Test Page 10

Warning: This page is an edit and testing page use by the wiki authors. It is not a content page for the Manual. Information on this page may not be accurate and should not be used as guidance in managing stormwater.

This page provides an overview of street sweeping and a discussion of water quality benefits and co-benefits of street sweeping.

Street sweeping overview

Street sweeping (also called street cleaning) refers to removal of sediment, litter, or other accumulated substances on roadways, particularly in urban and suburban areas. Street sweeping does not include removal of large quantities of leaves brought to the street/verge for removal, large debris or bulky items; removal of these items is typically handled by large vacuum leaf collectors or dump trucks, respectively.

Historically, street sweeping was conducted manually by a sanitation worker with a broom or shovel to remove animal waste from horse-drawn vehicles and other detritus on roadways. Mechanical sweepers such as broom systems attached to horse carts came about in the mid-1800s, and in the early 1900s street cleaning wagons sprayed water onto roadways to wash away debris. Motor-driven street sweeping vehicles were patented in the US in 1917.

Modern street sweeping has improved efficiency of debris removal from roadways dramatically. The focus of street sweeping was simple large “cosmetic” debris removal until the 1970s when concerns about water quality arose. In the decades following, improvements in street sweeping technology focused more on the removal and collection of coarse sand particle-sized street dirt, and smaller particles which contribute to instream sediment and nutrient pollution when swept off of or washed into waterways. Even when a street was cleaned of large refuse, the amount of tiny particulate matter that could not be effectively removed manually remained to wash-off into waterways following precipitation. Pollutants in stormwater runoff have long been recognized as contributors to aquatic habitat degradation, nuisance algal growth, low dissolved oxygen and toxicity in receiving water bodies . More recently, there has been a focus on street sweeping to remove the organic matter produced by street trees (leaves, seeds, flowers, etc), which can contribute significant amounts of phosphorus to runoff, especially in the fall during leaf drop. Particulate matter (air) also poses significant air-quality concerns when entrained in the air due to wind.

Water quality benefits of street sweeping

Benefits of street sweeping

Roadways accumulate debris and material such as sediment, vegetation, vehicle debris/waste, industrial emission particle deposition, and litter. Harmful pollutants which accumulate on roadways, parking lots, and pavement include metals, organics, nutrients, and particulate matter, which street sweeping helps remove. The effectiveness of street sweeping for removing specific pollutants depends on the timing and methods of sweeping, including season, frequency of sweeping, timing relative to runoff events, type of sweeper(s), sweeping practices such as speed of sweeper and vehicle parking, and the characteristics of the surface being swept (land use, surface roughness, etc.). Below is a qualitative summary.

• Nutrients (phosphorus and nitrogen): In areas with annual leaf drop from trees, nutrient removal is greatest at the time of leaf drop. Some additional benefit occurs with spring sweeping during seed drop. Sweeping at other times of the year provides limited benefit. For more information on phosphorus, see Event mean concentrations of total and dissolved phosphorus in stormwater runoff.
• Sediment and metals: Sediment removal as discussed here does not include coarse organic sediments, which would be included in the discussion for nutrients. Removal of metals is strongly correlated with sediment removal for most metals. In areas where sweeping cannot be done during winter, sediment removal is greatest immediately following snowmelt, or during snowmelt if streets can be accessed. Sediment buildup increases with length of time between runoff events. Sediment and metal concentrations are typically greatest in industrial and major transportation areas. Sediment associated with first flush is a greater concern in small watersheds with highly connected impervious surfaces. Focused sweeping should occur in areas where there is a significant amount of construction activity. For more information on sediment see Event mean concentrations of total suspended solids in stormwater runoff.
• Chloride: Chloride is a concern in areas where road salt is applied as a deicer. Sweeping in late winter and early spring can remove residual road salt from impervious surfaces and decrease chloride loads in those areas. However, since chloride is a mobile pollutant, disposal of these sweepings may create concerns in other areas.
• Bacteria and pathogens:
• Sweeper type:
• Season and frequency:
• Surface characteristics:
• Other factors:

For more information on stormwater and pollutants in stormwater, link here.

Co-benefits of street sweeping

There are a number of benefits associated with street sweeping, the most cited being improved appearances, improved roadway safety, and improved environmental quality through both reducing air pollution and water quality pollution. Many key benefits associated with street sweeping have cumulative impacts as well. For example, increased removal of fine particulate matter can reduce the sediment load to downstream BMPs, extending the life of these practices which provide improved water quality further downstream. As the old adage goes, “an ounce of prevention is worth a pound of cure” when it comes to source removal before sediment enters the stormwater system.