How do you measure stream flow?
Quick stream flow measuring is best done with a water current meter to measure water current velocity. Stream flow measuring is easily accomplished using a water current meter and a tape measure. The current velocity meter allows you to measure stream flow velocity in feet or meters per second and measure water depth in hundredths of a foot up to three feet. The average stream flow velocity times the cross-sectional area of the stream determines the stream flow measurement in cubic feet or meters per second. The area for of a channel is known for pipes, or is determined for a stream flow measurement by measuring the distance from shore and water depth at various points across the stream flow to construct a channel profile. The water current meter offers two unique methods for determining average water velocity: 1) For small stream flows and pipes, the current velocity meter may be moved smoothly and uniformly throughout the stream flow profile until a steady average reading is displayed. This steady reading is the true average velocity for the stream flow. 2) For larger streams, the current velocity meter may be used to measure a vertical profile of water velocity at several points across a stream channel. The stream flow measurement for the profile is the sum of the average velocity of each subsection of stream flow times its cross-sectional area
What are Inflow and Infiltration?
Inflow and infiltration or I & I are terms used to describe the ways that groundwater and stormwater enter into dedicated wastewater or sanitary sewer systems. Dedicated wastewater or sanitary sewers are pipes located in the street or on easements that are designed strictly to transport wastewater from sanitary fixtures inside your house or place of business. Sanitary fixtures include toilets, sinks, bathtubs, showers and lavatories.
Inflow is stormwater that enters into sanitary sewer systems at points of direct connection to the systems. Various sources contribute to the inflow, including footing/foundation drains, roof drains or leaders, downspouts, drains from window wells, outdoor basement stairwells, drains from driveways, groundwater/basement sump pumps, and even streams. These sources are typically improperly or illegally connected to sanitary sewer systems, via either direct connections or discharge into sinks or tubs that are directly connected to the sewer system. An improper connection lets water from sources other than sanitary fixtures and drains to enter the sanitary sewer system. That water should be entering the stormwater sewer system or allowed to soak into the ground without entering the sanitary sewer system.
Improper connections can be made in either residential homes or businesses and can contribute a significant amount of water to sanitary sewer systems. Eight inch sanitary sewer pipes can adequately move the domestic wastewater flow from up to 200 homes, but only eight sump pumps operating at full capacity or six homes with downspouts connected to the sanitary sewer pipe will overload the capacity of the same eight inch sewer pipes. A single sump pump can contribute over 7,000 gallons of water to sanitary sewer systems in a 24 hour period, the equivalent of the average daily flow from 26 homes.
Infiltration is groundwater that enters sanitary sewer systems through cracks and/or leaks in the sanitary sewer pipes. Cracks or leaks in sanitary sewer pipes or manholes may be caused by age related deterioration, loose joints, poor design, installation or maintenance errors, damage or root infiltration. Groundwater can enter these cracks or leaks wherever sanitary sewer systems lie beneath water tables or the soil above the sewer systems becomes saturated. Often sewer pipes are installed beneath creeks or streams because they are the lowest point in the area and it is more expensive to install the pipe systems beneath a roadway. These sewer pipes are especially susceptible to infiltration when they crack or break and have been known to drain entire streams into sanitary sewer systems. Average sewer pipes are designed to last about 20-50 years, depending on what type of material is used. Often sanitary sewer system pipes along with the lateral pipes attached to households and businesses have gone much longer without inspection or repair and are likely to be cracked or damaged.
Inflow and Infiltration water is called "clear water" (although it may be dirty) to distinguish it from normal sanitary sewage water in the sewer system.
Why is inflow and infiltration a problem?
Sanitary sewer systems are designed to carry wastewater from toilets, dishwashers, sinks, or showers in homes or businesses. Inflow and infiltration add clear water to sewer systems increasing the load on the systems. Clear water belongs in stormwater sewers or on the surface of the ground, and not in the sanitary sewers. A stormwater sewer is a pipe system designed to carry rainwater away. Stormwater sewers are normally much larger than sanitary sewer systems because they are designed to carry much larger amounts of water. Drainage ditches also act the same way in many neighborhoods. When clear water enters sanitary sewer systems, it must be transported and treated like sanitary waste water. During dry weather the impact of inflow and infiltration can vary from minimal impact to a significant portion of the sewer pipe flow. Wet weather magnifies existing inflow and infiltration sources. As a rain or snow melt event begins the inflow and infiltration sources start filling the sanitary sewer systems with clear water, eventually filling the sewer systems to capacity. Once the sanitary sewer systems have reached capacity or becomes overloaded, wastewater flows at much higher water level than normal and if sanitary fixtures or drains are below this overload level, water will flow backward through the sanitary sewer pipe, flooding basements or households and causing manholes to pop open releasing wastewater onto the street.
Overflow occurrences put public health at risk and violate state and federal environmental regulations. Sanitary sewer overflows release wastewater and potential pathogens onto streets, into waterways, and basements increasing potential health risks. As wastewater overflows into creeks, rivers, lakes, and streams it contaminates all bodies of water fed by the waterways and all creatures/plants coming in contact with the polluted water. Sewer overflows also contribute to beach advisories and closures due to contamination.
