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Irene Seco Manuel Gómez Alma Schellart Simon Tait Erosion resistance and behaviour of highly organic in-sewer sediment 7th International Conference on Sewer Processes & Networks Wednesday 28 - Friday 30 August 2013 The Edge Conference Centre, Sheffield

Irene Seco Manuel Gómez Alma Schellart Simon Tait

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7th International Conference on Sewer Processes & Networks Wednesday 28 - Friday 30 August 2013 The Edge Conference Centre, Sheffield. Erosion resistance and behaviour of highly organic in-sewer sediment. Irene Seco Manuel Gómez Alma Schellart Simon Tait. - PowerPoint PPT Presentation

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Page 1: Irene  Seco Manuel Gómez Alma Schellart Simon Tait

Irene SecoManuel GómezAlma SchellartSimon Tait

Erosion resistance and behaviour of highly organic in-sewer sediment

7th International Conference on Sewer Processes & NetworksWednesday 28 - Friday 30 August 2013The Edge Conference Centre, Sheffield

Page 2: Irene  Seco Manuel Gómez Alma Schellart Simon Tait

Wet weather pollution from combined sewer systems

Release of in-sewer sediment deposits accumulated during dry-

weather constitute a major source of pollutants that affect the water

quality of receiving natural water bodies

Page 3: Irene  Seco Manuel Gómez Alma Schellart Simon Tait

Long dry-weather periodsIntense precipitation events

Wet weather pollution from combined sewer systems

Rain regime

Particularities in the Mediterranean region in Spain:

cumulative precipitation = 600 mm/year(concentrater 50 days/year)

average dry-period between rain: 11 days

≈ 40% rainfall registered P(mm)>10mm

Page 4: Irene  Seco Manuel Gómez Alma Schellart Simon Tait

Long dry-weather periodsIntense precipitation events

Wet weather pollution from combined sewer systems

Rain regime

In-sewer sediment accummulation and consolidation

Particularities in the Mediterranean region in Spain:

Page 5: Irene  Seco Manuel Gómez Alma Schellart Simon Tait

Wet weather pollution from combined sewer systems

Low circulating flow(0.56 m3/s average Congost River. Vallès Oriental. Catalonia. Spain)

Low dilution capacity

Particularities in the Mediterranean region in Spain:

Flow regime in riversLong dry-weather periods

Intense precipitation events

Rain regime

Page 6: Irene  Seco Manuel Gómez Alma Schellart Simon Tait

Wet weather pollution from combined sewer systems

Particularities in the Mediterranean region in Spain:

Low circulating flowLow dilution capacity

Flow regime in riversLong dry-weather periods

Intense precipitation events

Rain regime

High percentage of impervious surface in

Urban areas

Urban pattern

Page 7: Irene  Seco Manuel Gómez Alma Schellart Simon Tait

Wet weather pollution from combined sewer systems

Particularities in the Mediterranean region in Spain:

Low circulating flowLow dilution capacity

Flow regime in riversLong dry-weather periods

Intense precipitation events

Rain regime

High percentage of impervious surface in

Urban areas

Urban pattern

Sewer solids mainly from wastewatersRelevant Organic

composition

Page 8: Irene  Seco Manuel Gómez Alma Schellart Simon Tait

Wet weather pollution from combined sewer systems

Particularities in the Mediterranean region in Spain:

Significant volumes discharged in a shorttime from sewer network (CSO)Significant organic Pollution in natural streams and sea

Overflows during wet-weather

Low circulating flowLow dilution capacity

Flow regime in riversLong dry-weather periods

Intense precipitation events

Rain regime

High percentage of impervious surface in

Urban areas

Urban pattern

Page 9: Irene  Seco Manuel Gómez Alma Schellart Simon Tait

Objectives of this study

Particular conditions of Build-up/Wash-off affects the initiation of sediment motion

Page 10: Irene  Seco Manuel Gómez Alma Schellart Simon Tait

Objectives of this study

Consider potential incidence of the environmental conditions in-sewer on the transport loads and initiation of motion

Analyse changes in transport potential for different lengths of antecedent dry-weather periodsInvestigate erosion

behaviour of real in-sewer organic-rich

sediment collected in Spain

Particular conditions of Build-up/Wash-off affects the initiation of sediment motion

Page 11: Irene  Seco Manuel Gómez Alma Schellart Simon Tait

• Long dry-weather period/Build-up

• Intense rainfall/Wash-off

Suitable to be applied to the particular Mediterranean climate and urban pattern

conditions

Objectives of this study

Improve prediction of in-sewer sediment transport loads

Page 12: Irene  Seco Manuel Gómez Alma Schellart Simon Tait

Real in sewer sediment characteristics

Sediment collected from a sewer system (residential and commercial area in

Catalonia, Spain)

Page 13: Irene  Seco Manuel Gómez Alma Schellart Simon Tait

Real in sewer sediment characteristics

relevant Organic content

(O.M. around 80%) organic nature of solid particles from domestic wastewaters, and the presence of

greasesCohesive properties

Sediment collected from a sewer system (residential and commercial area in

Catalonia, Spain)

