
Restoring Indiana’s Waterways Through Local Partnerships
How the IDEM Watershed Planning and Restoration Section works with local watershed groups to improve water quality throughout Indiana.
Introduction
The mission of the Indiana Department of Environmental Management (IDEM), Office of Water Quality (OWQ) is to monitor, protect, and improve the quality of Indiana's water resources. The IDEM Watershed Planning and Restoration Section specifically works towards this mission by partnering with local watershed groups to reduce nonpoint source pollution . This is accomplished through two different paths. In one option, IDEM works with local watershed groups directly to help them acquire funding through the Clean Water Act Section 319(h) and 205(j) Grants for baseline monitoring, planning, development of a Watershed Management Plan (WMP), and implementation. Alternatively, IDEM conducts monitoring and develops a Total Maximum Daily Load (TMDL) report for a watershed with an active local group who will use the TMDL analysis to further develop a WMP. This path also involves funding for local groups through federal grant programs. Both paths ultimately lead to implementation of best management practices to address nonpoint source pollution and improvements to water quality throughout Indiana.
This is a flowchart that depicts how IDEM and local watershed groups can work together to improve water quality.
Assessment
The first step to improve water quality is to identify those waterbodies that need restoring. To do this, the IDEM OWQ conducts surface water monitoring to assess the status of water quality across the state in accordance with the Indiana Surface Water Quality Monitoring Strategy . IDEM staff collect water chemistry, nutrient, E. coli, fish community, fish tissue, macroinvertebrate, algae, and aquatic habitat data through three primary monitoring designs. (1) Fixed station monitoring gathers monthly water quality data at 165 sites throughout Indiana. Fixed station data are used to establish baseline data, determine changing conditions, and in limited application for making designated use assessments. (2) Probabilistic monitoring occurs in one basin per year on a 9-year rotating basin cycle . This design delivers a comprehensive, unbiased assessment of the ability of waterbodies in the monitored basin to support its designated uses. (3) Targeted monitoring, unlike the probabilistic approach, involves the intentional selection of sampling locations based on the specific monitoring objective to be met. The data collected through these projects are used to answer specific questions and vary in terms of locations, parameters, and monitoring frequency. These data are also used to determine if the waters are meeting water quality standards. IDEM's routine targeted monitoring programs include Blue-Green Algae , Fish Tissue/Fish Consumption , Reference Sites, TMDL Watershed Characterization, and Performance Measures monitoring. Additional information on IDEM’s monitoring programs may be found here . IDEM also sponsors the Clean Lakes Program through Indiana University School of Public and Environmental Affairs, and the citizen science program, Hoosier Riverwatch . Geographically-referenced data can be viewed through the Indiana Water Quality Atlas , which is an interactive mapping application with water quality data access and download capabilities.
IDEM compares monitoring data to water quality standards to identify waterbodies that are impaired.
The monitoring data collected through IDEM's surface water monitoring programs is then compared to Indiana's water quality standards . The Clean Water Act requires that every state adopt water quality standards to protect, maintain, and improve the quality of the nation's surface waters. Indiana's water quality standards are set by state law . Water quality standards describe the desired condition of a waterbody for a designated use, such as public water supply, warm water aquatic life, and full body contact recreation (swimming), and the means by which that condition will be protected or achieved. A standard can consist of either numeric or narrative criteria for a specific physical or chemical parameter. Monitoring data is assessed annually to identify waterbodies that do not meet water quality standards.
Impaired Waters
When monitoring data for a waterbody is assessed, there are two possible outcomes. A waterbody either meets water quality standards or it does not and is considered to be impaired. To make decisions about impairments, IDEM uses a document called the Consolidated Assessment and Listing Methodology (CALM) , which was developed and updated based on federal Clean Water Act requirements and Indiana’s water quality standards. The CALM helps IDEM place waters in one of five categories , according to available data, that make up Indiana’s Consolidated List. The Indiana Section 303(d) List of Impaired Waters , also referred to as the 303(d) List, consists of waters in Category 5 that are impaired and for which TMDLs are required. This list is updated every two years. For every waterbody on the 303(d) List, IDEM identifies the specific pollutant that is causing the impairment when known.
Impaired waters are included on Indiana's Section 303(d) List of Impaired Waters.
Streams identified as impaired throughout Indiana.
IDEM has developed the Online e303d Mapping Tool to display the location and applicable impairment(s) of waterbodies listed on the Indiana Section 303(d) List of Impaired Waters. Use the "+" and "-" buttons in the bottom right corner of the map to explore streams in your area of interest.
Online e303d Mapping Tool.
TMDL
The Total Maximum Daily Load (TMDL) Program primary purpose is to assess streams, rivers, and lakes that are considered impaired by IDEM and develop reports that identify the causes of the impairment, the reductions of pollutants needed, and the actions needed to improve water quality. The Clean Water Act requires that states develop Total Maximum Daily Loads (TMDLs) for waters on the Section 303(d) List of Impaired Waters. The IDEM Watershed Planning and Restoration Section is tasked with developing TMDL reports for these impaired waterbodies.
