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2008 Michigan Academy Meeting - Holocene alluvial fill in a smallcolgan
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SMU A is a raised shrub bed with silty clay soil. It needs fertilizer and adding organic matter is recommended.
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This document analyzes the vertical distribution of groundwater contamination at the Tuba City Disposal Site in Arizona. It finds that while the current groundwater extraction system is effectively recovering contaminants, it may be excessively capturing uncontaminated water at depth. The report conducted aquifer isolation tests at two monitoring wells which found evidence of stratification and isolated contaminant plumes within the aquifer. It recommends further studies using downhole logging and multilevel sampling to better understand contaminant distribution with depth and potentially modify extraction well designs to minimize capture of clean water while still effectively remediating the site.
The document outlines a flood mitigation program for DKI Jakarta from 2012-2018 that includes structural projects like increasing the capacity of flood canals and normalizing rivers, as well as non-structural projects like an early warning system. Many of the structural projects are ongoing or planned, while some like increasing the capacity of the West and East Flood Canals have been completed. The program aims to reduce flood-prone areas through these structural and non-structural measures.
Presentation by Shannon & Wilson on some geotechnical aspects of the SR 532 Design-Build project in Washington State. Presented to the University of Washington Geotechnical Institute Graduate Student Society on 2/23/2011.
1) The document discusses stormwater retrofit assessments (SRA) conducted by Metro Conservation Districts to identify the most cost-effective locations for installing stormwater best management practices (BMPs).
2) An SRA involves delineating subwatersheds and catchments, analyzing land use and soil data, identifying potential BMP locations, modeling BMP designs and pollutant reductions, and ranking catchments based on performance metrics like cost per pound of pollutant reduced.
3) The assessments help direct limited funding and labor resources to projects that provide the greatest water quality benefits, in support of total maximum daily load implementation plans.
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This document discusses reconstructing past water levels in the Lake Michigan basin from sediment cores taken from embayed lakes. Lake level histories can be determined from geomorphic evidence like stranded shorelines and submerged forests, as well as sedimentological evidence like layers of sand, peat, marl, and gyttja in cores. Cores from small embayed lakes can preserve records of fluctuations in large lake levels over thousands of years. Comparing data from multiple sites allows development of a composite lake level curve for the region.
Reconstructing Water Levels in the Lake Michigan Basin from Embayed Lakes
Tete Bayou Presentation Ehab Edits
1. Drainage Assessment of Tete Bayou
Experience · Innovation · Results
PRESENTED TO
IBERIA PARISH CITY OF
GOVERNMENT NEW IBERIA
Engineers ∙ Surveyors · Environmental Consultants
2. Organizational Chart
Dr. Ehab Meselhe,
P.E.
Senior Hydraulic
Engineering
Consultant
Raymond Reaux, P.E.
Vice President – Engineering
Jeanne Arceneaux Robert Miller
M.S., E.I. MS, P.E.
Hydraulics Engineer Hydraulics Engineer
Dax Douet, P.E.
Engineering Project
Manager
Director
Justin Shaw
M.S., E.I. Ivan Diaz, P.E.
Drainage Engineer for City of New
Hydraulics Engineer Iberia
(33 Years)
3. General Scope of Work
• INVESTIGATE HISTORICAL FLOODING IN UPPER
PORTION OF TETE BAYOU
• EXAMINE REPETIVE LOSSES DUE TO OVERBANK
FLOODING
• DEVELOP POSSIBLE DRAINAGE IMPROVEMENT
SCENARIOS
• PERFORM FIELD SURVEYING
• ANALYZE IMPROVEMENT SCENARIOS THROUGH
HYDROLOGIC AND HYDRAULIC MODELS
• PRESENT QUANTITATIVE SOLUTIONS ALONG
WITH REPORT
5. Project Objectives
• Develop Numerical Models to Study Tete Bayou and Pharr Canal
• Examine Four Proposed Drainage Improvement Scenarios:
Scenario No. 1: Cleaning of Tete Bayou and the Pharr Canal;
Scenario No. 2: Scenario No. 1 + widening of the Pharr Canal intake, and removing
existing spoil banks along Tete Bayou;
Scenario No. 3: Scenario No. 2 + diverting flow from Tete Bayou to Bayou Teche
through a sub-surface box culvert system; and
Scenario No. 4: Scenario No. 1 + widening of Pharr Canal.
6. Analysis Timeline
• Contract Execution Date: January 19, 2011
• Field Survey Collection Start Date: February 8, 2011
• Numerical Model Development Start: February 21, 2011
• Agency Meeting with City and Parish Date: April 5, 2011
• Draft Report to City and Parish Date: July 22, 2011
7. Data Collected
• Survey Date Collected By C.H.
Fenstermaker & Associates, Inc.
