Optimizing and Evaluating the Performance of Green Infrastructure in a Washington DC Streetscape

Nicole Holmes, PE, LEED AP, Sustainability and Innovation Practice Lead, Nitsch Engineering

Introduction

DC Water is the water and sewer authority for the District of Columbia, which also manages wastewater from surrounding counties. The District of Columbia has an aging and undersized combined sewer system installed over 150 years ago. During wet weather, combined stormwater and wastewater frequently overflow to the Potomac River, Anacostia River, and tributaries such as Rock Creek. The DC Clean Rivers project is a 25-year project to reduce Combined Sewer Overflows (CSOs) using a combination of deep river tunnels and green infrastructure.
In 2013, DC Water launched the Green|Challenge international design competition to drive innovative, replicable, cost-effective, and high-performing urban green infrastructure solutions for CSO reduction. As the selected streetscape project from the competition, the Nitsch Engineering team designed and implemented 33 interconnected green infrastructure techniques within one city block on Kennedy Street. Meanwhile, DC Water’s metering and monitoring program measured the effectiveness of the green infrastructure solutions.

About The Kennedy Street Green Infrastructure Streetscape Project

The Kennedy Street Green Infrastructure streetscape project was completed and constructed in 2018. The limit of work for the right of way improvements was approximately 1.5-acres, comprising one city block. At almost 90% impervious cover, Kennedy Street generated a substantial amount of stormwater runoff to the combined sewer system, which ultimately contributed to combined sewer overflows in Rock Creek. In addition, DC Water selected Kennedy Street due to wide sidewalks, thin vegetation, and a streetscape that prioritizes vehicles over pedestrians, making it an ideal candidate for implementing green infrastructure to address stormwater runoff as well as a variety of other environmental and social co-benefits.

The pre-existing conditions photo from 2013 provides a summary of the pre-existing conditions and key drivers for green infrastructure. See Figure 1.

Figure 1: Existing conditions photo summarizing key drivers for green infrastructure at Kennedy Street

To create a better streetscape condition, the Team proposed and followed a series of design principles to guide the vision. First, we aimed to mimic natural hydrologic conditions by maximizing permeable landscape surfaces to absorb rainfall at its source. Next, we looked at decentralizing and spreading new landscape areas throughout the project area to micro-manage stormwater in smaller zones. Finally, we introduced a stormwater gradient that uses a “top down” approach to managing stormwater from enhanced tree canopy to at-grade landscape-integrated elements, to enhanced soils.

Instead of locating the stormwater facilities at the low point/end point of the site, the Kennedy Street design concept included strategies to spread the landscape-based approach across the length of the entire streetscape and include strategies that capture rainfall at the vertical and horizontal planes. As the first line of defense, the project included the addition of 35 new trees and preservation of five established trees that vertically capture rainfall. When precipitation does hit the ground, the project includes 520 linear feet of permeable paving in the parking lanes, 15 bioretention curb extensions, and 580 feet of interconnected recessed landscape areas. The project also incorporates four leaching drywells to capture and infiltrate stormwater runoff from adjacent alleys. See Figure 2.

Figure 2: Illustrative Plan summarizing green infrastructure strategies

Because Kennedy Street had many unique conditions, the Team explored and implemented several experimental design techniques. The three primary experimental design techniques included:

  • changing the street profile to a W-profile,
  • using raised boardwalks and metal grates to layer stormwater techniques under pedestrian spaces and preserve existing trees, and
  • introducing a concept called landscape infiltration gaps (LIGs) to capture sheet flow in small landscape strips.

Modifying the street profile from a traditional “crown” to a “W-profile” allowed the team to micro-manage stormwater from various zones across the streetscape to support the overall performance. The valley gutter between the drive and parking lane was used to separate and convey runoff from the roadway to each downstream bioretention curb extension, supporting the performance of the permeable parking lane by not adding additional un-treated “run-on.” See Figure 3.

Figure 3: Before and after photos illustrate the “W-profile” and use of a valley gutter between the drive and permeable parking lanes

The continuous recessed landscapes and LIGs in the sidewalk zone allowed for the management of sidewalk runoff, before reaching the bioretention curb extensions in the parking zone. See Figure 4.

Figure 4: Before and after photos illustrate the continuous recessed landscapes and LIGs used to capture stormwater runoff from the sidewalk zone

The elevated metal grates were used to span existing tree roots and provide accessible paths over stormwater management features. See Figure 5.

Figure 5: Before and After photos illustrate the use of elevated metal grates to create accessible pathways over exposed tree roots

The Green Infrastructure Streetscape project was coordinated as part of a larger construction project for a larger segment of Kennedy Street in coordination with DDOT. Although many features were considered experimental and innovative, typical construction techniques were used. See Figure 6.

Figure 6: Various construction photos illustrating construction of Green Infrastructure strategies by adapting typical construction techniques commonly used in horizontal construction

The project was required to retain 1.2-inch rainfall depth in accordance with Department of Energy and Environment (DOEE) requirements. The Kennedy Street project was designed to exceed this requirement, providing the equivalent volume to retain the 1.6-inch rainfall depth over the project site through the addition of 60,000 gallons of storage capacity in the combined green infrastructure elements.

During the design process, the Team developed hydraulic and hydrologic methods to help evaluate the effectiveness of the interconnected green infrastructure elements, which were anticipated to enhance the performance of the system overall. These predictions were further supported by the pre- and post-construction monitoring performed by DC Water, presented later in this report.

