Municipal Separate Storm Sewer System - nyc.gov · MS4 Permit and Stormwater Management Program...
Transcript of Municipal Separate Storm Sewer System - nyc.gov · MS4 Permit and Stormwater Management Program...
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Agenda
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1. MS4 Permit and Stormwater Management Program Overview
2. Media Campaign Update: Don’t Trash Our Waters
3. Bag Challenge
4. SWMP Chapter 11 - Control of Floatable and Settleable Trash and Debris
Overview
a. Loading Rate Draft Work Plan
5. Next Steps
6. Adjournment
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MS4 Permit and Stormwater Management Program
MS4 Outfalls: 357
MS4 Drainage Area:
84,300 ac; 40% of the City
In August 2015 the State
issued the City an MS4
Permit which seeks to
manage urban sources of
stormwater runoff to
protect overall water
quality and improve water
quality in impaired waters.
In response, the City is
developing a Stormwater
Management Program
(SWMP).
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Stormwater Management Program (SWMP)
1. Public Education and Outreach
2. Public Involvement/Participation
3. Mapping
4. Illicit Discharge Detection and Elimination
5. Construction Site Stormwater Runoff Control
6. Post-Construction Stormwater Management
7. Pollution Prevention/Good Housekeeping for Municipal Operations and Facilities
8. Industrial and Commercial StormwaterSources
9. Control of Floatable and Settleable Trash and Debris
10. Monitoring and Assessment of Controls
11. Reliance on Third Parties
12. Recordkeeping
13. Annual Reporting
14. Annual Report Certification
Stormwater Management Program (SWMP): is a comprehensive plan
that describes how the City will address pollution in stormwater
discharges through Best Management Practices (BMPs) and other
controls.
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Media Campaigns
Clean Streets = Clean Beaches B.Y.O. Campaign
Don’t Trash Our Waters Talk Trash New York
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Don’t Trash Our Waters - Bronx River
Red
markers –
Bus
Shelters
with the
Don’t
Trash Our
Waters
Posters
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Don’t Trash Our Waters- Coney Island Creek
Red –
Bus
Shelters
Blue –
Large
Signs
Green –
Subway
Turnstiles
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Don’t Trash Our Waters- Coney Island Creek
Raising Awareness with an event at New York Aquarium.
• Gave away 1,000 free tickets to the Aquarium
• Gave away 200 water bottles
• Gave away 100 reusable bags
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Don’t Trash Our Waters
Reaching New Yorkers when they are online
• During first iteration of social campaign, DEP had 872,460 impressions and 14,624 link clicks to
nyc.gov/trashfreewaters
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The Bag Challenge
The Bag Challenge:
The Bag Challenge is designed to target upstream prevention by encouraging behavior changes in
both retailers and consumers. This program will challenge participating supermarkets and grocery
stores to reduce their distribution of single-use bags by 5% over the course of the challenge.
The Bag Challenge aims to educate the supermarket industry and the communities they serve on how
their land-based operations and decisions directly impact surrounding waterbodies by utilizing a
combination of:
• Public outreach
• Market-based research
• Creative messaging
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The Bag Challenge Components
Component 1: The Challenge
Who?
What?
Where?
Why?
How?
The Bag Challenge targets Grocery Stores & Supermarkets
This program will target stores located within the Jamaica Bay Watershed, an
important ecological resource that is currently listed as impaired for floatables.
This program will challenge participating supermarkets and grocery stores to
reduce their distribution of single-use bags by 5% over the course of the challenge
The Bag Challenge aims to raise awareness and educate the supermarket
industry and consumers how our land-based actions directly impact water quality.
To achieve our stated goals, The Bag Challenge will utilize a combination of
workshops, outreach, creative branding and messaging to raise awareness and
educate communities. Additionally, the program will conduct behavioral research to
collect data and establish meaningful metrics for measuring success.
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The Bag Challenge Components
• Surveys, interviews and observational
research will allow us to gain insight
into the number of people using
reusable bags versus those using
single-use bags, as well as overall
consumer trends.
• This will provide us with a deeper
understanding of what drives
consumer decisions.
• A consultant will design an
appropriate methodology for
collecting data over the
course of the challenge.
• As the program progresses, these
factors will continue to be monitored
to identify whether or not there are
changes in behavior.
• Data, both quantitative and
qualitative, will be collected and
analyzed at the conclusion of The Bag
Challenge to help determine the
effectiveness of the program.
Component 2: Behavioral Research
Research Design Data Collection Data Analysis
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Chapter 11 Outline
Chapter 11: Control of Floatable and Settleable Trash and Debris
1. Existing Programs
2. Floatable and Settleable Trash and Debris Management Program
Development
1. Loading Rate Work Plan
2. Evaluation of Existing Programs
3. Review of Available Technologies and Controls
4. Methodology for Selecting Technologies and Controls
3. Media Campaign
4. Measurable Goals and Program Assessment
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Floatables Loading Rate Work Plan
Timeline
August 1, 2017
August 1, 2018
Within 3 months
of DEC approval
Within 2 years of
DEC approval
Within 3 years of
commencement of
study
Submit a draft work plan for determining amount of floatables discharged
from the MS4 to waterbodies listed as impaired for floatables for DEC
review and approval.
Propose a schedule to determine the floatables loading rate from the MS4
to waterbodies listed as impaired for floatables in the MS4 areas.
Submit a final proposed work plan for determining floatables loading rate,
to be included in the SWMP.
Commence a study to determine the floatables loading rate using the
approved work plan.
Complete study to determine the floatables loading rate using the
approved work plan.
