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Wastewater Treatment Plants / Industrial Pretreatment Program

A wastewater treatment plant basin filled with waste water. A life preserver hangs on the fence.

Wastewater Treatment Plants / Industrial Pretreatment Program

The Michigan Department of Environment, Great Lakes, and Energy (EGLE) is responsible for protecting the public health and the environment by regulating discharges of wastewater to Michigan's surface waters and groundwater.

Anyone discharging wastewater into waters of the state is required by law to obtain a National Pollutant Discharge Elimination System (NPDES) permit or a Groundwater Discharge permit. The NPDES and Groundwater programs regulate municipalities and industries that discharge directly into lakes, rivers, streams, and groundwater by limiting pollutants and requiring other protections. 

EGLE is undertaking several efforts to address PFAS in surface waters and groundwater, including monitoring municipal and industrial discharges, implementing the Industrial Pretreatment Program (IPP) PFAS Initiative, and monitoring lakes and streams. 

Learn more about EGLE's PFAS sampling of lakes and streams.

Diagram of PFAS Water Cycle

PFAS Water Cycle

Learn how PFAS cycles through the water in our environment. Wastewater, groundwater, surface water, and leachate all play a role.

Take a closer look
Definitions:

Surface waters are lakes, streams, wetlands, county drains, roadside ditches that drain to lakes, rivers, etc.

Groundwater is water below the land surface in a zone of saturation. 

Wastewater discharged directly into lakes, streams, and groundwater

EGLE's Water Resources Division (WRD) has added PFAS sampling into routine NPDES permit compliance sampling inspections to further understand the prevalence of PFAS in wastewaters of Michigan.  Since 2017, EGLE has sampled 56 municipal wastewater treatment plants (WWTPs) and 41 industrial dischargers (industries including airports, landfills, paper plants, and groundwater clean-up sites for other contaminants) for a total of 161 samples collected.

Industrial Discharges to Wastewater Treatment Plants

Many industries discharge to municipal WWTPs rather than discharge directly to surface waters or groundwater. Municipal WWTPs often regulate their industrial users through the IPP required by their NPDES or Groundwater Discharge permit. The IPP provides the basis for WWTPs to regulate industries so industrial pollutants do not interfere with treatment processes or pass through to our lakes, streams, and groundwater. IPPs may require industries to pretreat wastewater or otherwise reduce or eliminate harmful pollutants. The IPP is a federally mandated program and a core part of the federal Clean Water Act. 

Municipal WWTPs major sources of PFOS and PFOA come from industries that have used PFAS-containing chemicals (such as chrome platers and paper manufacturers) and industrial users that may have accepted wastes that used PFAS-containing chemicals in their processes and/or products (such as landfills and centralized waste treaters).  Although chemical manufacturers in the United States voluntarily stopped making PFOS and PFOA years ago, these persistent chemicals may be found in factories years after they were used.  Sites contaminated by firefighting foams or PFAS-contaminated industrial wastes have also been found to be sources for WWTPs when they discharge to the sanitary sewer.

Unfortunately, conventional WWTP treatment does not effectively remove PFAS if it is discharged to the sewer system by industries or contaminated sites. Instead, PFAS may be passed through treatment to lakes, streams, and groundwater, as well as interfere with management of solids from the treatment process referred to as sludge or biosolids, dependent on the disposal method.

  • Michigan has generic cleanup criteria for groundwater used as drinking water under Part 201 for seven PFAS as listed in the table below. Municipal WWTPs that discharge to groundwater are subject to the Part 201 criteria in their compliance monitoring wells.

     

    PFAS

    Generic Cleanup Criteria (ppt)

    Perfluorooctanesulfonic acid (PFOS) 16
    Perfluorooctanoic acid (PFOA) 8
    Perfluorononanoic acid (PFNA) 6
    Perfluorohexane sulfonic acid (PFHxS) 51
    Perfluorohexanoic acid (PFHxA) 400,000
    Perfluorobutane sulfonic acid (PFBS) 420
    Hexafluoropropylene oxide dimer acid (HFPO-DA or GenX) 370

     

  • Michigan has Water Quality Values (WQV or Michigan Rule 57 values) for discharges to surface waters for three PFAS, perfluorooctanesulfonic acid (PFOS), perfluorooctanoic acid (PFOA), and perfluorobutane sulfonic acid (PFBS).  PFOS has led to fish consumption advisories for some Michigan rivers because it bioaccumulates so readily in fish and has potential human health effects if eaten. The Michigan Rule 57 values apply to NPDES discharges.  

