Asylum Lake Assessment Following BTR2 Sediment Loss Event Mark S. - - PowerPoint PPT Presentation

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Asylum Lake Assessment Following BTR2 Sediment Loss Event Mark S. - - PowerPoint PPT Presentation

Preliminary ry Findings: Asylum Lake Assessment Following BTR2 Sediment Loss Event Mark S. Kieser, Senior Scientist Doug McLaughlin, PhD, Env. Engineering Manager Kieser & Associates, LLC 536 E. Michigan Ave., Suite 300 Kalamazoo, MI


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Preliminary ry Findings: Asylum Lake Assessment Following BTR2 Sediment Loss Event

Mark S. Kieser, Senior Scientist Doug McLaughlin, PhD, Env. Engineering Manager

Kieser & Associates, LLC 536 E. Michigan Ave., Suite 300 Kalamazoo, MI 49007 July 11, 2019 Presentation to the Asylum Lake Policy and Management Council

  • n behalf of Western Michigan University
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SLIDE 2

K&A Scope

  • Initial characterization of the 6/19-20 BTR2 erosion event with

respect to suspended solids and phosphorus concentrations, water clarity, and arsenic transport to Asylum Lake

  • Identification of potential short-term/long-term impacts to Asylum

Lake associated with the erosion event

  • Assessment of additional sampling needs to characterize extent of

potential arsenic transport to Asylum Lake

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SLIDE 3

Runoff Event Information

  • Rainfall of 3-4 inches over June 19-20th
  • Asylum Lake Preserve aerial drone video and photos from June 20th

after erosion event started

  • WMU asked K&A on June 20th to undertake a 3rd party evaluation of

the erosion event

  • K&A site inspections and sampling began morning of June 21st
  • K&A observations noted site erosion corrections being addressed by

contractor on June 21th

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Precipitation – June 1-25, 2019

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K&A Activities Timeline Overview

  • June 21 – first water and sediment sampling event
  • June 24 – site inspection/assessment to evaluate likely sediment flow path
  • June 25 – first drone video acquired on behalf of WMU
  • June 25 – second site inspection
  • July 2 – second water and sediment sampling event
  • July 3 – third site inspection
  • July 3 – second drone video acquired on behalf of WMU
  • July 9 – third water sampling event
  • July 11 – ALPMC presentation
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SLIDE 6

K&A Storm Event Runoff Flow Path Assessment

Likely water/ sediment transport pathways

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Asylum Lake Characteristics for Background

  • 46.5 acres surface area, maximum 50-feet deep
  • 588 acres of drainage
  • Hydraulic residence time about 7 months
  • Historic stormwater runoff from:
  • Orchards
  • Former power plant
  • Farmland
  • Commercial businesses
  • Apartments
  • Trailer park (with septic systems)
  • Roadways
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SLIDE 8

Contributing and Non-contributing Watershed Areas for Asylum/Little Asylum Lake (from K&A, 2008)

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Aerial Drone Video Assessment

  • No other known drone video prior to the event for comparison
  • Asylum Lake Preserve drone videos 6/20/19 – initial impact
  • Transport of highly turbid water to wetland and lake over Drake Road and

through ditch/wetland west of Drake Road

  • WMU drone video #1, 6/25/19
  • Indicates improved water clarity compared to 6/20/19
  • WMU drone video #2, 7/3/19
  • Indicates somewhat improved water clarity, but also shows considerable new

growth of filamentous algae near west end of lake also observed during 7/2/19 sampling event

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SLIDE 10

K&A Sampling Locations

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K&A Photos

June 21 – wetland just east of Drake looking east June 21 – wetland just east of Drake looking west

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K&A Photos (con’t.)

June 21 – accumulated sediment

  • n the east side of Drake Road

composite sampled for heavy metals; looking south

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K&A Photos (con’t.)

June 21 – culvert discharge just east

  • f Drake Road

looking east

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K&A Photos (con’t.)

June 21 – ‘rivulets’ sampled in wetland just east of Drake looking northwest

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K&A Photos (con’t.)

June 21 – Asylum Lake S5 station looking north June 21 – Asylum Lake S4 station looking northwest June 21 – Asylum Lake S3 station looking west

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K&A Photos (concluded)

June 24 – ditch west of Drake road culvert looking west June 24 – ditch just west of Drake road culvert looking south

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Asylum Lake Monitoring Data

a Engemann, E. (circa) 1977. “Observations on Asylum Lake, Kalamazoo, Michigan.” unpublished. (NOTE: Bottom water TP in Sept. 1976

was 1,500 ppb.)

b Kieser & Associates, LLC. (K&A) 2008. “Water Quality Evaluation of Asylum Lake and Little Asylum Lake with Management

Recommendations.” Prepared for WMU Asylum Lake Policy and Management Council, May 5, 2008, 194pp. (NOTE: Bottom water TP in

  • Aug. 2006 was 565 ppb; SRP was 334 ppb.)

c K&A preliminary monitoring results following the BTR2 erosion discharge to Asylum Lake.

