Point Break for the WSUD Asset Wave. Presentation by Brad Dalrymple

Similar documents
Construction and Establishment Guidelines: Swales, Bioretention Systems and Wetlands Version 1.1, April 2010

Waterways and wetlands investigations

Deemed to Comply Solutions Stormwater Quality Management (South East Queensland). Version 1.0, May

AGENDA 2015 Community Stormwater Event

C-12. Dry Pond. Design Objective

WAKE COUNTY STORMWATER MAINTENANCE CHECKLIST

Raingardens and Bioretention Tree Pits MAINTENANCE PLAN. EXAMPLE June 2008

Kearney Post-Construction Stormwater Program

Stormwater Management Techniques WMPF LAND USE TRAINING INSTITUTE MARCH 14, 2018

Guide to the Cost of Maintaining Bioretention Systems. Version 1, February 2015 Healthy Waterways Initiative

Hopwood Motorway Service Area, Worcestershire

Homeowners Guide to Stormwater BMP Maintenance

Just The Basics: Illicit Discharge. What does it mean to me?

Green City, Clean Waters

Monitoring Hydraulic Conductivity and Soil Contamination in SEQ Bioretention Systems Constructed in 2006

Infiltration basin under normal conditions, with generous grassed area for water soakage (Source: WSUD in the Sydney Region)

BIOMOD SYSTEM. Modular Bioretention/Biofiltration System BIORETENTION / BIOFILTRATION. Working in Harmony with Nature

Maintaining Your Neighborhood Stormwater Facilities How to identify stormwater facilities and keep them working

INTRODUCTION TO THE ADAPTING TO RISING TIDES EXISTING CONDITIONS AND STRESSORS REPORT

Water Sensitive Urban Design Guidelines

Maintaining Your Neighborhood Stormwater Facilities

2017/18 Financial Year Living Rivers Funded Projects

DRAFT DESIGN CRITERIA STORMWATER TREATMENT STANDARDS CITY OF OVERLAND PARK

Urban Stormwater: Best Practice Environmental Management Guidelines. CSIRO This electronic edition published by CSIRO PUBLISHING, 2006.

A Visual Guide to Assessing, Inspection and Maintaining LID Practices

Sustainable Urban Drainage Systems. Diederik Rousseau Tineke Hooijmans

2012 Saginaw Bay Watershed Conference

JCCC Campus Stormwater Project: Retrofitting Yesterday s Parking Lots With Today s Best Management Practices

What is YOUR biggest challenge in stormwater control measure accounting/planning?

Appendix F Construction phase management

City of Hume Planning Scheme Amendment C207. Statement of Expert Evidence Provided to Planning Panels Victoria

POLICY SRT/D4 STORMWATER MANAGEMENT

Selecting Appropriate Stormwater Control Measures for Your Development Project

4. CONCEPT PLAN DEVELOPMENT

PLANNING AND DESIGN OF PUTRAJAYA STORMWATER MANAGEMENT SYSTEM

Challenges of Implementing $270m of Regional Water Quality Infrastructure

LID Performance and Risk Assessment Program

A Business Case for Best Practice Urban Stormwater Management: Case Studies

Dissecting Rainwater Pump Energy Use in Urban Households

COMMUNITY DEVELOPMENT DEPARTMENT POLICY DRAINAGE FOR RESIDENTIAL PROJECTS WITH ONE OR TWO UNITS REVISED JANUARY 4, 2018

Presented By: Matt Roberts and Cass Chapman The University of Minnesota Law School Environmental Sustainability Clinic

Green Star Change in Ecology Calculator Guide

The Application of an Integrated Monitoring Plan on Stormwater Control Measures

Green Urban design for Can Tho city: Where to start?

Low Impact Development. Charlene LeBleu Auburn University Landscape Architecture (334)

New Development Stormwater Guidelines

Inspection Protocols for Maintaining and Verifying LID Practices

New Berrima and Medway Villages


Vegetated Filter Strips and Buffers

City of Yelm. Public Works Department. July 29, Re: Stormwater Maintenance Re-Inspection Results

Conservation Landscaping Spot Check Inspection Checklist

When planning stormwater management facilities, the following principles shall be applied where possible.

Map Reading 201: Where Does the Water Go?? Map Reading Map Reading 201. Interconnected Systems

Inspection and Maintenance of Stormwater Best Management Practices

ENVIRONMENTAL STEWARDSHIP, COMMITMENTS, AND COMPLIANCE

Introduction to Low Impact Development. Fred Milch. East Central Florida Regional Planning Council

Stormwater Low Impact Development - A Natural Solution

BIORETENTION CELLS. Green Infrastructure For Stormwater Management WHAT ARE BIORETENTION CELLS? WHERE ARE BIOCELLS INSTALLED?

