean entire screen -especially the bottom.

Long, stringy vegetation is a problem on small pump screens.

96

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Pump Screens

97

Pump Screens

98

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Pump Screens

99

Pump Screens

100

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Passive Screens

101

Passive Screens

102

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Passive Screens

103

Passive Screens

104

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Passive Screens

105

Passive Screens

106

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Passive Screens

107

Passive Screens

108

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Passive Screens

109

11. Debris Management

Trashracks

Screen Cleaning Systems

110

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Trash racks - Criteria

“Open channel intakes shall include a trashOpen channel intakes shall include a trash rack which shall be kept free of debris.”

“In certain cases, a satisfactory profile bar screen can substitute for a trash rack.”

Comment - No trashrack would be rare situation - such as an on-river screen.

111

Trashracks

112

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Trashracks

113

Trashracks

114

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Cleaning System

115

Cleaning System

116

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Cleaning Systems - Criteria

Screens shall have automatic cleaningScreens shall have automatic cleaning system.

Effective, reliable, proven, approved by NMFS

Head differential to initiate cleaning = 0.1 ft

117

Cleaning System - ?

118

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Cleaning System - ?

119

Cleaning System

120

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Cleaning System

121

Cleaning System

122

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Cleaning System

123

Cleaning System

124

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Cleaning System

125

Cleaning System

126

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Cleaning System

127

12. Balancing Screen Velocities

Flat Plate ScreensFlat Plate Screens

Rotary Drum Screens

Cylindrical Screens

Case Study

128

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Approach Flow Conditions

129

Approach Flow Conditions

130

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Channel Configuration – Hydraulic Modeling

131

Channel Configuration – Hydraulic Modeling

132

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Channel Configuration –Approach Flow Conditions

133

Balancing Screen Velocities

134

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Balancing Screen Velocities

135

Uniform Approach Velocity

136

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Uniform Approach Velocity

137

Balancing Rotary Drum Screens

138

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Cylindrical Screen Without Internal Baffles

139

Cylindrical Screen With Internal Baffles

140

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Useful Link

Link to “Anadromous Salmonid Facility Design” document:

http://www.nwr.noaa.gov/Publications/Reference-Documents/Passage-Refs.cfm

141

Recent Innovative Projects

Rocky Reach Dam – Chelan Co. PUD - Columbia River, WA

Upper Baker Dam – Puget Sound Energy - Baker River, WA

Round Butte Dam – Portland General Electric –Deschutes River ORDeschutes River, OR

142

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Rocky Reach Dam

143

Rocky Reach Dam

144

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Upper Baker Lake

145

Upper Baker Lake

146

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Upper Baker Lake

147

Upper Baker Lake

148

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Upper Baker Lake

149

Upper Baker Lake

150

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Upper Baker Lake

151

Upper Baker Lake

152

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Upper Baker Lake

153

Upper Baker Lake

154

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Upper Baker Lake

155

Round Butte Dam

156

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Round Butte Dam

157

Round Butte Dam

158

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Supplemental Screen Slides

159

Rocky Reach Dam

160

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Rocky Reach

161

Rocky Reach

162

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Rocky Reach

163

Rocky Reach

164

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Howard Hanson

165

Howard Hanson

166

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167

Howard Hanson

168

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Howard Hanson

169

Entrance Horn / Fish Screen / Bypass ConduitLooking D/S

Fish Pathway

(Representative)

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171

Turbine Intake Screens

172

Screen

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TurbineIntakeScreens

Screen

Model

173

Turbine Intake Screens

174

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Turbine Intake Screens

175

Turbine Intake Screens

176

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Turbine Intake Screens

177

Thank-you

178