    PFAS

    WQV* (ppt)

    Established Date

    PFBS (Drinking Water Source) 8,300 July 2022
    PFBS 670,000 July 2022
    PFOA (Drinking Water Source) 66 July 2022
    PFOA 170 July 2022
    PFOS (Drinking Water Source) 11 Mar 2014
    PFOS 12 Mar 2014

Michigan's IPP PFAS Initiative

In order to address the potential that municipal WWTPs could be passing through elevated levels of PFAS through their treatment systems to lakes, streams, and groundwater, EGLE launched the IPP PFAS Initiative in February 2018.

The IPP PFAS Initiative required all municipal WWTPs with required IPPs (95 statewide) to find out if they were passing through PFOS and/or PFOA to surface waters or groundwater and, if found, to reduce and eliminate any sources.  Under the Initiative, WWTPs were required to:

  • Identify industrial users to their system that were potential sources of PFAS.
  • Sample probable sources and their WWTP discharge (effluent) if sources were above screening criteria (12 ppt PFOS).
  • Require source reduction at confirmed sources.  This is being accomplished through pollutant minimization plans, equipment/tank change out/clean outs, product replacement, and installation of pretreatment to remove PFAS, specifically PFOS, prior to discharge.
  • Monitor compliance of  confirmed sources  and ensure that they meet local IPP PFAS requirements.
  • Submit required reports and monitoring results as required by the WRD.

As a part of this effort, the WRD developed numerous documents, including Frequently Asked Questions (FAQs), Wastewater PFAS Sampling Guidance, and Recommended PFAS Screening and Evaluation Guidance. 

A listing of documents produced or made available through that effort can be found at the EGLE WRD IPP PFAS webpage

  • Since implementation, significant progress has been made in identifying sources of PFAS, specifically PFOS, to WWTPs and reducing levels released to the environment. Four additional WWTPs have been added to the Initiative bringing the total to 99 WWTPs statewide with IPPs. Two of the WWTPs discharge to groundwater while the rest discharge to surface water.

     Key observations the WRD has made to date (July 2022):

    • Sixty-five (65) of 99 of WWTPs with IPPs (or 66%) either have no sources or have sources but have discharges at or less than the PFOS WQV.
    • 93 out of the original 95 WWTPs with IPP were able to complete the initial screening of their industrial users within one year of starting the Initiative.  Most were able to complete the screening within 6 months.
    • Low levels of PFOS (approximately 3 ppt - 7 ppt) were detected in wastewater even when no significant industrial sources were present.  This suggests that background levels of PFAS may be found in most communities.
    • Source reduction efforts have resulted in substantial drops in PFOS concentrations being discharged at the WWTPs.  (See Table 1)  The WWTPs listed in Table 1 all discharge to surface water. 

    Municipal WWTP

    PFOS, Effluent (ppt, June 2022)

    PFOS Reduction in Effluent (highest to most recent)

    Actions Taken to Reduce PFOS

    City of Ionia

    3.04

    99%

    Treatment (GAC) at 1 source

    City of Lapeer

    7.0

    99%

    Treatment (GAC) at 1 source

    City of Wixom

    9.4

    99%

    Treatment (GAC) at 2 sources

    City of Howell

    4.2

    96%

    Treatment (GAC/resin) at 1 source

    City of Bronson

    6.34

    98%

    Treatment (GAC) at 1 source

    City of Kalamazoo

    1.43

    96%

    Treatment (GAC) at 2 sources , change water supply

    K.I. Sawyer-Marquette County

    13*

    95%

    Eliminated leak PFOS-containing fire-fighting foam

    Great Lakes Water Authority (GLWA))

    17*

    54%

    Treatment (GAC) at 18 sources

    City of Belding

    5.2

    63%

    Restricted landfill leachate quantity accepted

    City of Port Huron

    12*

    99%

    Elimination of 2 PFOS sources

    *Effluent exceeds WQV of 12 ppt

    Monitoring results, if applicable, are provided for each WWTP that participated in the IPP PFAS Initiative in the interactive map below.  Additional information for each WWTP can be found in the MiWaters Site Map Explorer at Michigan.gov/MiWaters.