Many communities are likely to experience at least a few overflows in their sanitary sewer systems, but older communities located downstream from these overloaded sewer systems will experience the most overflows and basement backups because of their low location in the watershed. The sanitary sewer systems in these older communities not only carry their own wastewater and inflow an infiltration, they also receive the wastewater flow from the upstream neighboring community’s sewer systems. The network of integrated sewer collection system pipes throughout a regional service area makes it essential for all municipalities to collaborate on and share responsibility for developing and implementing long-term solutions to the inflow and infiltration problem.
Inflow and infiltration reduce the ability of sanitary sewer systems and treatment facilities to transport and treat domestic and industrial wastewater. As a result of the inflow and infiltration, wastewater treatment processes are disrupted and poorly treated wastewater is discharged to the environment.
There are various costs associated with inflow and infiltration including sanitary sewer system overflow, with wastewater treatment and transportation facilities, and funding opportunities. Overflow costs are associated with road and waterway cleanup and the potential for fines if the overflow problem is not corrected. Additionally, sewer system backups into basements or households can result in litigation and potential liabilities for the responsible city or agency. Eventually, new homes or businesses may not be allowed to connect to the sanitary sewer system if the inflow and infiltration issues are not corrected, increasing costs to residents as a new sanitary sewer systems are installed or potentially lowering housing values due to the inability to develop land for future growth.
Inflow and infiltration costs water treatment facilities and consumers large amounts of money in water treatment operating expenses. All water entering a water treatment facility must be treated as wastewater causing an increase in operating costs proportional to the amount of clean water entering the sanitary sewer system due to inflow and infiltration. For example, the Metro Plant in St. Paul, Minnesota typically receives 200 million gallons a day (mgd) of wastewater from its sanitary sewer systems. During a rainstorm the load on the sewer systems can triple to 700 mgd or more. Costs associated with processing the added clean water from inflow and infiltration are eventually passed back to the consumer in the form of rate increases. By reducing inflow and infiltration capital and operating costs can be lowered. Minimizing inflow and infiltration can also increase the lifetime-capacity of a treatment facility and wastewater transportation system. The pumps that are involved with wastewater treatment and transport operate 24 hours a day seven days a week; however they must work harder as the sewer system’s water level load increases. This puts an unneeded strain on the pumps and shortens the life expectancy of these expensive pumps.
Other costs include the city or agency failing to meet federal or state guidelines and causing the community to become ineligible for low interest loans from grant or revolving fund opportunities. Often state water boards will provide funding opportunities to a city or agency; however they will be tied to some related criteria. In this case the funding opportunities would be tied to the number of sanitary sewer system overflow incidences in the city or agency’s area. History and scope of the inflow and infiltration problem.
Inflow and infiltration problems are difficult to resolve because of the enormity of the infrastructure in place. It is estimated that there are approximately 4.0 billion feet of sanitary sewer pipe in the United States and more being installed daily. This estimate does not include "combined sewer systems" that serve as both storm and sanitary sewer system. If these sewer systems were laid end-to-end, they would represent about 290 parallel pipelines that would stretch from New York to California. Most sewer pipe inventory for older cities pre-dates World War II, were installed with materials that are well beyond their expected service life and using methods of construction that are not state of the art. Many old neighborhoods have “combined sewer systems”, which were designed before wastewater treatment plants existed. These combined sewer systems are typically routed to the wastewater treatment plants for processing. Due to their nature many of these sewer systems experience overflows during storm events. In response to this many cities and agencies are retrofitting or redesigning their systems to better meet the EPA requirements and the load their community places on the sewer systems.
The EPA requires any regulated agency with a NPDES permit to eliminate all wastewater overflows that reach the waters of the United States. The ability to achieve such a goal is virtually impossible for a large majority of cities and agencies, since inflow and infiltration cannot be completely stopped. Initial efforts, in the 1970’s, to reduce inflow and infiltration in sanitary sewer systems were, typically, unsuccessful, in spite of substantial funding from the EPA’s Construction Grants Program. Most inflow and infiltration control programs were reduced to emergency programs, in the late 1980’s, that tried to resolve isolated issues in the sanitary sewer systems. During this time period several major sanitary sewer systems were evaluated in cities such as Nashville, Atlanta, and Houston. These evaluations raised public interest in the repair and replacement of sanitary sewer system infrastructure. Additionally new and better sewer system technologies allowed for reduction or elimination of inflow and infiltration sources.
Public interest in sanitary sewer systems has also been aroused by the project growth estimates of many metropolitan areas. Growth projections are used to predict and plan for wastewater flows through the sanitary sewer systems and wastewater treatment plants. Typically the sewer systems and treatment plants are designed using national standards for average and peak flows of wastewater through the sewer systems.
If the inflow and infiltration levels were not reduced or eliminated, projecting their contribution to the sanitary sewer systems show that cities and agencies would be required to make significant investments in relief sewer systems and pumping stations. However it is not feasible to add capacity to transport and treat the clear water introduced by inflow and infiltration. Wastewater treatment infrastructure is an expensive investment for a community. Additionally most of the existing wastewater treatment plants would not be able to treat the additional flow of an ever increasing clear water problem because of space constraints at the wastewater treatment sites.
