Rock & Aggregate Drop Inlet Protection

Similar documents
[1] Performance of the sediment trap depends on the type of outlet structure and the settling pond surface area.

Construction Exits Rock pads

U-Shaped Sediment Traps

Type 1 System Sheet Flow Sandy Soils Type 2 System Concentrated Flow Clayey Soils Type 3 System [1] Supplementary Trap Dispersive Soils

Construction Exits Vibration grids

Coarse Sediment Traps

Sediment Weirs (Instream)

Chutes Part 5: Rock linings

Instream Sediment Control Systems

Stormwater Inlet Sediment Traps

Stormwater Outlet Sediment Traps

Low Gradient Velocity Control Short Term Steep Gradient Channel Lining Medium-Long Term Outlet Control Soil Treatment Permanent [1]

Rock Sizing for Small Dam Spillways

Rock Sizing for Waterway & Gully Chutes

Rock Sizing for Batter Chutes

Materials. Use materials meeting the following.

Sediment Trap. At multiple locations within the project site where sediment control is needed.

Suitable Applications Sediment traps should be considered for use:

Continuing Education Associated with Maintaining CPESC and CESSWI Certification

FOR PROJECTS INITIATED AFTER NOVEMBER 1, 2008 ITEM 716 EMBANKMENT EARTH OUTLET SEDIMENT TRAP

Orica Australia Pty Ltd Ammonium Nitrate Facility Upgrade

B805 TEMPORARY EROSION AND SEDIMENT CONTROL MEASURES - OPSS 805

Stone Outlet Sediment Trap

APPENDIX B WORKSHEETS & EXHIBITS

Sediment Trap. A temporary runoff containment area, which promotes sedimentation prior to discharge of the runoff through a stabilized spillway.

Rock Sizing for Drainage Channels

Erosion and Sediment Control Measures 2.7 Silt Fences

Rock Sizing for Multi-Pipe & Culvert Outlets

TPDES: Soil, Erosion and Sedimentation Methods

APPENDIX B DESIGN CRITERIA FOR TEMPORARY WATER QUALITY BMPS USED DURING CONSTRUCTION

Instream Erosion Control General

Erosion and Sediment Control Field Guide for Builders. Version 3, January 2013

Specifications Whitcomb Elementary School Demolition January 15, 2016

Use of Rock in Stormwater Engineering. Version 3, July 2017

Sediment Control Log (SCL)

WELCOME Lake Wabukayne OPEN HOUSE

Guide to the use of the Erosion and Sediment Control Evaluation Tool

The Mechanics Of Sediment Basin Operation

Sediment Control Practices. John Mathews Ohio Dept. of Natural Resources, Division of Soil and Water Resources

Rock Sizing for Bank Stabilisation

Independent Environmental Audit Erosion and Sediment Control

In-channel coarse sediment trap Best Management Practice

Track design and management

CHAPTER GEOLOGICALLY HAZARDOUS AREAS Applicability Regulations.

Gully Erosion Part 1 GULLY EROSION AND ITS CAUSES. Introduction. The mechanics of gully erosion

**Temporary Erosion Control**

Selected Site BMPs: Why s the Water Muddy? John C. Hayes, Ph.D., P. E. Biosystems Engineering Clemson University

Central Queensland Coal Project Appendix 4b Geotechnical Assessment. Environmental Impact Statement


Agenda. INDOT Office of Environmental Services. Describe Results of FHWA QAR. Landscape and Waterway Permitting Unit. Interviews Site Inspections

APPENDIX A: EROSION & SEDIMENT CONTROL FORMS

Template for Sediment and Erosion Control Plan General Instructions. Section Instructions

CONSTRUCTION EXIT SEDIMENT BARRIER

Erosion and Sediment Control A Field Guide for Construction Site Managers. Version 6, July 2017

Soil Erosion and Sediment Control. Basic Principles and Practices

MIDDLESEX COUNTY Department of Planning and Community Development P.O. Box 427, Saluda, VA Phone: Fax:

1.0 INSPECTION ANNUAL INSPECTION, JUNE 29, 2011 CARMACKS COPPER PROJECT, CARMACKS, YUKON. Dear Mr. West-Sells,

Woodford County Erosion Prevention Plan and Permit. Application #

APPENDIX G APPENDIX G SEDIMENT CONTAINMENT SYSTEM DESIGN RATIONALE

FINAL REPORT NO.54. Erosion and Sediment Control Plan - Coastal Reclamation. Tauranga City Council. Private Bag Tauranga 16 August

TABLE OF CONTENTS LIST OF TABLES. Page

Storm Sewer Design [2]

1 PROJECT BACKGROUND. August 14, Alberta Transportation Central Region #401, Street Red Deer, Alberta T4N 6K8

October 26, Ms. Aimee Zack Canadian Pacific 120 S. Sixth Street Suite 900 Minneapolis, Minnesota 55402

