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Materials Transport & NSCD Material Classes Velocity to Transport Relationships York NSCD Restoration PSY CCREP

Materials Transport & NSCD Material Classes Velocity to Transport Relationships York NSCD Restoration PSY CCREP

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Page 1: Materials Transport & NSCD Material Classes Velocity to Transport Relationships York NSCD Restoration PSY CCREP

Materials Transport & NSCD

Material ClassesVelocity to Transport Relationships

York NSCD RestorationPSY CCREP

Page 2: Materials Transport & NSCD Material Classes Velocity to Transport Relationships York NSCD Restoration PSY CCREP

Material Transport

• Organic Matter: DOM (70-90%), FPOM, CPOM, large woody debris (branches to whole trees).

• Inorganic Matter (Mineral): alluvium & bedload• Higher discharge streams can carry more and larger

particles.– Suspended load: fine suspended particles (turbidity).

– Bed load: Larger particles that bounce along bottom of stream.

– The relative amount of suspended vs. bed loads is dependent on velocity and turbulence of stream flow.

Page 3: Materials Transport & NSCD Material Classes Velocity to Transport Relationships York NSCD Restoration PSY CCREP
Page 4: Materials Transport & NSCD Material Classes Velocity to Transport Relationships York NSCD Restoration PSY CCREP

After rain, higher turbidity is not just a function of sediment run off; higher flow velocity suspends more sediments from bottom.

Total concentration of suspended particles highest near bottom.

Page 5: Materials Transport & NSCD Material Classes Velocity to Transport Relationships York NSCD Restoration PSY CCREP

Velocity & Material Transport Size

Page 6: Materials Transport & NSCD Material Classes Velocity to Transport Relationships York NSCD Restoration PSY CCREP

Deposition vs Erosion

Page 7: Materials Transport & NSCD Material Classes Velocity to Transport Relationships York NSCD Restoration PSY CCREP

Sediment Impacts & Contamination• Excess Sedimentation:

– Reduces hard substrate for periphyton.– Clogs gravel interstices; reduces spawning habitat for fish.– Microbial activity increase may cause oxygen depletion.– Filling and flooding.– Increases drinking water treatment costs; reduces aesthetics.

• Many chemicals, contaminants will collect within and adhere to sediments.

• Variable transport of contaminated sediments can have severe impact on biota:– Sediments collect in pools– Contaminated sediments can be retained for long periods of

time.

• Erosion is more aggressive due to unstable stream banks, flashy storm response, or sediment starved waters (e.g. below dams)

Page 8: Materials Transport & NSCD Material Classes Velocity to Transport Relationships York NSCD Restoration PSY CCREP

Rates of Stream-Bank Erosion

Cross Section of SBCC

486

488

490

492

494

496

498

0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150 160 170 180 190 200

Distance (ft)

Ele

vatio

n (f

t)

Aquatic Resource Restoration Company (ARRC), unpublished data

June 2003

March 2004

October 2004

About 2-20 ft of bank lost per year.

This is 10-100 times faster than expected.

How can we stabilize our stream channels?

Page 9: Materials Transport & NSCD Material Classes Velocity to Transport Relationships York NSCD Restoration PSY CCREP

Continuous monitoring instrumentation (below) is placed in the stream for a

month at a time

23 September 2003

Hour (from 17:00 on 09/22/2003)

17 21 01 05 09 13 17

Dis

cha

rge

(m

3/h

)S

usp

en

de

d S

ed

ime

nt L

oa

d (

kg/h

)

0

2e+4

4e+4

6e+4

8e+4

1e+5

Rai

nfal

l (i

nch

es

pe

r h

ou

r)

0.0

0.1

0.2

0.3

0.4

DischargeSS LoadRainfall

Data collected during a storm event (above) illustrates that this is when most erosion occurs.

Page 10: Materials Transport & NSCD Material Classes Velocity to Transport Relationships York NSCD Restoration PSY CCREP

NSCD• Natural Stream Channel Design

• Based on science of water flow = hydrology

• New channels may be created with meanders.

• Man-made structure of rock or logs to divert flow and slow erosion.

• Considers watershed size, climate, topography and geology to determine the proper dimensions, pattern and profile for no net erosion or accretion.

Page 11: Materials Transport & NSCD Material Classes Velocity to Transport Relationships York NSCD Restoration PSY CCREP

“J”-hook structures along meanders.

Natural Stream Channel Design (NSCD)

Page 12: Materials Transport & NSCD Material Classes Velocity to Transport Relationships York NSCD Restoration PSY CCREP

Replacing the streamside (riparian) forest.

Page 13: Materials Transport & NSCD Material Classes Velocity to Transport Relationships York NSCD Restoration PSY CCREP

odorus Creek Restoration Efficacy Program

Studying the Effectiveness of NSCD Restoration Efforts

- Does water quality during storm events improve?

- Is there a positive biological community response?

(periphyton, macroinvertebrates, finfish)

Page 14: Materials Transport & NSCD Material Classes Velocity to Transport Relationships York NSCD Restoration PSY CCREP

South and East Branch

Watersheds

Downstream Continuous Monitoring Sites

Upstream Reference Sites

Completed Restoration

Planned Restoration

Page 15: Materials Transport & NSCD Material Classes Velocity to Transport Relationships York NSCD Restoration PSY CCREP

Water Quality& Flow

• We measure nutrients and suspended sediments in water samples during all conditions and all year!

• We also measure the stream flow to determine how much nutrient and sediments travels downstream.

Page 16: Materials Transport & NSCD Material Classes Velocity to Transport Relationships York NSCD Restoration PSY CCREP

Storm Event Volume to Sediment Load(3/2003 – 3/2004)

Storm Event Volume (1000 x m3)

1 10 100 1000Sed

imen

t Lo

ad (

met

ric t

ons)

0.1

1

10

100

1000

?

Page 17: Materials Transport & NSCD Material Classes Velocity to Transport Relationships York NSCD Restoration PSY CCREP

Periphyton = “rock slime”

Indicator of nutrient and sediment pollution.

Page 18: Materials Transport & NSCD Material Classes Velocity to Transport Relationships York NSCD Restoration PSY CCREP

We also monitor the macroinvertebrate community, which mostly includes stream

insects.

Page 19: Materials Transport & NSCD Material Classes Velocity to Transport Relationships York NSCD Restoration PSY CCREP

Fish surveys by electrofishingPeter Siwik

Page 20: Materials Transport & NSCD Material Classes Velocity to Transport Relationships York NSCD Restoration PSY CCREP

PA Council of Trout Unlimited, 2002

Wild spawning trout would be a hallmark of restoration success, but it will likely require fisheries management changes such “catch and release”.

Page 21: Materials Transport & NSCD Material Classes Velocity to Transport Relationships York NSCD Restoration PSY CCREP

Below Sewage Treatment

Plants!

Parasites

Infections

Deformations