Computer simulations of pollution controls implemented between July 2009 and June 2013, calibrated using monitoring data, indicate that nitrogen loads to the Bay would have decreased 20.28 million pounds to 262.38 million*.
Air pollution affects each of the 17.7 million people who live in the Chesapeake Bay watershed. But it doesn’t just cloud the air we breathe. Airborne pollutants can also harm our land and water, fueling the growth of harmful algae blooms that create oxygen-depleted dead zones in the Bay. Randy Mosier from the Maryland Department of the Environment (MDE) explains how our watershed is affected by the “airshed” that surrounds it, and how airborne pollutants fall onto our land and into our water.
After eleven years, $40 million and more than 16,000 linear feet of pipe, West Virginia is set to bring a new wastewater treatment plant online and make huge cuts to the pollution it sends into the Chesapeake Bay. Under construction in West Virginia’s Eastern Panhandle, the Moorefield Wastewater Treatment Plant will replace four existing plants with one new system, marking a significant milestone in the headwater state’s efforts to curb pollution and improve water quality. Expected to go into operation this fall, the plant will remove 90,000 pounds of nitrogen and 93,000 pounds of phosphorous from West Virginia wastewater each year.
Closed Captions: http://www.youtube.com/watch?v=04Bgrrndm9I
The Chesapeake Bay Program visited three different wastewater treatment plants in the Chesapeake Bay watershed in various stages of upgrading their management systems. Join Doug Abbott, superintendent of wastewater treatment facilities in Easton, Maryland, and George Hawkins, general manager of the District of Columbia Water and Sewer Authority, as they explain the importance of these upgrades and getting the message out to the public.
The Bay cannot be restored without water that is clean, clear and rich in oxygen. Currently, the Bay and its rivers receive too much nitrogen, phosphorus and sediment for the ecosystem to remain healthy. The primary sources of these pollutants are agricultural runoff and discharges, wastewater treatment plant discharges, urban and suburban runoff and septic tank discharges, and air deposition.
Reduce computer-simulated nitrogen loads to the Bay by 75.09 million pounds, from 282.66 million in 2009, to 207.57 million by 2025*.
*Loads simulated using 5.3.2 version of Watershed Model and wastewater discharge data reported by the Bay jurisdictions. The Chesapeake Bay Program Watershed Model uses actual wastewater discharge data, which is influenced by annual weather conditions, to estimate wastewater pollution. The Model estimates pollution from other sources such as agriculture or urban runoff using average weather conditions. Loads include atmospheric deposition of nitrogen to tidal waters and the portion of atmospheric deposition to the watershed that is EPA's responsibility to reduce under the Clean Air Act. Planning targets represent the actions, assumptions, and “level of effort” necessary to meet the TMDL.
Measuring Progress and Pollution Loads
Progress is measured by using the most up-to-date wastewater discharge data and tracking data reported to EPA by Chesapeake Bay Program (CBP) partners. Computer model simulations are used to estimate the amount of nitrogen, phosphorus and sediment delivered to the Bay resulting from annual efforts to reduce pollutants from agricultural runoff and discharges, wastewater treatment plant discharges, urban and suburban runoff and septic tank discharges, and air deposition.
Pollutant loads to the Bay in any given year are influenced by changes in land-use activities and management practices, as well as the amount of water flowing to the Bay (hydrology). Annual rain and snowfall influence the amount of water in rivers flowing to the Bay.
These indicators report computer-simulated nitrogen, phosphorus and sediment loads to the Bay, using the Chesapeake Bay Program phase 5.3.2 Watershed Model. The CBP Watershed Model uses actual wastewater discharge data, which is influenced by annual weather conditions, to estimate wastewater pollution. The influence of weather, rain and snowfall can be quite large and can influence wastewater loads more than the restoration efforts in any single year. However, the indicator does demonstrate long-term progress to reduce wastewater pollution. The Model estimates pollution from other sources such as agriculture or urban runoff using average weather conditions. This allows managers to understand trends in efforts to implement pollution reduction actions. The simulations are also important for developing “what-if” scenarios managers can use to project future impacts of management actions on Bay water quality.
Other indicators featured in the Factors Impacting Health section of this website, track annual changes in river flow and pollutant loads to the Bay. It is important to calculate the amount of river flow and pollution load to the Bay in any particular year in order to understand and explain trends in Bay water quality conditions.
Because of these differences, the two types of indicators can report different pollutant load amounts in a particular year. For example, in the Nitrogen Loads and River Flow indicator, the annual load to the Bay in 2009 was 216 million pounds of nitrogen. This represents the best estimate of how much nitrogen reached the Bay in 2009 since it is based on actual river flow during that year. In the Reducing Nitrogen Pollution indicator, the simulation of nitrogen loads in 2009 was 283 million pounds. This simulation does not represent how much nitrogen actually reached the Bay in 2009 since the loads from agriculture, urban runoff, septic, forest and atmospheric sources are based on long-term average hydrology rather than the actual amount of water flowing to the Bay in 2009. Conversely, the wastewater portion of the Reducing Nitrogen Pollution indicator shows actual loads reaching the Bay, but high- or low-flow years may confound progress associated with wastewater treatment upgrades.