STRUCTURAL STABILITY ASSESSMENT

3.18 GEOLOGY AND SOILS

Standards for Soil Erosion and Sediment Control in New Jersey May 2012

Chapter 7 Mudflow Analysis

Sediment Capture in Pervious Concrete Pavement tsystems: Effects on Hydrological Performance and Suspended Solids

HISTORY OF CONSTRUCTION FOR EXISTING CCR SURFACE IMPOUNDMENT PLANT GASTON ASH POND 40 CFR (c)(1)(i) (xii)

1. PROJECT BACKGROUND. July 18, Alberta Infrastructure & Transportation Central Region #401, Street Red Deer, Alberta T4N 6K8

Long Valley Meadow Restoration Project

STREUVER FIDELCO CAPPELLI, LLC YONKERS DOWNTOWN DEVELOPMENT PHASE 1. DRAFT ENVIRONMENTAL IMPACT STATEMENT For: PALISADES POINT

Crows Landing Naval Base Easement

ROCK EXCAVATION (GRADING) OPSS 206 INDEX

CCR Rule Annual Inspection Report (cont.) 2

Stream Geomorphology. Leslie A. Morrissey UVM July 25, 2012

This report was prepared by Klohn Crippen Consultants Ltd. for Alberta Transportation Central Region under Contract No. CE053/2000.

Why Geomorphology for Fish Passage

3.12 Geology and Topography Affected Environment

CPESC Syllabus Australasia

December 11, 2006 File:

January 16, Re: Soo Line Dump Site 2018 Annual Soil Cover Inspection. Dear Mr. Nichols:

Culvert and Pipe Phasing

January 17, 2008 File:

Chapter 7 Mudflow Analysis

Introduction and Organization of Instructions The following is a brief outline for use the skimmer, how to size and shape the basin, how to construct

Modeling Great Britain s Flood Defenses. Flood Defense in Great Britain. By Dr. Yizhong Qu

Subject Name: SOIL AND WATER CONSERVATION ENGINEERING 3(2+1) COURSE OUTLINE

Provide sediment tubes for ditch check and Type A inlet structure filter applications that meet the minimum performance requirements of Table 1.

The results of KCB s site inspection observations and our recommendations for further work are presented herein.

Template for Sediment and Erosion Control Plan General Instructions

Type 1 System Sheet Flow Sandy Soils Type 2 System Concentrated Flow Clayey Soils Type 3 System Instream Works Dispersive Soils

NRCS - THUNDER ROAD #2, TRIBUTARY TO QUILEUTE RIVER CULVERT REMOVAL AND REPLACEMENT PLAN CLALLAM COUNTY, WA., WRIA: 20, SITE:

Erosion and Sedimentation Basics

Appendix E Guidance for Shallow Flooding Analyses and Mapping

Location Restriction Demonstration

Degradation Concerns related to Bridge Structures in Alberta

SILT FENCE EFFECTIVENESS

D. B. G R A Y E N G I N E E R I N G I N C.

Transcription:

Rock & Aggregate Drop Inlet Protection SEDIMENT CONTROL TECHNIQUE Type 1 System Sheet Flow Sandy Soils Type 2 System [1] Concentrated Flow Clayey Soils Type 3 System Supplementary Trap Dispersive Soils [1] A Type 2 sediment containment system may be formed if the sediment trap is designed in accordance with the guidelines for Rock Filter Dams. Symbol Photo 1 Rock and aggregate drop inlet protection located with dual carriageway Photo 2 Rock and aggregate drop inlet protection Key Principles 1. The critical design parameter is the surface area of the settling pond that surrounds the stormwater inlet. 2. The purpose of the aggregate is to control the rate of flow entering the stormwater inlet (thus allowing the formation of a settling pond around the inlet), and to provide limited filtration of flows passing through the aggregate. 3. During low flows, the trapping of coarse sediment is achieved through gravitational settlement within the settling pond, while the finer sediments are filtered by the aggregate filter. 4. During high flows, sediment trapping is achieved primarily through gravitational settlement within the settling pond that forms around the drop inlet. 5. If insufficient pond surface area is provided around the inlet, then the sediment trapping efficiency will be reduced and settled sediment will quickly block the aggregate filter. Design Information Maximum catchment area 0.4ha on sites with low sediment runoff, or 0.1ha on sites with expected high sediment runoff yields. Recommended maximum height of 600mm and minimum height of 300mm. Recommended minimum top width of the main support embankment of 300mm excluding the thickness of the aggregate filter layer. Catchments & Creeks Pty Ltd Version 2-2010 Page 1

Temporary flow control bunds may be required to control the depth and extent of ponding and to prevent water bypassing the inlet (Figure 5). The crest of these banks should be at least 150mm above the weir crest of the main support rock. Photo 3 Placement of main support rock Photo 4 Rock and aggregate drop inlet protection located with dual carriageway Where necessary, formation of the settling pond may require excavation of material from around the inlet. Figure 1 Rock and aggregate drop inlet protection Figure 2 Rock and aggregate drop inlet protection shown with optional sediment collection trench Catchments & Creeks Pty Ltd Version 2-2010 Page 2