• 1,589 Survey Points Collected
• Historical Hydrologic Data
• Land Use/Land Cover Maps
• Soil Type Maps
• LiDAR Data
• FEMA Flood Zones
8. FEMA Calibration
Existing 100-year Storm Event
15
10 CALIBRATION
CHECKS
Emile Verret Rd
Mullins Rd
Belle Place Olivier Rd
5
Elevation (ft)
Crochet Rd
0
100-year Rainfall Event
1% Chance that a 12.6 inch
-5 Rainfall over 24 hours will
Occur in a Given Year
Existing 100-yr WSE
Ground
FEMA BFE
-10
60,000 50,000 40,000 30,000 20,000 10,000 0
Main Channel Distance (ft)
9. December 2006 Storm Event Calibration
Tete Bayou at Belle Place Olivier Rd Facing South Tete Bayou near Candleglow Dr Facing East
Tete Bayou at Emile Verret Rd Facing East Tete Bayou at Emile Verret Rd Facing West
Estimated Rainfall Event
5.02” Rainfall (24 hours)
Approx. 3-yr., 24-hour Storm
10. December 2006 Storm Event Calibration
December 2006 Storm Event
15
10
Emile Verret Rd
Mullins Rd
Belle Place Olivier Rd
5
Elevation (ft)
Crochet Rd
0
Tete Bayou at Belle Place Olivier Rd Facing South
-5
December 2006 WSE
Ground
December 2006 High Water Mark
-10
60,000 50,000 40,000 30,000 20,000 10,000 0
Main Channel Distance (ft)
11. Scenario No. 1
Definition:
Channel Cleaning of Tete
Bayou and the Pharr Canal
11/XX
12. Scenario No. 1 – Water Surface Elevation Comparison
Existing - Scenario 1 Comparison
15
0.6’ Reduction in
Water Surface Elevation
10
Emile Verret Rd
Mullins Rd
Belle Place Olivier Rd
5
Elevation (ft)
Crochet Rd
0
10-year Rainfall Event
10% Chance that a 7.8 inch
Rainfall over 24 hours will
-5
Occur in a Given Year
10-yr Existing WSE
10-yr Scenario 1 WSE
Ground
-10 12/XX
60,000 50,000 40,000 30,000 20,000 10,000 0
Main Channel Distance (ft)
18. Scenario No. 2 – Results
Scenario No. 2 Inundation Area Comparison
Existing Conditions Scenario No. 2 Scenario No. 2 Scenario No. 2 Scenario No. 2
10-yr Inundation Area 10-yr Inundation 10-yr Reduction 10-yr Increase 10-yr Total Reduction
(acres) Area (acres) Area (acres) Area (acres) Area Reduction (acres)
6,390 6,209 289 108 181
Scenario No. 2 Flood Duration Comparison
Water Surface Elevation > 7’ NAVD 88
Bridge
Existing Scenario No. 2
Emile Verret Rd 24 hrs 14 hrs (42%)
Belle Place Olivier Rd 18 hrs 12 hrs (33%)
19. Scenario No. 3
Definition:
Channel Cleaning, Widening of the
Pharr Canal, Removing Spoil
Banks, and Diverting Flow From
Tete Bayou to Bayou Teche Through
a Sub-surface Box Culvert System
19/XX
20. Scenario No. 3 – Water Surface Elevation Comparison
Existing - Scenario 3 Comparison
15
1.7’ Reduction in
Emile Verret Rd Water Surface Elevation
10
Mullins Rd
Belle Place Olivier Rd
5
Elevation (ft)
Crochet Rd
Diversion
0
-5
10-yr Existing WSE
10-yr Scenario 3 WSE
Ground
-10 20/XX
60,000 50,000 40,000 30,000 20,000 10,000 0
Main Channel Distance (ft)
26. Scenario No. 4 – Results
Scenario No. 4 Inundation Area Comparison
Existing Conditions Scenario No. 4 Scenario No. 4 Scenario No. 4 Scenario No. 4
10-yr Inundation Area 10-yr Inundation 10-yr Reduction 10-yr Increase 10-yr Total Reduction
(acres) Area (acres) Area (acres) Area (acres) Area Reduction (acres)
6,390 5,977 463 50 414
Scenario No. 4 Flood Duration Comparison
Water Surface Elevation > 7’ NAVD 88
Bridge
Existing Scenario No. 4
Emile Verret Rd 24 hrs 9 hrs (62%)
Belle Place Olivier Rd 18 hrs 10 hrs (44%)
27. Scenario Comparisons and Costs
Flood Duration Flood Duration Inundation Inundation Total
Reduction at Reduction at Reduction Increase Planning
Scenario
Emile Verret Belle Place Olivier Area Area
(hrs) (hrs) (acres) (acres) Cost*
No. 1 9 6 220 197 $1,177,000
No. 2 10 6 289 108 $1,964,000
No. 3 19 8 619 64 $6,416,000
No. 4 15 8 463 50 $2,641,000
* It should be noted that these figures represent approximated cost only to be used for planning purposes.
28. Additional Analysis – Dredge Tete Bayou Mouth
Dredging Tete Bayou
15
Definition:
Dredging of Tete Bayou into Lake
Fausse Pointe
10
Emile Verret Rd
Mullins Rd
Belle Place Olivier Rd
5
Elevation (ft)
Crochet Rd
Negligible Water Surface
0
Elevation Change
-5
10-yr Existing WSE
Existing Ground
Dredged 10-yr WSE
Dredged Ground
-10
60,000 50,000 40,000 30,000 20,000 10,000 0
Main Channel Distance (ft)