The following photograph from 2018 shows the completed Kennedy Street Green Infrastructure project. See Figure 7.

Figure 7: Post-Construction photograph of Kennedy Street Green Infrastructure Streetscape

Pre- and Post-Construction Flow Metering

The DC Water Clean Rivers Project implemented a flow metering, monitoring, and data analysis program to measure how well their pilot green infrastructure projects performed. This included the Kennedy Street Green Infrastructure Streetscape project, three additional porous alleys, and one additional bioretention planter.
DC Water’s flow metering program included the installation of one flow meter and one rain gauge. The flow meter (RC-B) was installed on the 21-inch combined sewer within a manhole on Kennedy Street, near the intersection of Second Street, N.W. An estimated drainage area of 16 acres contributes to flow meter RC-B, although it should be noted that this estimate is approximate due to the complexity of the system. The Kennedy Street green infrastructure project included a combination of strategies to retain approximately 8,000 cubic feet (approximately 60,000 gallons) generated from the 1.5-acre limit of work.

A rain gauge (RC-A RC) was placed on the roof of the Latin School at the intersection of Ingraham St. NW and 2nd St. NW, approximately 2 blocks from the flow meter.

Figure 8: Map of Flow Meter and Rain Gauge Locations (prepared by Greeley and Hansen)
Figure 9: Photo of Flow Meter, RC-B (provided by Greeley and Hansen)
Figure 10: Photo of Rain Gauge, RC-A RG (provided by Greeley and Hansen)

The flow meter recorded the depth of flow (inches), velocity of flow (feet per second), and the rate of flow (million gallons per day, MGD) in the combined sewer during dry and wet weather, with recordings tabulated at five-minute time increments over the course of a 24-hour period (day). The rain gauge was operated during the same pre- and post-construction timeframe, with rainfall depths recorded at five-minute time increments.

The flow meter was operated continuously through wet and dry weather flows for two separate time periods: pre-construction and post-construction. The pre-construction period was between August 25, 2015, and October 1, 2016. During the pre-construction period, 82 rainfall events occurred with the largest recorded event measuring 2.14-inches or rainfall over a 24-hour period. The post-construction recording period was between March 14, 2019, and October 8, 2020. During the post-construction period, 132 rainfall events occurred, with the largest recorded event measuring 3.88 inches over a 24-hour period. The rain gauge experienced an outage for a brief one-week period in July 2016.

Greeley and Hansen synthesized the pre- and post-construction flow data for the dry and wet-weather conditions. For the wet weather conditions, a graph was prepared that plots the total measured flow in the combined sewer (volume, measured in million gallons) for each rainfall event (depth, measured in inches). See Figure 11.

Figure 11: Graph comparing pre-construction and post-construction wet weather flow for recorded rainfall depths (provided by Greeley and Hansen)

The total rainfall depth and wet weather flow volumes represent 24-hour totals for each corresponding event. Each wet weather event measured during pre-construction is plotted as a gray square. Each wet weather event measured post-construction is plotted as a blue circle (for events March through November 2019) or an orange triangle (for December 2019 through October 2020). The first series of post-construction data (March through November 2019) was initially plotted to provide DC Water with interim results; therefore, the final series of post-construction data (December 2019 through October 2020) was plotted as a separate color/icon to present the final data. A trendline was developed for the pre-construction data (gray squares) and the post-construction data (blue circles and orange triangles).

The comparison between the pre- and post-construction events is apparent even upon first glance, as the wet weather volumes associated with the pre-construction data are substantially larger than the post-construction data for the same or similar wet weather events. For example, during a 1.5-inch rainfall event, the combined sewer flow measured approximately 0.68 MG pre-construction and approximately 0.05 MG post construction. Favorable results were observed in rainfall events up to two inches. Unfortunately, no rainfall events that exceeded two inches were recorded during the pre-construction period.

On average, the wet weather flow volume was reduced by 72% after the construction of the green infrastructure projects in the watershed.

Key Takeaways

The flow metering and monitoring program demonstrates the effectiveness of green infrastructure in reducing wet weather discharges to the district’s combined sewers. One of the most important aspects of the Kennedy Street flow metering program was the collection of data both before and after construction. In total, the flow metering program captured data for 82 rainfall events pre-construction and 132 rainfall events post-construction, which allowed for the creation of trendlines and the calculated reduction in post-construction wet weather flow volume by 72%. The results of the flow metering helped validate the predicted effectiveness of the interconnected green infrastructure elements that were designed to optimize retention capacity. The actual results exceeded the predicted results developed using conservative stormwater models and calculations for permitting and design.

The Kennedy Street Green Infrastructure Streetscape project helped pilot innovative approaches and strategies to optimize and measure the performance of green infrastructure techniques such as permeable pavement, bioretention, and infiltration practices. In addition to demonstrating an enhanced level of stormwater management, the project preserved and planted new trees to reduce urban heat island, improved access and accessibility, increased safety for pedestrians and cyclists, and enhanced the streetscape with social gathering spaces.

Owner and Design Team

Owner: DC Water Authority
Metering & Monitoring Program Lead Engineer: Greeley and Hansen

Green Infrastructure Design Team:
Lead Engineer: Nitsch Engineering
Landscape Architect: Urban Rain|Design and Warner Larson, Inc.
Land Surveyor and Geotechnical Engineer: EBA Engineering, Inc.
Permitting: McKissack and McKissack
Community Engagement: Tina Boyd and Associates
Environmental Art: Stacy Levy/Sere Ltd.