The Borehole Permeameter Approach for Stormwater Infiltration Testing

Similar documents
StormCon August 2017

Determination of Design Infiltration Rates for the Sizing of Infiltration based Green Infrastructure Facilities

Presented by: David Albus, RCE, GE

CHAPTER 4 GEOTECHNICAL SITE CHARACTERIZATION

How & Where does infiltration work? Context: Summary of Geologic History Constraints/benefits for different geologic units

SOURCES OF WATER SUPPLY GROUND WATER HYDRAULICS

Determining Infiltration Rates: Approaches, Challenges & Lessons Learned

AN APPROACH FOR ESTIMATING INFILTRATION RATES FOR STORMWATER INFILTRATION DRY WELLS

Native Soil Assessment for Small Infiltration- Based Stormwater Control Measures

Infiltration Testing For Stormwater BMPs: What Would Mickey Mouse Do?

UC SANTA CRUZ NATIVE SOIL ASSESSMENT FOR SMALL INFILTRATION BASED STORMWATER CONTROL MEASURES

Stormwater Standards. Clackamas County Service District No. 1. Infiltration Testing Guide

Recharge Capacity Assessment Tulare Irrigation District. HydroMetrics Water Resources Inc. Montgomery & Associates

City of Vineland Health Department 640 E. Wood Street, Vineland, NJ (856) (ph.) / (856) (fax)

STORMWATER MANAGEMENT. 158 Attachment 2. Borough of Perkasie

Water Related Soil Properties

AESI AESI 6/17/2015 HOW AND WHERE DOES INFILTRATION WORK? o Context: Summary of Geologic History. o Constraints/benefits for different geologic units

Transient Seepage Analyses of Soil-Cement Uplift Pressures During Reservoir Drawdown

Stormwater Retention Pond Recovery Analysis

ADMINISTRATIVE MANUAL COUNTY OF LOS ANGELES 6/30/17 DEPARTMENT OF PUBLIC WORKS GEOTECHNICAL AND MATERIALS ENGINEERING DIVISION

Bioreactor Implementation and

Atterberg limits Clay A Clay B. Liquid limit 44 % 55% Plastic limit 29% 35% Natural water content 30% 50%

BENEFITS IN SITU HYDRAULIC CONDUCTIVITY TESTS P Hooghoudt test kits

Novel Modeling Approach to Understand the Fate of Infiltrated Water at Green Stormwater Infrastructure in Philadelphia, PA

BURLINGTON COUNTY HEALTH DEPARTMENT 15 PIONEER BOULEVARD, WESTAMPTON PO BOX 6000 MOUNT HOLLY, NEW JERSEY 08060

Effect of the Underlying Groundwater System on the Rate of Infiltration of Stormwater Infiltration Structures.

Shelbyville, Kentucky Stormwater Best Management Practices (BMPs) Stormwater Pollution Treatment Practices (Structural) DRAFT

A-2. Soils. Soil Media. Chapter Contents. Soil Media In-situ Soil Testing Separation from Seasonal High Water Table (SHWT)

ENGINEERING HYDROLOGY

Groundwater Mounding Causes, Issues and Prevention

Soil Water Relationship. Dr. M. R. Kabir

GROUND WATER RECHARGE

GROUNDWATER TABLE HYDRAULIC IMPACT ASSESSMENT GUIDE FOR INFILTRATION BMPS

Grouting Bilfinger Spezialtiefbau GmbH

SUPPORTING DOCUMENT STORMWATER BEST MANAGEMENT PRACTICE (BMP) INFEASIBILITY WORKSHEET FOR ON-SITE STORMWATER MANAGEMENT

Estimating K sat for Infiltration Assessment WSDOT Approach

Dewatering Fly Ash for Remediation: Two Approaches

PRACTICE NOTE 1: In Situ Measurement of Hydraulic Conductivity

Source of Pollution or Groundwater Solution?

The following sections provide the approved standard infiltration testing specifications.