Figure 3 Typical cross-section of rock and aggregate drop inlet protection Figure 4 Placement of aggregate Figure 5 Rock and aggregate drop inlet protection shown with flow control bund to limit the extent and depth of ponding Catchments & Creeks Pty Ltd Version 2-2010 Page 3

Description Rock and aggregate drop inlet protection systems consist of a ring of larger support rock placed around the stormwater inlet, with an outer layer of aggregate used as a filter medium. The crest of the structure acts as a spillway to regulate the height of ponding, and to prevent water from bypassing to undesirable locations, or from causing flooding problems. Purpose Used to remove and retain sediment from stormwater runoff before it enters the underground drainage network. Most commonly used around drop (field) inlets, but can also be used on culvert inlets and pipe inlets. Rock and aggregate drop inlet sediment traps perform two main functions: during minor storms, the partially sediment-blocked aggregate filters sediment from dirty water; during high intensity storms, the aggregate embankment causes storm runoff to pond around the inlet allow the settlement of coarse sediments. Limitations These types of sediment traps provide limited turbidity control. Limited to catchment areas around 0.4ha. Not suitable for inaccessible areas where regular maintenance cannot be performed on the sediment trap. The trap can become an undesirable traffic safety hazard. Advantages Large rock and aggregate drop inlet protection systems can be extremely rugged and thus difficult to damage or vandalise. Relatively inexpensive and usually requires little site disturbance. Can assist in reducing sediment build-up in stormwater drains and culverts, thus reducing the cost of post storm clean-up. High sediment concentrations in the stormwater runoff can quickly block the aggregate filter layer. Common Problems Drainage problems can occur if the aggregate fully blocks with sediment. Filtration of sediment by the aggregate filter may not be effective until partial sediment blockage of the aggregate occurs. Special Requirements When used on public roads, the sediment trap must not be allowed to cause a traffic safety problem. Allowance should always be made for potential bypass flows. The maximum depth of ponding around the structure must be controlled to prevent water from bypassing to undesirable locations, or from causing flooding problems. Where necessary, the sediment trap may need to be partially surround by a flow control bund to control the depth and extent of ponding (Figure 5). Location Placed around drop (field) inlets where the catchment area is relatively large. Typically used within the median of dual carriageways. Site Inspection Check the flow path of potential bypass flows. Look for potential flooding or traffic safety problems. Ensure that any water that bypasses the inlet will not cause flooding problems. Check the maximum allowable pond depth. Check the height and stability of the flow control bund. Disadvantages Drainage problems can occur if poorly designed or poorly maintained. Catchments & Creeks Pty Ltd Version 2-2010 Page 4

Materials Primary core (support) rock: well graded, hard, erosion resistant rock, minimum size as specified in the approved plan, but not less than 200mm. Filter medium: 15 to 25mm clean aggregate. Installation 1. Refer to approved plans for location and dimensional details. If there are questions or problems with the location, dimensions or method of installation contact the engineer or responsible onsite officer for assistance. 2. Ensure that the installation of the sediment trap will not cause undesirable safety or flooding issues. 3. Using minimum 200mm rock, construct an embankment around the stormwater drain, minimum height 300mm with a minimum top width of 300mm. Internal batter slopes shall be no steeper than 3:1(H:V) and the toe of the batter no closer than 300mm from the edge of the stormwater inlet. The outer batter shall be no steeper than 2:1(H:V). 4. The top of the rock embankment should operate as a spillway to control the maximum pond height. Ensure the maximum pond height will not cause a safety hazard, including undesirable flooding of an adjacent property or roadway. 5. Place a minimum 300mm thick layer of filter aggregate over the outer slope of the rock embankment. 6. Where necessary, establish a flow control bund(s) to appropriately manage the settling pond depth and movement of bypass flows. 7. Take all necessary measure to minimise the safety risk caused by the structure and to prevent unsafe entry into the stormwater inlet. Maintenance 1. Inspect the sediment trap after each runoff-producing rainfall event and make repairs as needed to the sediment trap and associated flow control bunds. 2. Remove collected sediment and dispose of in a suitable manner that will not cause an erosion or pollution hazard. 3. If flow through the sediment trap is reduced to an unacceptable level, the aggregate filter should be replaced. If a greater degree of water treatment (filtration) is required, geotextile filter fabric may be placed over the aggregate. 4. Remove sediment and restore original sediment storage volume when collected sediment exceeds one-third of the specified storage volume. 5. Sediment deposits should be removed immediately from any area where it is likely to cause a safety risk. Removal 1. When the up-slope drainage area has been stabilised, remove all materials included deposited sediment and dispose of in a suitable manner that will not cause an erosion or pollution hazard. 2. Bring the disturbed area to a proper grade, then smooth, compact and stabilise and/or revegetate as required. Catchments & Creeks Pty Ltd Version 2-2010 Page 5