States are required to develop TMDLs for waterbodies on the Section 303(d) List of Impaired Waters.
What is a TMDL?
A Total Maximum Daily Load (TMDL) by definition is the amount of a pollutant that a waterbody can receive and still meet water quality standards, as well as the allocation of that load among the various pollutant sources. The TMDL calculation is:
TMDL = ΣWLA + ΣLA + MOS + FG
Thinking of the TMDL as a pie helps us understand where reductions can come from and who gets what portion of the pollutant load.
The wasteload allocation (WLA) is the sum of point source pollutant loadings. Point source pollution comes from a single, discrete location, such as the end of a pipe. Point sources in a watershed may include wastewater treatment plants, industrial facilities, or other operations regulated by a permit through the NPDES permit program . The load allocation (LA) is the sum of nonpoint source pollutant loadings. Nonpoint source pollution comes from the water that flows over fields, lawns, parking lots, and backyards that can carry pollutants into waterways. Nonpoint sources include many different sources which are usually difficult to track, such as land disturbing activities, unregulated animal operations, agriculture, failing septic systems, and more. The TMDL calculation also typically includes a margin of safety (MOS) and an allocation for future growth (FG).
The objective of a TMDL is to determine the loading capacity of a waterbody and to allocate that load among different pollutant sources so that the appropriate control actions can be taken and water quality standards achieved. Although regulations refer to a TMDL as a calculation or formula used to address one pollutant in one particular part of a waterbody, the concept of a TMDL has become more expansive both in scale and content as the 303(d) program has evolved. In many cases, the word TMDL is used to describe a document that addresses multiple pollutants for multiple waterbodies (i.e., several TMDLs exist in one TMDL document). Current regulations do not define the scale of TMDLs, allowing states the flexibility to develop TMDLs for a single waterbody/pollutant or group together several waterbodies/pollutants. The current process in Indiana is to complete each TMDL project for the waterbodies and pollutants within a 10-digit hydrologic unit code (HUC) watershed scale.
Prioritizing Watersheds for TMDL Development
There are three primary selection criteria IDEM considers when prioritizing watersheds for TMDL development:
- Watersheds that have waterbodies with existing impairments requiring a TMDL as identified on Indiana's Section 303(d) List of Impaired Waters.
- Watersheds that do not have an existing multiparameter TMDL or Watershed Management Plan (WMP).
- Watersheds that have an active, local group interested in addressing water quality who can use the TMDL report to develop a WMP.
The IDEM Priority Watershed Selection Process.
IDEM also prioritizes watersheds with impaired biotic community (IBC) impairments that have good habitat, which indicates the impairment is driven by a pollutant, as well as watersheds with drinking water sources, endangered and threatened (ETR) species, state partner priorities, and recreational lakes.
Watershed Characterization Monitoring
A watershed characterization is conducted for each 10-digit watershed selected for TMDL development to determine the extent and magnitude of impairments throughout the watershed. Although some impairments are known to exist in the watershed based on monitoring previously conducted through one of IDEM's surface water monitoring programs, additional monitoring is necessary to fully characterize the watershed and determine the source and extent of impairments. Selecting a spatial monitoring design, with sufficient sampling density to accurately characterize water quality conditions, is a critical step in the process of developing an adequate watershed study. Sites within the watershed are selected based on a geometric progression of drainage areas starting with the area at the mouth of the main stem river or stream (pour point) and working "upwards" through the various tributaries to the primary headwaters. The geometric site selection process is then modified by adding a targeted selection of additional sampling sites that are used to focus on localized management issues, such as point sources discharges, habitat modifications, and other potential impacts within the watershed. Monitoring sites are then established at the nearest bridge to facilitate safe and easy access to the stream.
IDEM staff conducting water quality and fish community sampling.
Watershed characterization monitoring begins each November and continues for one year. Select pour point sites established at the base of each 12-digit subwatershed are sampled monthly from November through April for general water chemistry and nutrient parameters. All monitoring sites are sampled monthly from April through the following October for general water chemistry, nutrient parameters, and E. coli. E. coli is only collected from April through October when the water quality standard for full body contact recreational use is applicable. Each monitoring site is also sampled for fish and macroinvertebrate communities during the summer months to identify biological impairments.
TMDL Reports
TMDL reports include an assessment of the water quality of the rivers, lakes, and streams in a specified watershed. The report includes a description of the water quality data collected during the watershed characterization as well as new impairments discovered and pollutants driving the impairments as indicated by monitoring data. Monitoring data in combination with precipitation and flow estimates are used to calculate loadings for pollutants of concern for each subwatershed and reductions needed to meet Indiana's water quality standards. The report also contains an overview of the watershed geography, land use, soil types, point and nonpoint sources of pollutants, and recommended implementation activities to reduce pollutant levels and restore water quality.