Page 14: Irene  Seco Manuel Gómez Alma Schellart Simon Tait

Real in sewer sediment characteristics

relevant Organic content

(O.M. around 80%) Related with the organic nature of solid particles from domestic wastewaters, and

the presence of greasesCohesive properties

d50 = 0.31 mm (310 µm)

Density = 1310 kg/m3

0 0.25 0.5 0.75 1 1.25 1.5 1.75 2 2.25 2.50

20406080

100 Sieving analysis of sewer sediment in natural state

mesh width (mm) % a

ccum

ulat

ed

on th

e sie

ve

Sediment collected from a sewer system (residential and commercial area in

Catalonia, Spain)

Page 15: Irene  Seco Manuel Gómez Alma Schellart Simon Tait

Consolidation, microbiological degradation, chemical-biological interactions (bonding forces between particles )

Real in sewer sediment characteristics

Effects on the transport of solidssignificant influence on the incipient motion

Sediment with high organic content and cohesive properties

Page 16: Irene  Seco Manuel Gómez Alma Schellart Simon Tait

Laboratory erosion measurement

Liem et al. (1997) investigation on erosional proecess of cohesive sediment using an in-situ measuring device. International Journal of Sediment Research, 12 (3), 139-147

Evaluation Erosion Rate

Assessment critical threshold of motion at solid-

fluid interface

Erosion meter devised (based on a design by Liem et al. 1997).

Page 17: Irene  Seco Manuel Gómez Alma Schellart Simon Tait

Laboratory erosion measurement

A prepared sample is exposed to a consolidation period and subsequently subject to increased shear stress, to simulate increased flows through sewer pipes at the start of a storm event.

Simulation of dry-weather periods

• Different lengths: 16, 64, 140 hours• Environmental conditions:

Anaerobic and Aerobic• Constant low shear stress:

0.15 N/m2 (dry-weather flows inside conduits)

Consolidation period Erosion phase Sampling and Analysis

Page 18: Irene  Seco Manuel Gómez Alma Schellart Simon Tait

Simulation of dry-weather periods

• Different lengths: 16, 64, 140 hours• Environmental conditions:

Anaerobic and Aerobic• Constant low shear stress:

0.15 N/m2 (dry-weather flows inside conduits)

Laboratory erosion measurement

A prepared sample is exposed to a consolidation period and subsequently subject to increased shear stress, to simulate increased flows through sewer pipes at the start of a storm event.

Consolidation period

Simulation flows at start of storm

event

Increasing shear stress is applied

in a stepwise way

Erosion phase Sampling and Analysis

Page 19: Irene  Seco Manuel Gómez Alma Schellart Simon Tait

Simulation of dry-weather periods

• Different lengths: 16, 64, 140 hours• Environmental conditions:

Anaerobic and Aerobic• Constant low shear stress:

0.15 N/m2 (dry-weather flows inside conduits)

Laboratory erosion measurement

A prepared sample is exposed to a consolidation period and subsequently subject to increased shear stress, to simulate increased flows through sewer pipes at the start of a storm event.

Consolidation period

Simulation flows at start of storm

event

Increasing shear stress is applied

in a stepwise way

Erosion phaseSediment samples

collected during erosion tests at each shear stress

intervalRemaining

sediment after tests collected

Sampling and Analysis

Page 20: Irene  Seco Manuel Gómez Alma Schellart Simon Tait

Main Results

Average erosion rate (q) linked to the applied shear stress (tb)

Aerobic

0 0.2 0.4 0.6 0.8 10.00

0.40

0.80

1.20

1.60

2.00

Applied shear stress (Tau_b) [N/m2]er

osio

n ra

te (E

) [g/

m2/

s]

0 0.2 0.4 0.6 0.8 10.00

0.40

0.80

1.20

1.60

2.00

Applied shear stress (Tau_b) [N/m2]

eros

ion

rate

(E) [

g/m

2/s]

0 0.2 0.4 0.6 0.8 10.00

0.40

0.80

1.20

1.60

2.00

Applied shear stress (Tau_b) [N/m2]

eros

ion

rate

(E) [

g/m

2/s]

0 0.2 0.4 0.6 0.8 10.00

0.40

0.80

1.20

1.60

2.00

Applied shear stress (Tau_b) [N/m2]

eros

ion

rate

(E) [

g/m

2/s]

0 0.2 0.4 0.6 0.8 10.00

0.40

0.80

1.20

1.60

2.00

Applied shear stress (Tau_b) [N/m2]

eros

ion

rate

(E) [

g/m

2/s]

Anaerobic

T116h

T3140h

T264h

T416h

T564h

Erosion rate of sediments monitored in terms of Suspended Sediment concentration

Page 21: Irene  Seco Manuel Gómez Alma Schellart Simon Tait

Main ResultsErosion Rate valuesComparison between tests with increasing length of periods of consolidation.

