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Tenmile Creek and the Ottawa River Watersheds Fulton and Lucas Counties, Ohio Total Maximum Daily Load Development

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Tenmile Creek and the Ottawa River Watersheds Fulton and Lucas Counties, Ohio Total Maximum Daily Load Development Loading Analysis Plan and Supporting Data Acquisition Needed for the Tenmile Creek and the Ottawa River Watersheds Fulton and Lucas Counties, Ohio Total Maximum Daily Load Development Hill Ditch near mouth, Ottawa River (Toledo) basin. Ohio EPA Technical Report AMS/2011-OTTEN-3 Division of Surface Water Assessment and Modeling Section March 2019 TMDL DEVELOPMENT | AMS/2011-OTTEN-3 Loading Analysis Plan – Tenmile Creek and Ottawa River Watershed March 2019 Introduction This document provides an overview of the information considered in proposing analytical methods to address water quality impairments in the Tenmile Creek and Ottawa River watershed (Fulton and Lucas Counties, Ohio). These recommendations are based on data collected as part of a biological and water quality study in 2011. A description of the project area, sites, data types and methods can be found in the Tenmile Creek and Ottawa River study plan document at (https://epa.ohio.gov/portals/35/tmdl/TenmileStudyPlan2011_Final.pdf). A summary of the study results can be found in the biological and water quality report at (https://epa.ohio.gov/Portals/35/documents/Tenmile_Ottawa_TSD_2015.pdf). Sites in the Tenmile Creek and Ottawa River watershed were assessed for aquatic life use and recreation use. The public water supply use was not assessed since no surface waters are used as a public water supply in this study area. The attainment of aquatic life and recreation use is based on specific restoration targets. This document examines those targets and lays out proposals for addressing each impairment. Where appropriate, methods are outlined to develop total maximum daily loads (TMDL) for specific pollutants. Aquatic Life Use Evaluation of Biocriteria Attainment of Ohio EPA’s biocriteria are based on fish and macroinvertebrate scores, as measured by the Index of Biotic Integrity (IBI), Modified Index of well-being (MIwb) and Invertebrate Community Index (ICI). Goals for those indices in the Tenmile Creek and Ottawa River watershed are shown in Table 1. The attainment status for each site is shown in Figure 1 and the scores for impaired sites are shown in Table 2. Table 1 – Biological criteria applicable in the Ottawa River (Toledo) watershed for aquatic life use designations. Biological Criteria for the Biological Assessment Applicable Aquatic Life Use Ecoregion Index Method2, 3 Designations1 WWH MWH4 Headwater 28 20 IBI Wading 32 22 Huron-Erie Boat 34 20 / 22 Lake Plains Wading 7.3 5.6 (HELP) MIwb Boat 8.6 5.7 / 5.7 ICI All5 34 22 1 Aquatic Life Use (ALU) designations: warmwater habitat (WWH); modified warmwater habitat (MWH); limited resource waters (LRW) and seasonal salmonid habitat (SSH) do not have associated biological criteria. 2 The assessment method used at a site is determined by its drainage area (DA) according to the following: Headwater: DA ≤ 20 mi2; wading: DA >20 mi2 and ≤ 500 mi2; boat: DA > 500 mi2. 3 MIwb not applicable to drainage areas less than 20 mi2 (headwater sites). 4 Biocriteria depend on type of MWH. MWH-C (due to channelization) is listed first and MWH-I (due to impoundment) is listed second. 5 Limited to sites with appropriate conditions for artificial substrate placement. 2 AMS/2011-OTTEN-3 Loading Analysis Plan – Tenmile Creek and Ottawa River Watershed March 2019 Figure 1 — Map summarizing ALU attainment status in the Tenmile Creek and Ottawa River watershed in 2011. 3 AMS/2011-OTTEN-3 Loading Analysis Plan – Tenmile Creek and Ottawa River Watershed March 2019 Table 2 – Aquatic life use attainment information for impaired sampling locations in the Tenmile Creek and Ottawa River watershed, 2011. Shaded sites are in the Maumee Area of Concern. Drain. Ecoregion/ River Attain. Station Location Area IBI MIwbc ICId QHEI Causes Sources ALU Milea Status (mi2) 04100002 03 04 - Little Bear Creek-Bear Creek Bear Creek near Ohio/ 301452 Michigan border HELP/ WWH 8.44 22.90 26.0 7.82 38.0 31.5 NON Sedimentation/ siltation Channelization @Fulton County Rd. 7 04100001 03 01 – Shantee Creek Shantee Creek Urban runoff/storm P11S96 diversion at Toledo @ HELP/ LRW 3.10 7.70 12.0 N/A VP 29.0 NON Sedimentation/siltation sewers Lewis Ave. Sediment resuspension Shantee Creek Priority organics (contaminated P11S60 diversion at Toledo @ HELP/ MWH 0.70 9.10 24.0 N/A LF 35.0 PARTIAL (PCB/PAH in sediments) sediment), Urban Stickney Ave. runoff/storm sewers Silver Creek at Toledo Urban runoff/storm P11S79 HELP/ LRW 4.44 4.60 16.0 N/A P 43.0 NON Sedimentation/siltation @Lewis Ave. sewers Urban runoff/ storm Sedimentation/ siltation