How can the inflow and infiltration problem be solved?
The reduction and control of inflow and infiltration in sanitary sewer systems should be considered with regard to a disciplined, long-term monitoring and maintenance program. The first step to resolving any inflow and infiltration problems is determining how significant the problem is. Typically a sanitary sewer system evaluation is performed to assess the system. An evaluation of the sewer system will determine the quantity of inflow and infiltration, determine their sources and provide guidance to determine a cost effective corrective action plan.
As with most situations you can’t manage what you can’t measure and the first step to managing the inflow and infiltration issue is to measure the extent of problem. To quantify the inflow and infiltration into a sanitary sewer system means a significant attempt to locate and record information that relating to a variety of issues including but not limited to observed overflows, measured or observed surcharges, reported bypasses, customer backup complaints, and chronic maintenance activities. The information should be obtained from different places including maintenance records, sewer maps, complaint records, assorted department files, work orders, past studies, engineering reports, and interviews with personnel who are responsible for maintenance and management of the sanitary sewer system. A large amount of information can be found using these sources as well as others. Once the data has been found it must be recorded and displayed in a way that will show possible relations between overflows, bypasses and other related factors such as capacity models, rainfall records, maintenance activities, and reported backups. If electronic maps of the sanitary sewer system are available, they should also be used to confirm the result of the data findings.
Once the data has been researched and correlations found the city or agency must establish sewer flow monitoring points at various locations within the system. Typically sanitary sewer systems can be broken down into associated watersheds. Then those watersheds can be separated into basins and if necessary sub-basins.
Flow monitoring instrumentation must be placed in sanitary sewer systems at locations appropriate to obtain the data desired. To measure wastewater flows through the sanitary sewer system it is important to select the appropriate flow meter. Many types of flow monitoring instrumentation are available and pricing varies accordingly. Simple instruments like a flow probe measure water velocity and depth but do not record data. This type of instrument is good for spot flow checks or random checks of permanently installed flow meters. Often long term flow measurements can be made using simple water level recorders. In this case only water level is recorded then the data is exported into a spreadsheet and the data can be processed through an equation or lookup table that cross references water level to flow for that particular site. The advantage of water level recorders is that they are relatively inexpensive and multiple units can be purchased with a moderate investment to monitor the water level (flow) throughout the sanitary sewer system. Alternatively more sophisticated flow meters can output, display, and record flow information directly. Often these instruments also have output that can trigger wastewater samplers or other devices. These instruments are typically a larger investment, but have greater monitoring abilities.
The following "rules-of-thumb" may be used to determine a monitoring and evaluation strategy to adequately measure amount of inflow and infiltration in a sanitary sewer system. These parameters vary depending on the overall city or agency goals.
• One flow meter for every 30,000 – 50,000 feet of sanitary sewer pipe
• The flow meter recording should be set at 15-minute intervals
• Flow meter capable of measuring surcharges
• One rain gauge for every 2-4 flow meters
• Minimum monitoring period – 45 days with 60 days being optimal
• Measurement of between 6-8 separate rainfall events
• The system should be monitored during a period of high seasonal groundwater
Once the flow monitoring data has been collected it should be carefully evaluated. Adjustments to account for periodic flow profiling at the monitoring site, errors associated with grease or deposits on the sensors, drift of the depth recordings, and downtimes related to flow meter malfunction. The corrected data should be tabulated and analyzed to make comparisons between the measured inflow and infiltration and the corresponding rainfall intensity. Data under surcharge conditions should be avoided for analysis purposes. The analysis will provide two essential parameters that are used to quantify the inflow and infiltration problem. The first parameter is a comparison between different basins so that basins can be prioritized for future studies and potential inflow and infiltration reduction. The second parameter is information that will be useful if subsequent relief or replacement sewer systems are necessary to reduce or eliminate overflow or bypass conditions.
Basins can be ranked in a range of ways. Rankings might include unit inflow or infiltration rates such as gallons/day/foot, mgd/1,000’, gpd/inch-mile of pipe, mgd/acre, etc. By changing the raw flow data into a measured unit rate, comparisons may be made between basins as well as comparisons relating factors such as general age of the sanitary sewer system, frequency of reported overflows, etc.
In addition to flow monitoring there are other tests that a city or agency can use to identify sources of inflow and infiltration. These tests include dye and smoke testing and visual inspection. Smoke and dye testing work by introducing either dye or smoke into the sanitary sewer system and determining where it comes out. Visual inspection can be done with remote television monitoring devices and used to look for cracks or other damage in a sewer pipe.
Once a source of inflow and infiltration has been discovered the city or agency will take appropriate action to resolve the problem, including fixing or replacing damaged or leaky sewer pipes and notifying property owners of improper connections. Periodically the city or agency must monitor and measure their sanitary sewer system to maintain the integrity of the system and determine new sources of inflow and infiltration. Continuous monitoring is also beneficial to the cities and agencies so appropriate cost increases can be applied to communities/basins that are heavy contributors to inflow and infiltration into the sanitary sewer system.