0 0.2 0.4 0.6 0.80.0

0.4

0.8

1.2

1.6

2.0

Applied shear stress (Tau_b) [N/m2]

eros

ion

rate

[g/

m2/

s]

0 0.2 0.4 0.6 0.80.0

0.4

0.8

1.2

1.6

2.0

Applied shear stress (Tau_b) [N/m2]

eros

ion

rate

[g/m

2/s]

16h (T1)

64h (T2)140h (T3)

16h (T4)

64h (T5)

AerobicAnaerobic

Page 22: Irene  Seco Manuel Gómez Alma Schellart Simon Tait

Main ResultsErosion Rate valuesComparison between tests with increasing length of periods of consolidation.

0 0.2 0.4 0.6 0.80.0

0.4

0.8

1.2

1.6

2.0

Applied shear stress (Tau_b) [N/m2]

eros

ion

rate

[g/

m2/

s]

0 0.2 0.4 0.6 0.80.0

0.4

0.8

1.2

1.6

2.0

Applied shear stress (Tau_b) [N/m2]

eros

ion

rate

[g/

m2/

s]

16h (T1)

64h (T2)140h (T3)

16h (T4)

64h (T5)

AerobicAnaerobic

drop in overall values of Erosion Rates as length dry-period increase

Page 23: Irene  Seco Manuel Gómez Alma Schellart Simon Tait

Main Results

0 0.2 0.4 0.6 0.80.0

0.4

0.8

1.2

1.6

2.0

Applied shear stress (Tau_b) [N/m2]

eros

ion

rate

(E) [

g/m

2/s]

0 0.2 0.4 0.6 0.80.0

0.4

0.8

1.2

1.6

2.0

Applied shear stress (Tau_b) [N/m2]

eros

ion

rate

(E) [

g/m

2/s]

Tests with the same consolidation period and different environmental ambience.

(T1) Anaerobic

(T4) Aerobic

64h consolidation period

16h consolidation period

(T2) Anaerobic

(T5) Aerobic

Page 24: Irene  Seco Manuel Gómez Alma Schellart Simon Tait

Main Results

0 0.2 0.4 0.6 0.80.0

0.4

0.8

1.2

1.6

2.0

Applied shear stress (Tau_b) [N/m2]

eros

ion

rate

(E) [

g/m

2/s]

0 0.2 0.4 0.6 0.80.0

0.4

0.8

1.2

1.6

2.0

Applied shear stress (Tau_b) [N/m2]

eros

ion

rate

(E) [

g/m

2/s]

Tests with the same consolidation period and different environmental ambience.

(T1) Anaerobic

(T2) Anaerobic(T4) Aerobic

(T5) Aerobic

64h consolidation period

16h consolidation period

Page 25: Irene  Seco Manuel Gómez Alma Schellart Simon Tait

Conclusions

Laboratory tests to estimate erosional resistance from highly organic sediment beds under storm runoff conditions

Improvements in prediction of in-sewer sediment transport loads

(Mediterranean conditions)

Page 26: Irene  Seco Manuel Gómez Alma Schellart Simon Tait

Conclusions

Environmental conditions influence over sediment-bed

nature and structure

Page 27: Irene  Seco Manuel Gómez Alma Schellart Simon Tait

Conclusions

Increase of erosional strength with depth

Increment of resistance against erosion (as consolidation dry-period lengthen and oxygen is available)

Environmental conditions influence over sediment-bed

nature and structure

Page 28: Irene  Seco Manuel Gómez Alma Schellart Simon Tait

Conclusions

comparing with results obtained with low-organic sediment and synthetic sediment (differences in sediment properties)

Lesser magnitudes of Critical Shear Stresses

Increase of erosional strength with depth

Increment of resistance against erosion (as consolidation dry-period lengthen and oxygen is available)

Environmental conditions influence over sediment-bed

nature and structure

Page 29: Irene  Seco Manuel Gómez Alma Schellart Simon Tait

Conclusions

Future investigations aimed to:

- asses critical shear stress in highly organic sediment beds

- analyse influence of temperature in dry-period

Page 30: Irene  Seco Manuel Gómez Alma Schellart Simon Tait

Concerned about pollution control

Thank you for your attention

Page 31: Irene  Seco Manuel Gómez Alma Schellart Simon Tait
Page 32: Irene  Seco Manuel Gómez Alma Schellart Simon Tait

Long dry-weather periodsIntense precipitaction events

Wet weather pollution from combined sewer systems

Particularities in the Mediterranean region climate in Spain:

0102030405060708090

100

0510152025303540Pm (mm)

mean T (°C)

aver

age

cum

mul

ative

Pr

ecip

itatio

n (m

m)

mea

n Te

mpe

ratu

re (°

C)

day-precipitation = 4 day/monthcumulative precipitation = 600 mm/year

(concentrater in spring and fall)average dry-period between rain: 11

daysMax. dry-period: 70 days (2010-2012)

Intense precipitation events following long dry-periods

≈ 40% rainfall registered P(mm)>10mm

Rain regime

Page 33: Irene  Seco Manuel Gómez Alma Schellart Simon Tait

Main results

Erosion of sediments from bed during tests were monitored in terms of Suspended Sediment concentration and related

with Erosion Rate

q : average Erosion Rate in a applied Shear Stress

step (tb) linked to Suspended Sediment Concentration (CSS)

V : water volume of the column over sediment sample

AS : surface area bed subjected to erosion