The District has completed the first phase of its PFAS sampling and analysis plan, and the results are favorable.
The first phase of the plan tested for 33 PFAS compounds, as outlined by the Wisconsin Department of Natural Resources (WDNR). The District’s influent (incoming wastewater), effluent (outgoing, cleaned wastewater) and biosolids were tested. Struvite, a phosphorus-rich nutrient recovered from wastewater, and polymers, which are used in the treatment of biosolids, were also tested.
Samples were collected by a consultant, TRC, using lab-accepted collection methodologies. The samples were analyzed by Eurofins|TestAmerica, which is certified by WNDR to conduct PFAS testing.
Overall, the results of the District’s initial testing were as expected based on the characteristics of the 180-square-mile service area.
Sampling highlights are summarized below.
Released September 30, 2021
The District tested influent from the five large sewer pipes, called forcemains, that aggregate wastewater from the service area and deliver it to the plant.
Examining all of the 33 compounds tested, the types of PFAS found in local wastewater is consistent with results from other municipal wastewater treatment plants in urbanized areas without significant industrial sources.
| PS08 | PS18 | PS07 | PS11 | PS02 | Weighted Average, District | Median Concentration, Michigan Study** | |
|---|---|---|---|---|---|---|---|
Percent of Total PFAS Attributed to Forcemain | 40% | 32% | 16% | 7% | 6% | N/A | N/A |
PFOA (ppt)* | 2.2 | 7.8 | 11 | 2.2 | 3.3 | 5.13 | 4.6 |
PFOS (ppt) | 2.6 | 12 | 6.2 | 3.5 | 6.9 | 6.86 | 7.5 |
If you have difficulty reading these charts on a mobile device, download this summary document.
*In the full report, numbers are reported as ng/L, which is the same as ppt, or parts per trillion. For context on ppt equivalents, see our About PFAS page.
**The Michigan Department of Environment, Great Lakes, and Energy conducted a statewide assessment of PFAS in 42 wastewater plants (WWTPs), which included the 20 largest WWTPs and 22 other WWTPs selected to represent different flow rates and treatment processes.
The District cleans wastewater to river-quality water and returns it to local watersheds via Badger Mill Creek and Badfish Creek.
The Department of Natural Resources approved surface water criteria for levels of PFOA and PFOS in Summer 2022. These criteria establish a threshold beyond which certain pollution minimization efforts must be undertaken. Our testing reveals PFOA and PFOS levels in the District’s effluent are lower than WDNR’s surface water criteria.
The waterways the District discharges to are not drinking water sources.
| District | WDNR Surface Water Criteria - Public Water Supply | WDNR Surface Water Criteria- all other surface waters | |
|---|---|---|---|
PFOA (ppt) | 9.7 - 11 | 20 | 95 |
PFOS (ppt) | 3.7 | 8 | 8 |
The District produces two biosolids products. The primary product is Metrogro, a liquid class B biosolids product that is land applied to local farm fields as a valuable, nutrient-rich fertilizer. The District also produces a small amount of class A cake.
The amounts of PFOA and PFOS in the District’s biosolids are similar to data from other municipal wastewater treatment plants that do not, like Madison, accept industrial waste from major PFAS sources.
WDNR has not established PFAS standards or provided guidance for land application of biosolids, but Michigan offers proposed action levels in its interim guidance for comparison. The interim guidance specifies PFOS thresholds at which biosolids cannot be land applied (150 ppb); at which land application should be limited (50 ppb); and at which investigation of sources and sampling of effluent is recommended but land application is not restricted (20 ug/kg). The PFOS concentrations detected in both of the District’s biosolids samples are less than Michigan’s 50 ppb threshold for limited land application rates and also slightly less than the 20 ppb threshold for suggested source investigation and effluent sampling.
Land application of Metrogro is the most cost-effective and environmentally friendly way for the District to dispose of the solid waste recovered from wastewater. Alternatives such as landfilling or incineration are costly and have additional impacts on the environment and human health.
| Class B Liquid (Metrogro) | Class A Cake | |
|---|---|---|
PFOA (ppb)* | 1.2 - 1.6 | 16 |
PFOS (ppb) | 8-10 | 19 |
*In the full report, numbers are reported as ug/kg, which is the same as ppb, or parts per billion. For context on ppb equivalents, see our About PFAS page.
Polymer: The District uses polymer to help thicken biosolids. These polymers do not add any significant amount of PFAS to the waste stream. In fact, only two PFAS compounds were found, PFOS and PFBA, and both at less than 0.5 ppb. All other PFAS compounds were at a level below the laboratory method detection limit (MDL)*, which is considered zero.
Struvite: Struvite is a phosphorus-rich nutrient we recover from wastewater. Only one PFAS compound, PFHxA, was found in struvite at 0.06 ppb. All other PFAS compounds were at a level below the laboratory method detection limit*, which is considered zero.
Neither polymer nor struvite is a source of PFAS to the environment or waste stream.
| Polymer 1 | Polymer 2 | Polymer 3 | Struvite | |
|---|---|---|---|---|
PFOA (ppb) | Less than MDL | Less than MDL | Less than MDL | Less than MDL |
PFOS (ppb) | Less than MDL | Less than MDL | 0.48 | Less than MDL |
*According to the U.S. Environmental Protection Agency, method detection limit (MDL) is “the minimum measured concentration of a substance that can be reported with 99% confidence that the measured concentration is distinguishable from method blank results.”
As outlined in the sampling and analysis plan, the District is taking a phased approach to testing, with these initial results informing next steps in the testing process.
Click each toggle for information regarding what the District will investigate in the next round of testing.
What effects do certain treatment processes have on PFAS transformations and partitioning within the plant? Answering this question will also require further characterization of the sample points in phase one to focus on mass changes of PFAS within the treatment plant processes.
What are the differences in the amount of PFAS in the Class A biosolids versus Class B biosolids. Answering this will involve additional characterization of the biosolids sample points in phase one to determine why different biosolids products differ in the amount of PFAS.
Do certain areas of the collection system contribute more PFAS than others? This will involve additional examination of influent data from the five force mains entering the plant and determine if additional pump station investigation and sampling is warranted.
For additional information about what the District is doing to address PFAS, check out the information below.
The District's initial look at PFAS, including action steps. June 2019
A look at how PFAS move through the environment and cycles through wastewater treatments plants and their effluent. Produced by District consultant, TRC, February 2020.
Guidance and procedures for conducting a comprehensive PFAS sampling plan. Produced by District consultant TRC, February 2020.
The District presented the results of its testing for PFAS, or per- and polyfluoroalkyl substances, in the local wastewater cycle today. The results were as expected and fall below proposed standards and existing screening levels.
Lab certification ensures the District receives high-quality, reproducible and accurate PFAS testing results.
Sign up to stay up to date on on the District’s PFAS work, including sampling and analysis results once available.
