Optimizing Resources for Restoring Streams Impaired by Acid Mine Drainage Paul Ziemkiewicz, Director West Virginia Water Research Institute West Virginia.

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Presentation transcript:

Optimizing Resources for Restoring Streams Impaired by Acid Mine Drainage Paul Ziemkiewicz, Director West Virginia Water Research Institute West Virginia University

Program Scope: Stream segments impaired by historic acid mine drainage Program Objective: To restore fisheries in the maximum number of stream miles

Treatment Options At source lime dosing with sludge collection and disposal In stream dosing: –Limestone sand dump stations –Pebble lime dosers At source passive treatment

WVDEP On Site Doser: Construction

Charging the Lime Bin

Sludge Cleanout

In Stream Dosing: Middle Fork Limestone Sand Station

In Stream Dosers: Maryland Boxholm Pumpkonsult Aquafix

In Stream Lime Dosing: Davis WV

North Branch: pH Before Doser Project

North Branch: pH After Doser Installation

On Site Passive Treatment: Open Limestone Channel

Ohio DNR: Slag Leach Bed

Ohio DNR: LCD-Lime-Cored Dam

Watershed-based versus At-source- based AMD Treatment: Costs and Benefits

A comparison of AMD treatment costs was made related to the following scenarios: Single AMD sources Multiple AMD sources Manganese sources. Methods

Parameters AMD Cost = S+C+A+O+D Site access S Construction C Alkalinity additionA Oxidation O Sludge disposalD Environmental efficiency = AMD Cost/ Recovered stream miles Treatment efficiency= AMD Cost/Tons of acid load removed

Cost Centers Capital Costs: doser installation, pond construction, roads (3,000 ft ea.) land access, ditching, engineering Annual Costs: water sampling, labor, operations and maintenance, chemical, sludge removal In Stream Dosing: Delete pond construction and sludge removal

Multiple AMD Sources S-91-85ROCKVILLE MINING WVDEP acid load Capital Annual sample # (tpy) cost 2Discharge pond #3 5 $ 65,698 $ 18,026 3Discharge pond #5 5 $ 65,698 $ 19,790 4Discharge pond #4 33 $ 125,698 $ 30,206 5Discharge pond #5 into sediment ditch 12 $ 125,698 $ 32,468 55seep to diversion ditch to Pond #5 3 $ 65,698 $ 20,018 totals: At source treatment 58 $ 448,490 $ 120,508 In Stream Doser in Martin Ck to Glade 330 $ 94,325 $ 91,601

At-source vs. In-stream costs StreamAcid Load 20-yrStreamRecovery Removal acid load Trt.Rec. Cost Efficiency Treatment Scenario(tpy) ($)(mi.) ($/mi/yr) ($/ton) A. single AMD, in stream , , A. single AMD, at source 12532, ,5142,211 B. multiple AMD, in stream 3301,926, , B. multiple AMD, at source 582,858, ,8652,468

Conclusions: In-stream AMD Treatment vs. At-source treatment Always treated more acid load Recovers more stream miles More expensive than at-source, single AMD Less expensive than multiple at-source treatment

Conclusions: Stream miles recovered In-stream treatment resulted in much higher stream recoveries (1.5 to 2.5 miles) At-source treatment stream recoveries were always less (0.1 to 0.8 miles) The Mn treatment project resulted in negligible stream recovery

Conclusions: Acid removal efficiency All three of the most efficient sites were in stream dosing units. At source: $2,200 to $272,000 In stream: $175 to $1,478 Or between 12 and 180 times more efficient

Conclusions: Acid removal efficiency ($/ton of acid load removed) All three of the most efficient sites were in stream dosing units. In-stream: $175 to $1,478 At source: $2,200 to $272,000 Or between 12 and 180 times more efficient In-stream efficiencies similar to on site passive

In-stream doser efficiencies similar to on site passive In Stream Dosing –Positives: High stream recovery –Alkalinity export Minor pre-design monitoring –Adjustable feed rate –Reliable performance Few treatment units Low cost –Low capital cost –High/predictable O&M cost Works under most site conditions At Source Passive –Positives: No in stream impacts Minimal maintenance Low cost –High capital cost –Low/variable O&M

In-stream doser efficiencies similar to on site passive In Stream Dosing –Negatives: Stream impacts-sludge –Extent of mixing and precipitation zone Regular maintenance At Source Passive –Negatives: Low stream recovery –Little if any alkalinity export Numerous treatment sites –Access agreements –Roads/maintenance Site-limited treatment options –Water quality –Space –Flows

With In-Stream Treatment We Need to Know: How many miles of stream are actually restored to biological health with in stream treatment? How quickly metal floc comes out of the water column Effects of metal loading, stream hydraulics: oxidation and floc settlement