Below Water Table Sites Borrow Pit Dewatering Below Water Table Sites OUTLINE • Administrative Issues • Basics of gravitational settling • Relationship between: – Basin volume – Detention time, and – Pump rate. • Borrow Pit as a Stilling Basin. • Tier I Methods – Stilling Basins • Tier II Methods CCPCUA Requirements • Central Coastal Plain Capacity Use Area – Affects 15 Counties in Eastern NC. • Locate number of wells within 1500 feet of pit. boundary – Use Latitude and Longitude Coordinates • Determine whether adjoining dwellings are served by county/municipal water supplies. • Contractor to assume liability for impacts to wells and surface waters. • Average daily pump rate. • Estimate number of pumping days for life of pit. • Pit water elevation prior to pumping. • Pit water elevation after pumping. Below Water Table Sites Turbidity Limits Surface Water Classification Streams Lakes & Reservoirs All Trout Waters Turbidity Not to Exceed Limit* (NTU’s) 50 25 10 * Turbidity may not exceed upstream background levels. If background levels are less than the above limits, the above limits must be met. 1 Below Water Table Sites Focus of This Discussion • To find a low-cost, convenient way to get the sediment entrained in the borrow pit water from the water. • Let’s look at several possibilities. Below Water Table Sites Settling Velocity and Detention Time • Using the Continuity Equation, Q = AV (Clarifier Theory) – Q = Pump Rate, L3/T – Vs = Settling velocity, L/T – A = Surface Area required to remove sediment (by gravity), L2 • Therefore: A = Q/Vs Settling Velocity Below Water Table Sites Below Water Table Sites Stilling Basin Requirements 10000.0 4 MGD 3 MGD 2 MGD 1 MGD Area Required (acres) 1000.0 0.5 MGD 0.25 MGD 100.0 SILT 1.0 0.1 0.0001 0.001 0.01 • To use gravitational settling to remove clays (even silts) is unreasonable. • Need either: – Excessive detention times, or – Excessive basin volumes. 10.0 CLAY Conclusions 0.1 • May need additional technology to yield the required NTU-Levels. Particle Diameter (mm) 2 The Borrow Pit Below Water Table • Detention Time, td (Q = Pump Rate) Sites V td = Q Below Water Table Sites Suggestion • Use a step-wise, progressive approach: – First, try simpler/cheaper technology (Stilling Basins). – If Stilling Basins do not yield the desired NTU levels, • Basin Volume, V is a function of td and Q) V = td Q • ADD additional/better technologies. Break for Worksheet; #21 Below Water Table Sites Borrow Pit an the Stilling Basin • With few minor considerations you maybe able to use the borrow pit and its rim ditch as a stilling basin. • The key is to eliminate (at least minimize) resuspension of sediments from within the borrow pit when the pit is pumped. Borrow Pit as the Stilling Basin Below Water Table Sites 3 Below Water Table Sites Borrow Pit as a Stilling Basin (Present) Borrow Pit as a Stilling Basin (Desired) Water Flow Water Flow Plastic or Filter Fabric Borrow Pit as a Stilling Basin (Desired) Water Flow Below Water Table Sites • Tier I Methods – – – – – – Outline Stilling Basin for Pumped Effluent Land Application (Irrigation) Silt Bags Alum Gypsum Polyacrylamide (PAM) • Tier II Methods [Rare & unique resources] – – – – – Well Point Pumping Impoundments Cell Mining Sand Media Filtration Wet Mining Break for Worksheet; #22 4 Below Water Table Sites The Next Step! • If the water pumped from the Borrow Pit does not meet the required NTU levels, THEN Below Water Table Sites – Land Application (Irrigation) – Silt Bags – Alum – Gypsum – Polyacrylamides (PAM) – Pump the Borrow Pit water into a Stilling Basin. – Full Example in next module. Below Water Table Sites Irrigation • Pump the borrow pit water into and through a sprinkler irrigation system. • Irrigated water must be able to infiltrate into the soil. • Infiltrated water should be sediment free. The Next Step! • If the water leaving the Stilling Basin has an NTU level that is too high, Look to other Tier I Methods. Below Water Table Sites Irrigation 5 Special Stilling Basin (Silt Bag) • Geotextile bag that filters sediment from pumped water. • Used for small jobs near streams where basins do not work well. • Class A stone placed LEVEL under the silt bag. Below Water Table Sites Flocculants • Alum (Aluminum Sulfate) • Gypsum • Flocculants that are rarely used. PAM • Polyacrylamides (PAM) are polymers (of proprietary formulations). – Available as liquids, powders, or in solid form in “floc-logs”. – Different formulations of PAM work better in different soils. PAM Mixing • Should be applied at rate of about 1 mg/L. – Flow 60 to 80 gpm over one Floc-Log in turbulent flow. • Inside a corrugated plastic pipe (no inner liner). • Must have turbulent contact with the water flowing past the logs. – Powder • Mix 1 pound of PAM per 100 gallons of water. 6 PAM Injection Below Water Table Sites PAM Injection Rate 4.0 PAM Injection Rate (gpm) Below Water Table Sites 3.5 3.0 2.0 1.5 1.0 0.5 0.0 500 1000 1500 2000 2500 3000 Pump Rate (gpm) Below Water Table Sites PAM • Follow PAM application with a stilling basin. – Stilling Basin; td = 2hrs • Use skimming outlet • Use 3 porous coir baffles • Use a near bottom inlet • Break for Worksheet; #23 • Following appropriate mixing: – Clay flocs form quickly. – Flocs should settle from water column in 2 to 6 hours. – Some flocs may float. – Porous baffles help to capture flocs. 2.5 0 PAM The Next Step! Below Water Table Sites • If one of the Tier I approaches does not yield water with an appropriate NTU level, • OR you have rare or unique resources on the site, look to Tier II Methods. – – – – – Well Point Pumping Impoundments Cell Mining Sand Media Filtration Wet Mining 7 Below Water Table Sites Well Point Pumping • Place a row(s) of sand point wells into the bottom of the borrow pit. • Connect all wells to the pumping system. • Pump all wells simultaneously. Well Point Pumping Below Water Table Sites Water Removed via wells & Filtered in the process – Pumped water draws the water down through the bottom of the borrow pit. • Filtered water should be sediment free. Below Water Table Sites Impoundments • Pump polluted water into large impoundments. – Let the water stand until the water quality improves sufficient to permit stream discharge. Below Water Table Sites Cell Mining • Divide the borrow Pit into several large cells separated by embankments. • Pump the polluted water from the working cell into an unused cell. Let the water stand until its water quality improves and it can be discharged. 8 Below Water Table Sites Sand Media Filtration • Key component is chitin, a coagulant/flocculant processed from the shells of crab, shrimp, or lobster. – Can be applied as a liquid (Liqui-FlocTM) • Waters with 100 to 700 NTU • Waters with pH of 6.5 to 8.5 – Can be applied as a gel (Gel-FlocTM) • Waters with > 700 NTUs. • Coagulated/flocculated clays must be removed from the water by filtration. Below Water Table Sites Wet Mining • Excavate from the borrow pit under the water level. • Stack the excavated material above the water. – Gravitational water will drain from the material. – Drained material can then be taken to construction site. Wet Mining Below Water Table Sites Questions? Water Flow 9