Working with Local Groups to Implement TMDLs
IDEM prioritizes watersheds with an active, local watershed group interested in improving water quality for TMDL development. Partnering with a local entity ensures that the TMDL findings will ultimately be used to improve water quality in the watershed. A local partner can use the final approved TMDL report to craft a WMP. TMDL reports provide valuable information, such as baseline monitoring data and loading calculations, that offer a "shortcut" for local groups interested in developing a WMP. Local partners provide a wealth of knowledge of historical land use and public interest as well as a drive to improve water quality in their community. Working together allows both IDEM and local groups to make progress towards the ultimate goal of improving water quality throughout Indiana.
Section 319
Funding
IDEM provides about $2.5 million per year through the Clean Water Act Section 319(h) Nonpoint Source Program and 205(j) to support watershed management throughout Indiana. 205(j) grants are used to fund the development of watershed management plans (WMP) only while Section 319(h) grants are used to develop WMPs, education and outreach programs , and implementation activities with the goal of reducing nonpoint source pollution in the watershed. Section 319(h) and 205(j) grants can be coupled with other funding sources, such as the DNR Lake and River Enhancement and ISDA Clean Water Indiana , to further expand on local groups watershed efforts. IDEM created a Funding Matrix , a list of public and private grants, to help local groups identify potential funding sources for their projects.
Local watershed groups can apply for Section 319(h) grant funding for watersheds with impaired waterbodies with TMDLs and watersheds currently without WMPs.
Watershed Management Plans
A watershed management plan (WMP) is a strategy and a work plan for achieving water resource goals that provides assessment and management information for a geographically defined watershed. The watershed planning process uses a series of cooperative, iterative steps to characterize existing conditions, identify and prioritize problems, define management objectives, and develop and implement protection or remediation strategies as necessary. The primary purpose of a WMP is to guide watershed coordinators, resource managers, policy makers, and community organizations to restore and protect the quality of lakes, rivers, streams, and wetlands in a given watershed. WMPs are considered to be “living documents”, meaning that as conditions change over time in a watershed, the plan should be reexamined and revised to reflect goals that have been achieved or not met.
The TMDL report can be used as a tool to guide watershed planning and implementation.
WMP development projects are typically funded by 319(h) and 205(j) funds and take about 2-3 years to develop by local government or watershed groups. TMDL reports can provide valuable information when developing a WMP and the report's information should be incorporated into the final WMP. A WMP that is approved by IDEM and EPA is required to meet IDEM's 33 element checklist and EPA's 9 minimum elements . IDEM lists all approved WMPs on their website and places the documents in Virtual File Cabinet , a site where IDEM houses all public record documents.
Existing watershed management plans as of December 2023.
WATRS Tool
The WMP and TMDL Reports Search (WATRS) Tool can be used to locate waterbodies and watersheds where a WMP and/or TMDL report has been developed. Zoom in to the 12-digit HUC watershed scale to view subwatershed names, IDEM Watershed Specialists, and applicable TMDL reports and WMPs.
WMP and TMDL Reports Search (WATRS) Tool
Implementation
Once a WMP is approved, local groups can apply for Section 319(h) implementation funds to start working on the protection and remediation strategies that were outlined in the WMP. Most WMPs include an action register that identify what steps need to be taken to reach pollutant load reduction goals . Implementation projects do "on-the-ground" work in their watersheds by installing best management practices (BMPs) in critical areas of the watershed. BMPs are techniques that are recognized to be the most effective and practical means to control nonpoint source pollutants and can be used in both urban and agricultural areas. Essentially, a BMP allows the landscape to be used in a more environmentally friendly way. Examples of BMPs include cover crops, grassed waterways, tree plantings, and rain gardens. BMP implementation leads to nonpoint source pollutant load reductions and improved water quality. IDEM tracks the amount of pollutant load reductions completed each year through 319(h) grants with sediment, phosphorus, and nitrogen being the three main pollutants that are reduced each year.
Reported estimated load reductions for BMPs implemented FFY 2018-2020
Cover crops installed (acres) that were funded with 319(h) implementation dollars in Indiana. Data source: Federal Grants Reporting and Tracking System (GRTS).
Success Stories
Watershed restoration is no easy task. When restoration efforts prove to be successful, IDEM and the U.S. EPA like to recognize these efforts through success stories . IDEM success stories include projects that used Clean Water Act Section 319(h) grant funding to reduce nonpoint source pollution that resulted in a delisting of a waterbody from the Section 303(d) List of Impaired Waters. These success stories include waterbodies where TMDLs were developed and where a local watershed group received funding to restore the waterbody before a TMDL was developed. Learn more about IDEM’s success stories in the map below and read the reports here.