sewers Silver Creek at Toledo Sediment resuspension 301449 HELP/ MWH 1.70 5.70 22.0 6.98 VP 41.0 NON @ Futura Dr. Priority Organics (PAH in (contaminated sediments) sediment), Urban runoff/storm sewers 04100001 03 02 – Halfway Creek Urban runoff/ storm Halfway Creek near Sedimentation/ siltation 301448 Ohio/ Michigan border HELP/ WWH 4.88 22.10 36.0 7.96 F 50.0 PARTIAL sewers @ East State Line Rd. Priority Organics sediment resuspension 04100001 03 04 – Headwaters Tenmile Creek Tenmile Creek east of 301446 Metamora @ Fulton HELP/ WWH 16.0 25.90 26.0 7.38 G 32.5 NON Sedimentation/ siltation Channelization County Rd. 1 Tenmile Creek west of P11K65 HELP/ WWH 9.76 43.00 31.0 6.75 G 49.0 PARTIAL Sedimentation/ siltation Channelization Sylvania @ Kilburn Rd. 4 AMS/2011-OTTEN-3 Loading Analysis Plan – Tenmile Creek and Ottawa River Watershed March 2019 Drain. Ecoregion/ River Attain. Station Location Area IBI MIwbc ICId QHEI Causes Sources ALU Milea Status (mi2) 04100001 03 05 – North Tenmile Creek North Tenmile Creek Crop production with P11S77 at Sylvania @ Monroe HELP/ WWH 0.12 42.1 28.0 7.89 F 54.0 PARTIAL Low flow alterations subsurface drainage St. 04100001 03 06 – Tenmile Creek Tenmile Creek P11S76 southwest of Sylvania HELP/ WWH 5.94 64.5 34.0 6.98 18.0 52.5 PARTIAL Sedimentation/siltation Channelization @ Herr Rd Tenmile Creek P11K64 southwest of Sylvania HELP/ WWH 2.97 70.0 37.0 6.14 26.0 51.0 PARTIAL Sedimentation/siltation Channelization @ Brint Rd. 04100001 03 07 – Heldman Ditch-Ottawa River Ottawa River near Urban runoff/ storm 301440 Sylvania @ Harroun HELP/ WWH 19.50 124.6 37.0 6.34 34.0 78.0 PARTIAL Sedimentation/siltation sewers Rd. Ottawa River near Urban runoff/ storm 301442 Ottawa Hills @ HELP/ WWH 14.42 131.6 34.0 5.63 28.0 59.3 NON Sedimentation/siltation sewers Edgehill Rd. Zink Ditch west of Urban runoff/ storm P11P37 HELP/ MWH 0.70 3.5 38.0 N/A LF 34.5 PARTIAL Sedimentation/siltation Toledo @ Dorr St. sewers Hill Ditch @ Carriage Urban runoff/ storm 301450 HELP/ MWH 2.58 3.5 22.0 N/A P 64.5 PARTIAL Sedimentation/siltation Dr. sewers Hill Ditch near Ottawa Urban runoff/ storm P11K61 HELP/ MWH 2.11 6.3 22.0 N/A LF 55.0 PARTIAL Sedimentation/siltation Hills @ Reynolds Rd. sewers 04100001 03 08 – Sibley Creek-Ottawa River Ottawa River at Urban runoff/ storm 301444 HELP/ WWH 9.25 155.60 25.0 8.41 24.0 72.0 NON Sedimentation/siltation Toledo @ Monroe St. sewers Ottawa River at Urban runoff/ storm 301443 Toledo @ Douglas HELP/ WWH 10.86 155.0 30.0 6.23 16.0 43.0 PARTIAL Sedimentation/siltation sewers Ave. Ottawa River at Urban runoff/ storm P11S74 Toledo @ University of HELP/WWH 11.15 155.0 33.0 7.13 28.0 48.5 PARTIAL Sedimentation/siltation sewers Toledo 5 AMS/2011-OTTEN-3 Loading Analysis Plan – Tenmile Creek and Ottawa River Watershed March 2019 Drain. Ecoregion/ River Attain. Station Location Area IBI MIwbc ICId QHEI Causes Sources ALU Milea Status (mi2) Ottawa River at Urban runoff/ storm P11K59 HELP/ WWH 11.67 154.0 27.0 4.34 22.0 63.0 NON Sedimentation/siltation Toledo @ Secor Rd. sewers 04100001 03 09 – Detwiler Ditch-Frontal Lake Erie Urban runoff/ storm Detwiler Ditch at Sedimentation/siltation P11S84 Toledo @ Detweiler HELP/ MWH 0.5 6.2 31.0 7.22 P 35.0 PARTIAL sewers, Park Priority organics Sediment resuspension a River Mile (RM) represents the Point of Record (POR) for the station and may not be the actual sampling RM. c MIwb is not applicable to headwater streams with drainage areas < 20 mi2. d A narrative evaluation of the qualitative sample based on attributes such as EPT taxa richness, number of sensitive taxa, and community composition was used when quantitative data was not available or considered unreliable. VP=Very Poor; P=Poor; LF=Low Fair; F=Fair; MG=Marginally Good; G=Good; VG=Very Good; E=Exceptional ns Nonsignificant departure from biocriteria (<4 IBI or ICI units, or <0.5 MIwb units). * Indicates significant departure from applicable biocriteria (>4 IBI or ICI units, or >0.5 MIwb units). Underlined scores are in the Poor or Very Poor range. H Headwater site (draining ≤20 miles2). W Wading site (non-boat site draining >20 miles2). B Boat site (large or deep waters, necessitating the use of boat sampling methods) Proposed Actions Ohio EPA considers many factors when deciding how to address impairments. For some projects, no TMDL is required. The watershed may be in attainment or the impairment is being addressed by another program/entity so no further action by the Division of Surface Water is necessary. Additionally, the cause of impairment may be natural (i.e., flow or habitat), in which case no action is required. For those needing a TMDL, the complexity of each impairment—including the primary origin of the pollutant, its delivery mechanisms and the waterbody kinetics involved—will determine the complexity needed in a model.
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