POROSITY, SPECIFIC YIELD & SPECIFIC RETENTION. Physical properties of

Re: Geotechnical Consultation for Storm Infiltration Robert Louis Stevenson ES Modernization th Avenue San Francisco, California

Design Guideline for Gravity Systems in Soil Type 1. January 2009

Agry 560 Exam November 7, 2002 (135 points) (10 pages)

Water Well Decommissioning Guidelines

mtec REPORT OF GEOTECHNICAL EXPLORATION FTFA Construct Bin Wall at HERD Eglin AFB, Florida

***NO SEPTIC SYSTEM EXCAVATION WITHOUT AN APPROVED PERMIT IN POSSESSION****

CITY UTILITIES DESIGN STANDARDS MANUAL

November 13, IP3406. Mr. Uriah Sowell Rooney Engineering 115 Inverness Drive East, Suite 300, Englewood, CO 80112

Code No: RR Set No. 1

Sump Pump Feasibility Review Summerside West Residential Development - Phases 4, 5 and 6 Tenth Line Road - Ottawa, Ontario

November 13, IP3406. Mr. Uriah Sowell Rooney Engineering 115 Inverness Drive East, Suite 300, Englewood, CO 80112

3. FIELD INVESTIGATION PROGRAM

WELL DECOMMISSIONING

3.2 INFILTRATION TRENCH

VERTICAL BARRIERS SLURRY TRENCH BARRIERS: excavation equipment. prof. E. Fratalocchi Environmental Geotechnics Waste and polluted sites containment

Water Resources Management Plan

Water Budget IV: Soil Water Processes P = Q + ET + G + ΔS

Groundwater 3/16/2010. GG22A: GEOSPHERE & HYDROSPHERE Hydrology

Appendix C Geotechnical Soil Testing Data

North End and South End Section Hauled Wastewater Receiving Facilities Page 1 Bid Opportunity No

SEMBODAI RUKMANI VARATHARAJAN ENGINEERING COLLEGE SEMBODAI BACHELOR OF ENGINEERING DEPARTMENT OF CIVIL ENGINEERING QUESTION BANK

REFERENCES AND DESIGN AIDS FOR ENVIRONMENTAL RESOURCE PERMIT APPLICANT S HANDBOOK VOLUME II

Bioreactor Landfill Design

9. SOIL PERMEABILITY. 9.0 Why is it important to determine soil permeability?

Alteration/Expansion or Change in Use Alteration/Malfunctioning System Deviation from Standards Repairs to Existing System

SMALL WASTEWATER FACILITY APPLICATION PACKET

Memorandum. Introduction. Carl Einberger Joe Morrice. Figures 1 through 7

WARNING DO NOT BID ON THIS PROJECT

November 2007 DRAFT Appendix E: Soil Testing Criteria

Water Wells for Florida Irrigation Systems 1

4. Groundwater Resources

DESIGN PARAMETERS FOR MULTI-PHASE EXTRACTION SYSTEMS USING UNSATURATED AND SATURATED SOIL PROPERTIES

CHAPTER 32 - WELL ABANDONMENT ORDINANCE OF DUBUQUE COUNTY, IOWA. Adopted September 5, Part 1 Introduction...2

Concurrent Session B: LID Design Specifications (Chapter 4 in Draft Manual)

SOIL MECHANICS Assignment #4: Soil Permeability.

GREEN CITY, CLEAN WATERS

Northern Nevada Water Planning Commission

REPORT OF SUBSURFACE EXPLORATION AND GEOTECHNICAL ENGINEERING SERVICES

Water for the World. Methods of Developing Sources

Background. AEM Tier 2 Worksheet Farmstead Water Supply Evaluation. AEM Principle: Glossary

Applicant s Handbook, Volume II (including Appendices A through F`) is Incorporated by Reference in Rule , F.A.C.

Published by: PIONEER RESEARCH & DEVELOPMENT GROUP ( 1

To The Applicant For A Small Wastewater System Permit Sheridan County, Wyoming

PONDS 3.2 TECHNICAL MEMO

MEMORANDUM. TO: STUART OLSON DOMINION CONSTRUCTION LTD. DATE: JANUARY 31, 14 ATTENTION: MR. Dave Bauder, Construction Manager KENNY K. C.KO, P.ENG.

GRAY WATER RECYCLING SYSTEMS

STORMWATER INFILTRATION TESTING AT DEPTH

Infiltration Guidelines

Underground Heterogeneity 9/5/2017. Groundwater Monitoring Well Construction. Groundwater Sampling. Groundwater Movement and Related Terms.

Standard Guide for Comparison of Field Methods for Determining Hydraulic Conductivity in the Vadose Zone 1

Groundwater Control for Design & Construction

The ability of water to flow through a saturated soil is known as permeability.

1. Apply knowledge of the controlling variables for groundwater flow. 2. Demonstrate groundwater flow direction based on hydraulic head observations.