Bull Run
Bull Run. Click to expand.
IDEM funded nine projects in the greater Lake County area. These projects included a locally-led development of a comprehensive watershed management plan. The projects also funded technical expertise for the development and placement of agricultural BMPs. These projects resulted in improvements in the biotic community in the Bull Run/West Creek watershed that allowed IDEM to remove the listed streams in this watershed from the 303(d) List.

Emma Creek
Emma Creek. Click to expand.
In 2002 IDEM added Emma Creek to the 303(d) list for impaired biotic communities (IBC) and ammonia. The Lagrange County SWCD developed a WMP in 2007 using Section 319 funding. Key to this restoration effort was the participation of members of the Amish community, who comprise about 75 percent of the agrarian population of the Emma Creek watershed. Numerous partners implemented BMPs throughout the watershed resulting in decreased pollutant runoff.

Metcalf Ditch
Metcalf Ditch. Click to expand.
Monitoring found that Metcalf Ditch was impaired for aquatic life resulting in the addition of Metcalf Ditch to Indiana’s 2002 303(d) List. Between 1990 and 2011, IDEM funded fifteen nonpoint source projects in the greater St. Joseph watershed. These project funds were used to develop a WMP, identify critical areas and priority actions to improve water quality, and implement BMPs to address failing septic systems, install tree plantings and encourage agricultural BMPs. As a result, IDEM removed the segment from the state’s CWA section 303(d) list in 2012.