Regional Stormwater Management Program

Chapter 1 Introduction

Water sensitive urban design

Figure 1. Bioswale along roadside. Photo courtesy of CalTrans. Figure 2. Diagram of typical bioswale (adapted from UDFCD 1999)

Rain Gardens - A Local Government Perspective

Beyond Rain Gardens Advancing the Use of Compost for Green Infrastructure, Low Impact Development, & Stormwater Management

Infiltration / Soakaway Systems CASE STUDY PROJECTS

Framework for Post-Construction SMP Program Management

Inventory and Assessment of Stormwater Infrastructure

Tips for Maintaining and Enhancing Stormwater Management Areas

Green Stormwater Infrastructure Maintenance Manual

Rain Garden Site Selection and Design. Andrew Anderson, E.I.T. Extension Associate Engineer Biological & Agricultural Engineering NCSU

SUPPORTING DOCUMENT STORMWATER POLLUTION PREVENTION PLAN (SWPPP) NARRATIVE

Draft Rhode Island Stormwater Design and Installation Standards Manual

Ben Powell, Clemson Extension

University of Southern Queensland. Faculty of Engineering and Surveying

Simplifying the design of bioretention system to minimise complexity, cost and carbon footprint - forebays as a case study

Bioretention. Matt Scharver Northeast Ohio Regional Sewer District. #ProjectCleanLake

Cost Effective Low Impact Development

Sutton Forest. Development Control Plan

OPERATION & MAINTENANCE

APPENDIX C: STORMWATER CONTROL PLAN

4. Contractor (and subcontractors if applicable) certification statement(s)

EROSION PREVENTION BMP SUGGESTED USES MATRIX

Monitoring Flow and Quality for Stormwater Control Measures

Project Applicant Checklist for NPDES Permit Requirements SAN MATEO COUNTYWIDE STORMWATER POLLUTION PREVENTION PROGRAM

KENT COUNTY STORMWATER MAINTENANCE DISTRICT STORMWATER BMPs MAINTENANCE TASKS AND RESPONSIBILITIES GUIDANCE DOCUMENT BIO-RETENTION FACILITIES

Structural Stormwater Best Management Practices

Misunderestimating Maintenance: An empirical approach to quantify maintenance expectations for BMPs

92 Minnesota Stormwater Manual

Use of Best Management Practices

NON-PRIORITY PROJECT WATER QUALITY PLAN (NPP)

Key elements : Filter Strips must be designed within parameters required by the Fort Wayne s Development Standards/Criteria Manual.

Evaluating Low Impact Development Practices for Stormwater Management on an Industrial Site in Mississippi

Concreteville, CT. March 10, 2004

Appendix D - Technical Design Criteria for BMPs

Evaluating Urban Stormwater Retrofits in the SE US Coastal Plain

STORMWATER REPORT FOR WALMART SUPERCENTER STORE # SIOUX FALLS, LINCOLN COUNTY, SOUTH DAKOTA BFA PROJECT NO

The Zero Additional Maintenance Water Sensitive Urban Design

Urban Water Management and Soils (ESRM 311 & SEFS 507)

EXECUTIVE SUMMARY Greater Milwaukee Watersheds Stormwater Report. Background and Significance

Transcription:

Point Break for the WSUD Asset Wave Presentation by Brad Dalrymple Stormwater Australia Conference 10 October 2018

Intro

The WSUD Asset Wave Planning & Development Approval Construction & Establishment Handover Operation & Maintenance Adapted from Leinster et al (2010)

Objectives Collate and review stormwater control measure (SCM) asset condition data from a range of sources within Australia Provide recommendations for the future management of SCMs

Methods

Location SCM Asset Information Source Moreton Bay Regional Council local government area, Queensland Un-named Council A in Queensland Un-named Council B in Queensland Un-named Council C in Sydney, NSW Un-named Council D in Sydney, NSW Un-named Council E in NSW Condition assessments on 318 Council-owned bioretention systems in the Moreton Bay Region), undertaken in August to October 2017. Condition assessments on 213 Council-owned vegetated SCMs, including 12 swales, 70 sediment basins, 44 wetlands, 5 infiltration basins, and 82 bioretention basins, undertaken in September and October 2016. Condition assessments on 52 Council-owned gully baskets, undertaken in June 2018. Condition assessments on 30 Council-owned SCMs, including 5 bioretention systems, 4 GPTs and 21 gully baskets, undertaken in March 2018. Condition assessments undertaken on 291 Councilowned primary treatment devices (e.g. gross pollutant traps), undertaken in November 2017. Condition assessments undertaken on 236 Councilowned gully baskets, undertaken in September 2017. Jonathon Whitcombe (MBRC, 2018: Pers.Comm.) Un-named Council (2018: Pers.Comm.) Study authors Study authors Study authors Study authors

Condition Assessment Ratings Rating Condition Description Response 1 Very Good The asset is in very good condition and fully functioning with no visible degradation. 2 Good The asset is in good condition and fully functioning with some minor visible degradation. 3 Fair The asset is in fair condition with some loss of function and significant visible degradation. 4 Poor The asset is in poor condition with major loss of function and/or asset failure is imminent. 5 Very Poor The asset is in very poor condition with no function and/or has failed. Routine maintenance only Extra maintenance as required Significant maintenance required to address defects Further investigation & rectification required Further investigation & rectification/renewal required Source: Whitcombe (MBRC, 2018: Pers.Comm.)