Preview of the IPP WWTP PFAS interactive map
Preview of the IPP WWTP PFAS interactive map

Michigan IPP WWTP PFAS status interactive map

There are 95 Wastewater Treatment Plants (WWTP) with required Industrial Pretreatment Programs (IPP) in Michigan.  All of these facilities were required to submit reports identifying any industrial users that may be sources of PFOS or PFOA.  Monitoring results, if applicable, are provided for each WWTP that participated in the IPP PFAS Initiative in the interactive map.
If you have questions or comments, please contact Brian Zuber at ZuberB@Michigan.gov.


Statewide PFAS Assessment of WWTPs and Biosolids/Sludge

In 2018, EGLE implemented two initiatives to assess potential environmental impacts of PFAS associated with municipal wastewater. The first initiative, the IPP PFAS Initiative, was launched in February 2018.  As described above, the purpose of the IPP PFAS Initiative was to evaluate the potential for PFAS from industrial sources to pass through WWTPs to receiving waters (groundwater, lakes, and streams), and to reduce or eliminate significant industrial sources of PFAS to the municipal system. 

EGLE launched a second initiative in the fall of 2018. Under this initiative, a statewide PFAS assessment of 42 WWTPs was conducted to better understand the fate of PFOS and PFOA at municipal WWTPs. Influent, effluent and biosolids/sludge sampling was performed to calculate mass balances for PFOS and PFOA through municipal wastewater treatment processes. The 20 largest WWTPs with the highest flows, along with an additional 22 WWTPs with various treatment processes, were selected. A total of 29 agricultural fields associated with 9 WWTPs were also evaluated for potential PFAS impacts utilizing soil, surface water, tile drains, and groundwater samples. This statewide PFAS sampling study provides a robust evaluation of potential PFAS impacts to the WWTPs and biosolids from Michigan.

In fall 2021, EGLE completed a second statewide PFAS assessment of 44 WWTPs, which focused on resampling WWTPs included in the fall 2018 assessment as well as sampling WWTPs without IPPs and several with groundwater discharges. Influent, effluent, biosolids/sludge, and groundwater monitoring wells were sampled. This statewide sampling helps expand EGLE’s dataset and allows for evaluation of the effectiveness of industrial source control on reducing PFOS and PFOA at municipal WWTPs since the IPP PFAS Initiative was implemented in 2018. EGLE is currently preparing a summary report of this assessment, which is expected to be published in 2022. 

Identified Industrial Sources of PFOS to Municipal WWTPs (Report): The Wastewater Workgroup summarized the industrial sources of PFOS to municipal WWTPs that were identified through the IPP PFAS Initiative.  Sources are defined as those industrial users with discharges to WWTPs greater than 12 ppt, which was used as screening level.  The majority of significant PFOS sources were metal finishers with a history of fume suppressant use, contaminated sites associated with industries or activities with PFOS usage, and landfills that accepted industrial wastes containing PFOS. 

NPDES PFAS Permitting Strategy

The Wastewater Workgroup has developed a Municipal NPDES Permitting Strategy for PFOS and PFOA. The goal of the strategy is to continue to identify, reduce, and remove PFOS and PFOA at WWTPs with NPDES permits. 

The Wastewater Workgroup also developed a compliance strategy for addressing PFAS from public and private municipal WWTPs with groundwater discharges. The goal of this compliance strategy is to evaluate, prioritize, and reduce and/or eliminate PFAS at public and private municipal WWTPs with Groundwater Discharge permits to ensure protection of public health and groundwaters used for drinking water. Read the Compliance Strategy for Addressing PFAS From Public and Private Municipal Groundwater Discharges for more information.

The Wastewater Workgroup developed an Industrial Direct Discharger and Industrial Storm Water Compliance Strategy for addressing PFOS and PFOA discharges from industrial direct and industrial storm water discharges.  The goal of the strategy is to reduce or eliminate PFOS and PFOA from industrial facilities holding NPDES and Groundwater Discharge permits to meet applicable criteria.  


Content on this page last updated on March 2023.