Flowers Creek
Flowers Creek. Click to expand.
Monitoring conducted by IDEM in 2003 on Flowers Creek showed elevated levels of total phosphorus and ammonia in conjunction with low dissolved oxygen and impaired biotic communities. On the basis of these data, Flowers Creek was listed as impaired for nutrients, dissolved oxygen and biological impairments in 2006. Using Clean Water Section 319 funds, Manchester University finalized a watershed management plan for the larger Middle Eel River watershed in early 2011. Additional federal, state, and local funding was used to install a variety of BMPs throughout the watershed. Post-project sampling showed that the biological communities had recovered and the streams were no longer impaired for nutrients or low dissolved oxygen. This allowed Flowers Creek to be removed from the 303(d) List in 2018.

Boyles Ditch
Boyles Ditch. Click to expand.
In 2004, IDEM conducted a biological study on the watershed and found that the stream was not supporting a well-balanced aquatic community. This caused IDEM to list the stream on its 2006 303(d) list of impaired waters for IBC. For over two decades stakeholders have been working to improve the watershed. With funding provided by the Indiana Association of Soil and Water Conservation Districts (IASWCD), the Wildcat Creek Watershed Network hired an executive director to develop a long-term strategic plan for the Wildcat Creek watershed to serve as the foundation for future planning and implementation efforts. IDEM conducted follow-up monitoring on Boyles Ditch in 2017, which showed improvement. On the basis of these data, IDEM proposed to remove the IBC impairment from this segment on its impaired waters list in 2020.

Jenkins Ditch
Jenkins Ditch. Click to expand.
In 2004, IDEM collected chemical, physical, and biological data from Jenkins Ditch which indicated that the stream did not support aquatic life designated use. IDEM added the stream to its 303(d) List in 2006. From 1999-2012, IDEM’s Nonpoint Source program funded various activities in the watershed to promote restoration of Jenkins Ditch and other streams within the Wildcat Creek watershed. Watershed partners conducted education and outreach through stakeholder meetings, public workshops, field days, newsletters, and community cleanups. Landowners utilized various funding sources to implement best management practices such as conservation crop rotation, residue and tillage management, pest and nutrient management plans, waste management practices, filter and buffer strips, and habitat management practices on more than 20% of the land area of Jenkins Ditch-South Fork Wildcat Creek watershed. IDEM revisited the stream in 2011 to collect follow-up information on the biological community. Data indicated that the stream now fully supports the biological community. As a result, IDEM removed Jenkins Ditch from its 303(d) List of Impaired Waters in 2012.

South Fork Wildcat Creek
South Fork Wildcat Creek. Click to expand.
Agricultural activities related to crop cultivation and livestock rearing contributed nonpoint source pollution to an unnamed tributary to the South Fork Wildcat Creek (SFWC), which caused the waterbody to fail to support its aquatic life use. As a result, IDEM added this waterbody to its 2002 Section 303(d) list for biotic communities. Project partners developed a WMP and implemented BMPs to improve water quality in the stream. The waterbody now supports its aquatic life use. IDEM will propose to remove this waterbody from its list of impaired waters in 2020.

Big Walnut Creek
Big Walnut Creek. Click to expand.
Big Walnut Creek is in a predominately agricultural area. Bacteria from livestock, leaking septic systems and wildlife polluted Big Walnut Creek. IDEM added the waterbody to Section 303(d) list for Escherichia coli bacteria. Using CWA section 319 funds, project partners installed best management practices and educated stakeholders about sound agricultural management throughout the watershed. Recent monitoring data show that the Big Walnut Creek segments meet water quality standards for bacteria, prompting IDEM to propose remove it from the 2010 Section 303(d) list.

