Environmental Challenges for the Charles River
Reducing high levels of bacteria in the Charles River has been a top priority for The Clean Charles River Initiative.
Elevated bacteria levels are primarily caused by the following sources:
- Illicit sewage discharges to storm drain systems
- Illicit discharges are generally any discharge from a storm drain system that is not composed entirely of stormwater. Illicit discharges are a problem because, unlike wastewater which flows to a wastewater treatment plant, stormwater generally flows to waterways without any treatment. Illicit discharges often include sewage, bacteria, viruses, phosphorus and nitrogen (nutrients), surfactants, and various toxic pollutants.
- Combined Sewer Overflows (CSO)
- CSOs occur when wastewater containing untreated human waste, industrial waste and other debris is carried through the stormwater pipes and discharged into the River. Boston's sewer system was originally designed to carry sewage and stormwater in the same pipe to a sewage treatment plant. After heavy rainfall or snowmelt events, however, the wastewater volume can be more than the sewer system or treatment plant can handle. For this reason, combined sewer systems were designed to have safety valves that allow overflow after rain events, which results in wastewater being discharged directly into the River. Visit EPA's National Pollutant Discharge Elimination System web site for additional information on Combined Sewer Overflows (CSOs).
- Charles River Map of CSO Outfalls Into the Lower Basin (pdf)
- Massachusetts Water Resources Authority (MWRA) information on CSOs in Greater Boston area
- Uncontrolled urban stormwater runoff that contains pet and animal waste
- Stormwater runoff occurs when precipitation from rain or snowmelt flows over the ground. Impervious surfaces like driveways, sidewalks, and streets prevent stormwater runoff from naturally soaking into the ground. Stormwater can pick up sediments, oil, nutrients like phosphorus and nitrogen that can cause algae, debris, chemicals, dirt, and other pollutants, which flow into a storm sewer system or directly to a lake, stream, river, wetland, or coastal water. Anything that enters a storm sewer system is discharged untreated into the waterbodies we use for swimming, fishing and sometimes drinking water. Pet waste can be a major source of bacteria and excess nutrients in local waters.
Reducing Discharges from CSOs
In March 2006, EPA reached a settlement with Massachusetts Water Resources Authority (MWRA)A 1985 Federal Court Order directed the newly formed Massachusetts Water Resource Authority to develop a CSO reduction plan that included construction of the sewage treatment plant on Deer Island and reconstruction of much of the sewer system in metropolitan Boston. This billion dollar investment yielded dividends of a drastic reduction of CSOs into Boston Harbor and its tributaries leaving Boston with some of the cleanest urban rivers and urban beaches in the nation.. This was the final step to reducing CSO discharges to the Charles River from 1.7 billion gallons per year (1988) to just 6.88 million gallons per year.
Under the 2006 settlement, MWRA committed to take a number of actions at the Cottage Farm The Cottage Farm Primary Treatment Facility is a MWRA CSO treatment facility in Cambridge, MA. It screens, chlorinates and de-chlorinates sewage mixed with stormwater prior to discharge into the Charles River. primary treatment facility. These include:
- Utilizing an abandoned 54-inch pipe beneath the Charles River to relieve pressure on the treatment facility during heavy storm events;
- Conveying additional flow to the Ward Street Headworks;
- Optimizing operations at the Cottage Farm facility (including the interconnection of sewer lines at the facility) to better balance flow; and
- Additional sewer separation in Brookline and Boston (including the Bullfinch Triangle area near North Station).
The MWRA also performed an engineering evaluation of further system enhancements, including:
- Use of real-time controls at a number of overflow regulators;
- Modification of existing interconnections to better balance flow in a number of primary sewer pipes; and
- Evaluation of the construction of new interconnections between two main sewer interceptors in the vicinity of the Charles River.
Nutrients, primarily phosphorus, are a chief culprit for dramatic algae blooms that plague the River with blue-green algae during the summer months.
These "blue green" algae blooms, are a form of bacteria known as Cyanobacteria, whose cells may release a toxin when they die. Exposure to the toxin can cause skin rashes and irritate the nose, eyes or throat, and if ingested can lead to serious liver and nervous system damage. Other harmful effects of the algae include reduced water clarity, nuisance scum, and reduced oxygen in the water which is necessary for a healthy fish habitat.
EPA's goal is to reduce phosphorus discharges to the lower Charles by 54 percent to restore the river to a healthy state. In order to meet that goal, EPA must reduce the amount of stormwater runoff entering the River.
How Phosphorus gets into the River
Phosphorus enters the river by a number of routes, some of which are already controlled by permits issued by EPA and MassDEP. These include:
- combined sewer overflows,
- illicit connections through which sanitary sewage seeps into storm drains, and
- outflows from wastewater treatment plants
- stormwater discharges through the stormwater systems of municipalities
Some are uncontrolled:
- stormwater runoff from impervious areas, such as pavement and roofs that do not enter municipal storm drains.
How to Regulate Phosphorus Discharges
In October 2007, EPA and the Massachusetts Dept. of Environmental Protection (MassDEP) announced aggressive targets to reduce harmful levels of the nutrient phosphorus from entering the Charles River through stormwater.
EPA and MassDEP established a "Total Maximum Daily Load" (TMDL) for discharges of phosphorus into the lower Charles River. A Total Maximum Daily Load, or TMDL, is a calculation of the maximum amount of a pollutant that a waterbody can receive and still safely meet water quality standards. A TMDL determines how much of a pollutant can be put into a body of water before it has harmful effects. EPA and MassDEP developed and approved the new limits on phosphorus to the lower Charles using extensive data collected in the river over several years.
The TMDL forms the scientific basis for controlling the discharge of phosphorus by implementing various stormwater management practices to ratchet down the discharge of phosphorus into the river to a level where the discharge is not impairing water quality.
EPA and MassDEP are permitting municipalities and other stormwater dischargers to reduce their contribution of phosphorus to the Charles.
Techniques to reduce phosphorus in stormwater include the construction of infiltration chambers, the installation of permeable pavement that enhances the return of water to the soil, the use of high efficiency street sweepers, and other low-impact development methods.
Residual Designation Authority
The Clean Water Act (CWA) and related regulations define the specific industrial and municipal stormwater sources that must be authorized by an NPDES permit. The CWA recognizes that other sources, such as commercial, industrial, and other private properties, may need to be regulated on a case-by-case or category-by-category basis based on additional information or localized conditions. The authority to regulate other sources based on the localized adverse impact of stormwater on water quality through NPDES permits is commonly referred to as the "Residual Designation" authority.
In May 2019, EPA New England received a petition from the Conservation Law Foundation ("CLF") and the Charles River Watershed Association ("CRWA"), requesting that EPA exercise its Residual Designation authority for parcels greater than 1 acre in the Charles River watershed.
In response, EPA has initiated a detailed stakeholder outreach process outlined in the letter below:
In addition, EPA will hold a number of webinars for specific stakeholder groups on the following dates:
- Wednesday, September 16, 2020 - Webinar for Municipalities, Co-Hosted by the Massachusetts Municipal Association
- Thursday, September 17, 2020 - Webinar for Commercial Real Estate, Industrial Parks, and other Institutions, Co-Hosted by the Commercial Real Estate Development Association (NAIOP)
- Friday, September 18, 2020 - Webinar for Watershed Associations and other Non-Profit groups, Co-Hosted by the Massachusetts Rivers Alliance
A copy of the presentation that was provided to the above stakeholder groups is available here:
In addition, EPA has developed a Frequently Asked Questions document that is available here:
Please contact us with any questions or comments.