Draft Work Plan
Draft Work Plan Milestones:
• Submitted to New York State DEC on
August 1, 2017
• Posted online on August 1, 2017
• Presented to Public on October 4, 2017
• Public Comments are due by Monday
October 16, 2017 to [email protected]
• Final Work Plan due with the SWMP on
August 1, 2018
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Overview of Draft Work Plan
Review of Methodologies to
Determine Loading Rates
• Los Angeles, CA
• Baltimore City & County, MD
• Washington, DC
• San Francisco, CA
• New York, NY
Advantages and Disadvantages of
Different Methodologies
• Metrics
• Factors
Proposed Methodology for NYC
• Overview
• Justification
• Implementation
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Review Of Other Municipalities
Factors Affecting Loading Rates Field Monitoring Overview
Municipality
Land
Use
Median
Income
Street
Sweeping Rainfall
Field
Sampling Metric
Site
Type
Los Angeles, CA Yes No No No Yes Volume
Catch
Basin
Baltimore City and
County, MD Yes No No Yes Yes Weight Outfall
Washington, DC Yes No No Yes Yes Weight Outfall
San Francisco, CA Yes Yes Yes Yes Yes Volume
Catch
Basin
Select representative sites
Conduct field monitoringAnalyze data to calculate
loading rate
Details
General Strategy
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Findings from Past NYC Studies
o Street-litter level
o Street sweeping (frequency and efficiency)
o Rainfall
o Length of curb in the catchment
o Catch basin hoods
o Presence of booms or nets
Key Factors
DEP has conducted multiple field studies between 1993 and 2005 to
understand the factors affecting floatables loads in NYC.
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Advantages & Disadvantages
Litter Generation RatesMetric
Weight
Relatively easy to measure
More susceptible to skewing
Volume
Relatively easy to measure
Less susceptible to skewing
Rainfall
Not Included
Simpler analysis
Doesn’t establish relationship with
rainfall
Included
More complex analysis
Establishes relationship with rainfall
Land Use
Readily available information
Not a great proxy
Requires single/dominant land use
Land Use Plus
Readily available information
Better proxy
Requires single/dominant land use
Observed Litter Levels
Not always readily available
Actual litter data
Does not require single/dominant
land use
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Street Catch Basin Sewer Waterway
PedestriansVehicles
Improper Trash Management
Street Sweeping
PedestriansVehicles
Catch Basin Cleaning
In-line and End-Of-Pipe
Capture
Sources
Proper Disposal
In-Water Capture
Overview of Proposed Methodology
DEP has proposed a hybrid approach that combines field
measurements used by other municipalities and existing DEP floatables
model
Measure floatables
entering MS4
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Overview of Proposed Methodology
Select representative sites
Conduct field monitoringAnalyze data to calculate
loading rate
General Strategy
o Based on prior
knowledge of key
factors affecting
floatables loads in
NYC
o Sample at manholes
to isolate load to
waterways from the
MS4
o Use existing model to
check data and
calculate loading rate
Factors Affecting Loading Rates Field Monitoring Overview
Litter
Level Land Use
Catch
Basins
Street
Sweeping Rainfall
Field
Sampling Metric Site Type
Yes Selectively Yes Yes Yes Yes Volume
Catch
Basin
Details
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Selecting Representative Catch Basins
Major characteristics determining
floatables loading rate for a catch
basin are:
• Catch basin attributes
o hood vs. no hood
• Tributary characteristics
o street litter levels
o street cleaning frequency
Additionally, NYC will select catch
basins along arterial highways and
within parks. These catch basins may
have different loading rates from DEP
catch basins based on:
o Design
o Land use
o Maintenance
Category
Catch Basin
Attributes
Street
Litter
Level
Street
Sweeping
Frequency
Sites per
Category
1 Hooded High High 3
2 Hooded High Med 3
3 Hooded High Low 3
4 Hooded Med High 3
5 Hooded Med Med 3
6 Hooded Med Low 3
7 Hooded Low High 3
8 Hooded Low Med 3
9 Hooded Low Low 3
10 Unhooded High High 3
11 Unhooded High Med 3
12 Unhooded High Low 3
13 Unhooded Med High 3
14 Unhooded Med Med 3
15 Unhooded Med Low 3
16 Unhooded Low High 3
17 Unhooded Low Med 3
18 Unhooded Low Low 3
19 Arterial Highway Typical N/A 3
20 Within Parks Typical N/A 3
Total # of catch basins sites to monitor: 60
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Monitoring Representative Catch Basins
• Duration: ~7 months capturing seasonality
• Floatables Metric: volume
• Rate Metric: annual average
• Method: baskets located in manholes
• Sampling Frequency: weekly
• Estimated Number of Samples: ~1680
Monitoring Details
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Analyzing Data and Calculating Loading Rate
Establish unit loading rates by catch basin category, normalized by
catchment size and rainfall frequency/amount
Ensure that results are scalable and logical
– This could include application of existing floatables model
Establish conditions for calculation of loading rate:
– Loading rate can be calculated for conditions different from the
monitoring period such as long-term average rain pattern or extent of
catch basin hooding
Determine loading rate for each catch basin in MS4 by multiplying
appropriate unit loading rate by catchment size and days of accumulation
Sum calculated loading rates to establish total volume per year
Analyze Data
Calculate Loading Rate
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Justification for Proposed Methodology
Considers factors beyond land
use
Utilizes institutional knowledge
and already developed tools
Provides opportunities to update
previous assessments
Isolates floatables contribution at
the entry point to the MS4
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Next Steps!
• Join our Social Media Challenge!
• Tag a photo of yourself throwing something away, recycling, or participating in
a cleanup event!
• Post it by October 9, 2017 with #donttrashourwaters
• Winner will receive a DEP Swag Bag and Tickets to the Open House NY
Digester Egg Tour on October 14th