Homework # 4 - Solutions Fluid Flow (5 problems)

CHAPTER 5 WELL CONSTRUCTION

April 7, Webster Street Sub-Surface Stormwater Storage System Bid No Bid Date: 4/13/17 ADDENDUM NO 1

STANDARD OPERATING PROCEDURES

204 - EXCAVATION AND BACKFILL FOR STRUCTURES SECTION 204 EXCAVATION AND BACKFILL FOR STRUCTURES. Granular Backfill (Wingwalls) (Set Price)

Design of Stormwater Wetlands

Transcription:

The Borehole Permeameter Approach for Stormwater Infiltration Testing AWRA National Conference J. Scott Kindred, PE Kindred Hydro, Inc. November 9, 2017

Topics Covered Borehole permeameter (BP) equation Updating the Pilot Infiltration Test (PIT) approach Borehole Infiltration Test Approach (BIT) Small-scale hand dug holes Vactor explorations Drilled wells Predicting performance of infiltration facilities Thanks to Chris May at Kitsap County and John Phillips at King County for supporting use of these methods on their projects.

The Most Important Take-Away Infiltration rate is not a soil property! Infiltration rate depends on: Hydraulic conductivity (K) which is a soil property Hydraulic gradient Facility geometry Stratigraphy Depth to groundwater (sometimes)

Soil is a 3-D Water Conveyance System Hydraulic conductivity (K) is a 3-D vector For our purposes, 2-D is sufficient Water-deposited soils are layered, so vertical K (Kv) is less than horizontal K (Kh) Anisotropy ration: 1 < Kh/Kv < 10 Borehole tests weighted towards Kh Shallow horizontal test facilities weighted towards Kv Use of term Bulk K represents our inability to evaluate anisotropy

Borehole Permeameter (BP) Approach (Also referred to as Constant Head Well Permeameter Approach, Reynolds, 2008) Hydrostatic Pressure Flow K= CCCC 2πHH 2 + πrr 2 C + 2ππHH αα EEEEEEEEEEEEEEEE 1 Vertical Gravity Flow Capillarity Flow Where: K = Field saturated bulk hydraulic conductivity (feet/day) Q = Steady state flow (cubic feet/day) H = Steady State head/ponding Depth (feet) r = Radius of borehole(feet) αα = Porous media sorption number (1/feet) C = Shape factor (dimensionless) Where: C = H L r Z 1 +Z H 2 L r Z 3 Zhang et al., 1998

PIT and USBR Equations Compared with BP Equation BP Equation: K= CCCC 2πHH 2 + πrr 2 C+ 2ππHH αα USBR Equation: K= CCCC 2πHH 2 PIT Equation: K= QQ πrr ee 2 Where: K = Field saturated bulk hydraulic conductivity (feet/day) Q = Steady state flow (cubic feet/day) H = Steady State head/ponding Depth (feet) r = Radius of borehole(feet) αα = Porous Media sorption number (1/feet) C = Shape factor (dimensionless)

Capillary and Shape Factor Parameters Zhang et al, 1998 Soil Type α * (feet -1 ) Z 1 Z 2 Z 3 1) Compacted clays 0.3 2.081 0.121 0.672 2) Unstructured fine-grained 1.2 1.992 0.091 0.683 porous media 3) Structured fine grained 3.7 2.074 0.093 0.754 porous media or unstructured fine-medium sandy media 4) Structured fine-medium sandy porous media and coarse-grained gravelly 11 2.074 0.093 0.754 media Most porous media of interest for infiltration are Type 3. Decreasing Capillary Flow Effect

Numerical Simulation of Falling Head Attached is a computer simulation (based on Richards equation for variably saturated flow) of falling head in an uncased borehole after initially achieving steady flow at constant ponded head (50 cm in this case). Note that the field-saturated zone around the borehole (i.e. volume inside the dashed blue line which represents zero pore water pressure head) contracts uniformly back toward the borehole as the ponded head falls toward zero. Below are the simulated vertical and horizontal pore water pressure head gradients along the base of the borehole when the ponded head is near zero (about 2.2 mm). The vertical gradients are substantially greater than zero along the entire borehole base, so the hydraulic head gradient does not approach unity as the borehole empties.

BP Assumptions Isotropic (Vertical K = Horizontal K) Uniform K within test interval Steady state No groundwater table or perching layer near bottom of test excavation/boring One or more of these assumptions generally not met, Results reported as Bulk K

Mounding Effects of Nearby Groundwater Table Water table initially 25 cm below base of borehole at start of constant head phase

Types of BP Tests Valid for any scale from hand-auger borings to 100 feet deep drilled wells.