Results

MBRC

MBRC Summary of Defects

Un-named Council A in Queensland

Un-named Council A in Queensland Common defect = excessive sediment accumulation

Un-named Council A in Queensland Common defect = lack of vegetation in macrophyte zone

Un-named Council A in Queensland

Un-named Council A in Queensland Common defect = poor drainage/ infiltration (extended ponding)

Un-named Council A in Queensland

Un-named Council B in Queensland Most common defect = basket simply not present (7 out of 52)

Un-named Council C in NSW Vast majority of baskets át capacity 29 of 30 assets with defect 4 out of 5 bioretention = poor (with minimal vegetation coverage, and other defects)

Un-named Council D in NSW

Un-named Council D in NSW Key findings: 66 (22%) of the 291 SCMs were identified as being in a poor or very poor condition Of the 12 litter booms, 8 could not be located (and had likely washed downstream in a high flow event) Of the 95 accessible sites identified as having gully baskets present, the vast majority did not have a gully baskets present Of the wet-sump GPTs inspected, common defects included: Structural defect causing a bypass of incoming flows (and pollutant loads) downstream receiving environment causing backwater in/partial submersion of asset GPT storage was over capacity (i.e. full of accumulated material) for many wet sump GPTs

Un-named Council E in NSW

Un-named Council E Summary of Defects

Published SCM Condition Data in Australia Location: Melbourne (Un-named Council A) Assets: 18 SCMS 16 bioretention, 1 tree pit, 1 wetland Source: Thomas et al (2016) Key findings: 76% of all SCM assets with a poor rating (on a scale of good, fair and poor ) Maintenance practices (or lack-there-of) = the lead reason for the high proportion of assets being in poor condition

Published SCM Condition Data in Australia (Cont d) Location: Melbourne (Un-named Council B) Assets: 76 SCMS 4 sediment basins, 16 sediment basin-wetland systems, 20 bioretention, 6 car-park swales, 4 retarding basins with wetlands, 3 ponds, 23 GPTs 16 bioretention, 1 tree pit, 1 wetland Source: Thomas et al (2016) Key findings: 38% of all SCM assets with a poor rating Maintenance identified as being responsible for the highest proportion of poor condition ratings 89% of assessed GPTs were also identified as full or overflowing

Published SCM Condition Data in Australia (Cont d) Location: Melbourne (Un-named Council C) Assets: 83 SCMS 13 infiltration, 64 rain gardens, 5 swales, 1 wetland Source: Thomas et al (2016) Key findings: 28% of all SCM assets had a poor rating Maintenance category seeing the highest proportion of assets rated as poor Maintenance assessment category also produced the lowest proportion of assets with a rating of good

Published SCM Condition Data in Australia (Cont d) Location: Penrith City Council Assets: 88 GPTs 74 trash racks, 14 underground GPTs Source: Weaver et al (2016) Key findings: 46% of SCM assets being either in poor condition (working at less than 20%) or non-operational 52% requiring structural works/ major works or decommissioning/ replacement.

Key Findings A large proportion of the SCM assets that had a condition assessment rating were in a poor or very poor condition, requiring significant rectification works to address the problem(s) with the asset A lack of maintenance activities is the key reason for these poor (or very poor) condition ratings

Study Limitations Condition assessment rating methodologies utilised in this study (and literature review) are not consistent Condition rating does not necessarily correlate with stormwater treatment performance (or service delivery) and/ or operational life or life cycle costs of the SCM Study only includes results for SCMs that have had a condition assessment undertaken

Conclusions & Recommendations

The WSUD Asset Wave Planning & Development Approval Construction & Establishment Handover Operation & Maintenance Adapted from Leinster et al (2010)

The WSUD Asset Wave Planning & Development Approval Construction & Establishment Handover Operation & Maintenance Rectification?

The WSUD Asset Wave Planning & Development Approval Construction & Establishment Handover Operation & Maintenance Rectification?

The WSUD Asset Wave Planning & Development Approval Construction & Establishment Handover Operation & Maintenance Rectification?

The WSUD Asset Wave Future? Planning & Development Approval Construction & Establishment Handover Operation & Maintenance Rectification?

The WSUD Asset Wave Future?? Planning & Development Approval Construction & Establishment Handover Operation & Maintenance Rectification?

Business as Usual Consequences Significantly reduced benefits of existing SCMs Reduced waterway health Poor decision-making Higher life cycle costs

Recommendations Develop and implement an evidence-based approach to stormwater management Standardised condition assessment inspection protocol for SCM and other WSUD assets (for both government and privately owned assets). Standardised monitoring protocols for asset performance (or level of service) and life cycle costs. Regulatory authorities (e.g. local government) should also consider making appropriate evaluation, monitoring and maintenance of SCMs (and associated reporting) a legislative requirement

Thank you Charles Coathup Ben Penhallurick James Coathup Jonathon Whitcombe Personnel from un-named Councils