Bay “Pollution Diet” and Watershed Implementation Plans
In December 2010, the Environmental Protection Agency established a pollution diet for the Chesapeake Bay, formally known as a Total Maximum Daily Load or TMDL. The TMDL is designed to ensure that all nitrogen, phosphorus and sediment pollution control efforts needed to fully restore the Bay and its tidal rivers are in place by 2025, with controls, practices and actions in place by 2017 that would achieve at least 60% of the reductions from 2009 necessary to meet the TMDL. The TMDL sets pollution limits (allocations) necessary to meet applicable water quality standards in the Bay and its tidal rivers. Specifically, the TMDL allocations are 201.63 million pounds of nitrogen, 12.54 million pounds of phosphorus, and 6,453.61 million pounds of sediment per year (note, the nitrogen allocation included a 15.7 million pound allocation for atmospheric deposition of nitrogen to tidal waters).
As a result of this new Bay-wide “pollution diet,” Bay Program partners are implementing and refining Watershed Implementation Plans (WIPs) and improving the accounting of their efforts to reduce nitrogen, phosphorus and sediment pollution. The WIPs developed by Delaware, the District of Columbia, Maryland, New York, Pennsylvania, Virginia and West Virginia identify how the Bay jurisdictions are putting measures in place by 2025 that are needed to restore the Bay, and by 2017 to achieve at least 60 percent of the necessary nitrogen, phosphorus and sediment reductions compared to 2009. Much of this work already is being implemented by the jurisdictions consistent with their Phase I WIP commitments, building on 30 years of Bay restoration efforts.
Planning targets were established to assists jurisdictions in developing their Phase II WIPs. Specifically, the planning targets were 207.27 million pounds of nitrogen, 14.55 million pounds of phosphorus and 7,341 million pounds of sediment per year (note, the planning target for nitrogen included a 15.7 million pound allocation for atmospheric deposition of nitrogen to tidal waters). These planning targets, while slightly higher than the allocations published in the December 2010 TMDL, represent the actions, assumptions, and “level of effort” necessary to meet the TMDL allocations.
In 2013, the CBP partners agreed to some post-Phase II WIP adjustments to the nitrogen and phosphorus targets based on nitrogen/phosphorus exchanges and exchanges between New York’s nitrogen target and EPA’s target for atmospheric deposition of nitrogen to tidal waters. The revised planning targets are 207.57 million pounds of nitrogen and 14.46 million pounds of phosphorus per year (note, the planning target for nitrogen includes a 15.2 million pound allocation for atmospheric deposition of nitrogen to tidal waters).
The CBP partnership is committed to flexible, transparent, and adaptive approaches towards Bay restoration and will revisit these planning targets in 2017. The partnership will also conduct a comprehensive evaluation of the TMDL and the CBP’s computer modeling tools in 2017.
Phase III WIPs will be established in 2017 and are expected to address any needed modifications to ensure, by 2025, that controls, practices and actions are in place which would achieve full restoration of the Chesapeake Bay and its tidal tributaries to meet applicable water quality standards.
Additional Notes About Data Portrayed in Charts
Loads to Bay were simulated using CBP phase 5.3.2 Watershed Model.
Atmospheric deposition simulated using the Chesapeake Bay Airshed Model (a combination of a regression model of wet deposition and a continental-scale air quality model of North America called the CMAQ for estimates of dry deposition).
Atmospheric deposition to the watershed that is EPA's responsibility to reduce under the federal Clean Air Act is calculated by subtracting watershed loads in 1985, 2009 and 2012 assuming that existing requirements under the Clean Air Act are fully implemented (known as “allocation air”) from watershed loads and the actual atmospheric deposition that occurred in 1985, 2009 and 2012.
Urban Runoff and Septic loads typically increase with development unless offset by BMPs due to growth in impervious surfaces, turf, the number of septic systems, and their associated loads.
Forest loads will increase due to buffer and tree plantings, but this change lowers total loads since less pollution comes from an acre of forest than from agricultural or urban lands.
Supplemental Wastewater Indicator
The Supplemental Wastewater Indicator is a load-based measure of average annual progress toward the 2025 planning targets for wastewater treatment plants and industrial sources. Unlike the Reducing Pollution indicators which report wastewater flows from annual discharge data, this wastewater indicator uses long-term average flows to control for annual variations in weather and hydrological conditions. Since these hydrological influences can cause load fluctuations that exceed restoration efforts in any given year, this indicator was developed as a tool for watershed managers to better understand the effects of their management decisions.