Buck Creek - Busseron Creek
Buck Creek - Busseron Creek. Click to expand.
IDEM added Busseron Creek-Robbins Creek to the Indiana’s 2002 & 2010 Section 303(d) list of impaired waters for nutrients and biotic communities. IDEM used CWA section 319 grant funding to support the creation of a WMP in 2010. A variety of state and federal programs were used to install Best Management Practices (BMPs) to improve water quality. IDEM reassessed the water quality in the Buck Creek-Busseron Creek watershed in 2016. Results of that sampling indicate that nutrients are no longer a water quality threat and that the biologic community has recovered.

Pigeon Creek
Pigeon Creek. Click to expand.
Pigeon Creek was impaired for chlordane and other priority pollutants from use of chemicals on agricultural lands with poor stream buffers and high historic soil loss and placed on the 303(d) list in 1996 and 1998. Installing BMPs such as vegetated buffers and conservation tillage, combined with landowner education, produced a measurable improvement in water quality. As a result, Indiana removed Pigeon Creek from the 303(d) list in 2002.

Devil's Backbone
Devil's Backbone . Click to expand.
Water quality data collected by IDEM in 2000 indicated that E. coli and DO standards were not being met and added Devils Backbone to the 303(d) list in 2002. A WMP was developed in 2008 by HCRSD through 205(j) funds. The restoration of Devils Backbone was supported by numerous state and federal partners. NRCS provided EQIP funds, FSA provided CRP funding, TNC provided stream restoration and outreach funding, and Harrison County SWCD completed a cost-share program for agricultural BMPs. IDEM completed monitoring in 2010 and results indicated that water quality standards had been met. Devils Backbone was removed from the 2014 CWA section 303(d) impaired water list for DO and pathogen impairment.

Pendleton Branch of Indian Creek
Pendleton Branch of Indian Creek. Click to expand.
IDEM listed the Pendleton Branch of Indian Creek on its 2008 Section 303(d) list of impaired waters due to high levels of Escherichia coli. The Indian Creek WMP was completed in May 2008. The Switzerland County SWCD, HHH RC&D, NRCS, and FSA helped implement numerous BMPs and other management activities between 2005 and 2015. IDEM resampled the reach for E. coli in 2011 and found the levels to be acceptable. As a result, IDEM removed Pendleton Branch of Indian Creek from the impaired waters list in 2014 for E. coli.

Hogan Creek
Hogan Creek. Click to expand.
In 2010, IDEM sampled Little Hogan Creek and found the segment to have a failing macroinvertebrate community. This led IDEM to list this segment on its 2014 CWA Section 303(d) List of Impaired Waters for impaired biotic communities. The Dearborn County SWCD initiated the HCWP in 2005 and completed the Hogan Creek WMP in 2007. The HWCP received four 319 implementation grants from 2008 to 2018 to implement BMPs. IDEM conducted monitoring in 2015 which showed great improvement and that the biotic community was no longer failing. IDEM will be proposing to move it from the 303(d) list in 2022.

Stump Ditch and Kilmore Creek
Stump Ditch and Kilmore Creek. Click to expand.
Stump Ditch and Kilmore Creek account for approximately 11.6 miles of stream in the South Fork Wildcat Creek (SFWC) watershed in Clinton and Tipton counties, Indiana. IDEM listed Kilmore Creek and Stump Ditch on its Section 303(d) list of impaired waters in 2006 due to impaired biotic communities. Following years of best management practice (BMP) implementation paired with education and outreach in the watershed, follow up sampling by IDEM in 2019 on Kilmore Creek and Stump Ditch showed that both segments are now fully supportive of aquatic life.