Standard Pilot Infiltration Test (PIT)

Standard PIT

Standard PIT Analysis vs. BP Analysis Analysis Approach Standard PIT: Fixed Head Standard PIT: Falling Head Estimated K (inch/hour) 8.1 5.5 BP Approach 4.1

PIT Approach Only Accounts for Vertical Gravity Flow (2 nd term in BP equation)

What Actually Happens During a PIT

PIT Approach Bulk K Error Small-Scale PIT 60% Over-Estimate Large-Scale PIT 25% Over-Estimate

US Bureau of Reclamation 7300 Approach USBR approach only accounts for hydrostatic pressure flow (first term in BP equation) Doesn t address vertical gravity flow or capillarity flow (thus not useful for tests in open excavations, i.e., when H/r is small) USBR used less accurate Zanger, 1953 shape factor CC = sseeees 1 HH rr rr HH 2 rr + 1 + HH

Bureau of Reclamation Bulk K Error Over-predicts K when H/r is small Under-predicts K when H/r is large due to inaccurate shape factor

New Infiltration Test Methods Falling head in open excavation (updated PIT) Infiltration testing in hand-dug holes Infiltration testing in vactor explorations Infiltration testing in drilled borings

Falling Head Tests in Open Excavation Stage Using Q = Infiltration Rate * Area BP analysis provides K= 1.6 inch/hour Steady state achieved after about 60 minutes Infiltration Rate Advantages: Doesn t require meter Facilitates multiple tests per day

Multiple Refills May be Needed Stage BP analysis provides K= 6.9 inch/hour Steady state achieved after about 120 minutes Infiltration Rate

Borehole Infiltration Test (BIT) in Hand Dug Holes More Accurate than RainWise perk test 2-3 hours/test Can be performed by homeowner or contractor

Hand Dug Steady State Borehole Test Water Added (gal) 0.8 0.7 0.6 0.5 0.4 0.3 0.2 0.1 0.0 Hand Dug Borehole Infiltration Test Initial Infiltration Rate = 15 inch/hr 0 0 30 60 90 120 150 180 210 240 270 300 Time (minutes) Bulk K= 0.8 inch/hr 3-10 gallons/test 1-3 hours/test Final Infiltration Rate = 1.7 inch/hr 32 28 24 20 16 12 8 4 Head (inch) and Infiltration Rate (inch/hour) Water Added (gal) Head (ft) Infiltration Rate (inch/hr)

Vactor Explorations Advantages: Minimal disturbance Less likely to break utilities Vactor Exploration Loosen soil with high-pressure water jet, air-knife, or pry-bar Excavate using vactor truck Collect soil samples using hand auger Up to 10 ft deep with no well permit

Infiltration Test in Vactor Explorations Build Temporary Test Well 2-inch PVC well screen and casing Fill annular space with pea gravel Conduct Borehole Test Use vactor truck water tank Use transducer to measure water levels during fixed head and falling head portion of test Abandon well by pulling casing and replacing dirt and sod Daily Production 20-450 gallons/test Average ~200 gallons/test for Qva With 1,000 gal tank on Vactor truck, average 5 tests/day

BP Results in Vactor Exploration Stage BP analysis of fixed head provides bulk K = 2.3 inch/hr Infiltration Rate Flow

BH Approach in Drilled Boreholes Production Rate: 1,500-12,000 gal/test Average ~7,000 gal/test for Qva Ran 2 water trucks and completed 3 tests/day

BH Results in Drilled Boring Flow BP analysis provides bulk K = 19 inch/hr Stage

Characterizing Infiltration Feasibility Using these Methods 23 Vactor Explorations 14 Drilled Wells

Estimating Design Infiltration Capacity Capillary Flow Q m = K 2πH m 2 C + πr 2 + 2πH m Cα Hydrostatic Pressure Flow Vertical Gravity Flow Where: K = Bulk hydraulic conductivity (feet/day) Q m = Maximum flow capacity (cubic feet/day) H m = Maximum ponded head (feet) r = Effective radius (feet) α = Porous medium sorption number = ~3.7 (1/feet) C = Shape factor (dimensionless) Where: C = H L r Z 1 +Z H 2 L r Z 3 Zhang et al., 1998

Deep Infiltration Drain Capacity 10-inch diameter wells

Final Thoughts Open excavation, shallow head test with BP analysis provide Bulk K with a vertical K bias Best suited for sizing shallow BMPs using vertical infiltration Borehole test with BP analysis provide Bulk K with a horizontal K bias Best suited for designing BMPs with vertical infiltration drains BIT should be acceptable approach for sizing BMPs that rely on vertical infiltration with appropriate safety factor Future topics: Effects of groundwater or perching layer beneath test facility Effects of anisotropy Effects of permeability changes within tested horizon

More Information Scott Kindred, PE ScottK@KindredHydro.com 206-660-5417 www.kindredhydro.com