Date Total Phosphorus - TP (ppb) Soluble Reactive Phosphorus - SRP (ppb) Total Suspended Solids - TSS (ppm) Secchi Depth (ft) Turbidity (NTU) 7/26/76a “Non-detect”

  • 11.5 - 16.5
  • 8/9/06b

13 - 22 2 - 3 <4 12.5 6/21/19c 30 - 110

  • 7 - 20

2.8 – 3.8 23 - 35 7/2/19c 30 - 80 5 - 24

  • 7/9/19c

pending pending pending 10.5 - 11 23 - 24.5

Historic Recent

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Historic Asylum Lake Stormwater Conditions

Date TP (ppb) SRP (ppb) TSS (ppm) Asylum Lakeb (Sept. 2006) 99 - 498 6 - 255 3 - 46 Asylum Lakeb (July 2007) 299 - 326 121 - 247 4 - 76

b Kieser & Associates, LLC. (K&A) 2008. “Water Quality Evaluation of Asylum Lake and Little Asylum Lake

with Management Recommendations.” Prepared for WMU Asylum Lake Policy and Management Council, May 5, 2008, 194pp.

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SLIDE 19

Arsenic Water Sampling in Asylum Lake

Date Water Sampling Location Arsenic Concentration (ppb) 6/21/2019 S1 3 6/21/2019 S2 3 6/21/2019 S3 2 6/21/2019 S4 <2 (non-detect) 7/2/2019 S1 <2 (non-detect) 7/2/2019 S2 <2 (non-detect) 7/2/2019 S3 <2 (non-detect) 7/2/2019 S4 <2 (non-detect) 7/9/2019 S1 pending 7/9/2019 S2 pending 7/9/2019 S3 pending 7/9/2019 S4 pending Water Quality Criteria for Comparison: Criterion Value (ppb) Cate- gory Definition 10 HNV- Drink Human non-cancer value, includes drinking water exposure 280 HNV Non- drink Human non-cancer value, does not include drinking water exposure 10 HCV- Drink Human cancer value, includes drinking water exposure 10 HCV- Non- drink Human cancer value, does not include drinking water exposure 150 FCV Final Chronic Value (aquatic life) 340 AMV Aquatic Maximum Value (aquatic life) 680 FAV Final Acute Value (aquatic life)

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Asylum Lake Sediment Sampling Results

1 Table 2. Soil: Residential Part 201 generic cleanup criteria and screening levels/Part 213 risk-based screening levels. 2 Table 3. Soil: Non-residential Part 201 generic cleanup criteria and screening levels/Part 213 risk-based screening levels.

Surficial (top 0.5-in) Composite Sediment Sample >> Curb/ Gutter (ppb) Creek Bed (ppb) Creek Bed (ppb) Wetland Soil Surface (ppb) Non-residential Direct Contact Criteria2 (ppb) EGLE WRD- 048 Table 2 Aquatic Life and Wildlife Screening Guidelines (ppb) Statewide Default Background Level (ppb)1 Residential Direct Contact Criteria1 (ppb) Date >> 6/21/2019 6/21/2019 7/2/2019 7/2/2019 Arsenic 420 1,180 1,980 12,700 37,000 33,000 5,800 (<300-22,800) 7,600 Barium 2,960 16,900 pending pending 130,000,000 none 75,000 37,000,000 Cadmium <200 <200 pending pending 2,100,000 4,980 1,200 550,000 Chromium 640 6,730 pending pending 9,200,000 111,000 18,000 2,500,000 Copper 1,620 9,030 pending pending 73,000,000 149,000 32,000 20,000,000 Lead 830 28,100 pending pending 900,000 128,000 21,000 400,000 Mercury <50 <50 pending pending 580,000 1,060 130 160,000 Selenium <400 570 pending pending 9,600,000 1,900 410 2,600,000 Silver <200 <200 pending pending 9,000,000 none 1,000 2,500,000 Zinc 4,120 55,800 pending pending 630,000,000 459,000 47,000 170,000,000

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Preliminary Findings

  • Low to non-detect Arsenic measured in water from wetland and lake has

shown no exceedances of relevant water quality criteria

  • Loss of Arsenic-contaminated soils via erosion event appears to have been

limited

  • Comparatively low levels of Arsenic in representative curb/gutter soil sample
  • No exposed contaminated soils observed/reported at BTR2 erosion locations during

rain event

  • Some sediment was recovered from roadway and ditch west of Drake post-event
  • Observations of mostly fine sediment discharges to Asylum Lake and wetland
  • Evidence of legacy stormwater loading impacts on wetland sediment

contaminants (consistent with previous historic reporting)

  • Short-term phosphorus, turbidity, algal bloom impacts are evident
  • Limited historic sediment data/limited access to water quality data; both

needed to clearly establish baseline conditions from post-event conditions

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Next Steps

  • Finish data analysis with pending lab data
  • Assess need for additional monitoring
  • Short-term in-lake phosphorus conditions
  • Wetland/lake sediments for heavy metals
  • Updated presentation for summary findings on short-term/long-term

impacts and recommendations

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Questions?