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Conference<br />

Program<br />

<strong>Abstracts</strong><br />

HOSTED BY:<br />

International Association<br />

of Hydrogeologists -<br />

Canadian National Chapter<br />

IAH-CNC 2015 WATERLOO<br />

October 27 - 30, 2015<br />

Platinum Sponsors:


TABLE OF CONTENTS<br />

IAH-CNC 2015 Waterloo Organizing Committee.......................................... 2<br />

Greetings from the Chairs.......................................................................................... 3<br />

Greetings from the IAH-CNC.................................................................................... 4<br />

Greetings from the IAH................................................................................................. 5<br />

Platinum Sponsors........................................................................................................... 6<br />

Gold/Silver Sponsors...................................................................................................... 8<br />

Bronze/Other Sponsors ................................................................................................ 9<br />

Exhibitors............................................................................................................................. 10<br />

Hotel Floor Plans .............................................................................................................12<br />

Social Program..................................................................................................................14<br />

Wednesday Plenary Session ...................................................................................15<br />

Thursday Plenary Session .........................................................................................17<br />

Friday Plenary Sessions..............................................................................................19<br />

Conference Program & Timetable .......................................................................21<br />

Wednesday Program “At a Glance”....................................................................24<br />

Thursday Program “At a Glance”..........................................................................28<br />

Friday Program “At a Glance”................................................................................ 32<br />

Abstract Table of Contents ..................................................................................... 33<br />

<strong>Abstracts</strong>............................................................................................................................. 34<br />

Program accurate as of printing - October 14, 2015.<br />

IAH-CNC 2015 WATERLOO CONFERENCE<br />

1


IAH-CNC 2015 WATERLOO<br />

ORGANIZING COMMITTEE<br />

Conference Co-chairs<br />

Tammy Middleton, Region of Waterloo<br />

Stephen Di Biase, Aquatech Dewatering Company Inc.<br />

Technical Co-chairs<br />

Christopher J. Neville, SS Papadopulos & Associates Inc.<br />

Richard E. Jackson, Geofirma Engineering Ltd.<br />

Organizing Committee<br />

Lesley Veale, Stantec Inc.<br />

Nataliya Tkach, SPL Consultants Ltd.<br />

Tiffany Svensson, Blumetric Environmental Inc.<br />

David Rudolph, University of Waterloo<br />

Cailin Hillier, Municipal Water Consortium at Canadian Water Network<br />

Peter Gray, MTE Consultants Inc.<br />

Conference Management<br />

Wayne Gibson, Gibson Group Management Inc.<br />

Lisa McJunkin, Gibson Group Management Inc.<br />

2 IAH-CNC 2015 WATERLOO CONFERENCE


GREETINGS FROM THE CHAIRS<br />

Welcome to Waterloo 2015! On behalf of the entire<br />

organizing committee we extend our thanks<br />

for joining us at the 2015 conference of the Canadian<br />

National Chapter of the International Association<br />

of Hydrogeologists.<br />

Hydrogeology is becoming a “mature science” in<br />

Canada and it is time to celebrate our Canadian,<br />

professional association for hydrogeologists.<br />

What better place to do so than Waterloo - for<br />

years the centre of hydrogeology education in Canada and which is the alma mater for<br />

many hydrogeologists. By joining us at this conference, you are taking an active part in<br />

your continuing education as professional hydrogeologists. And we also hope that you will<br />

continue on as active members of the IAH-CNC, and help us foster a thriving professional<br />

association for Canadian hydrogeologists.<br />

Supporting the IAH in Canada is only one of our conference objectives- other priorities<br />

are to provide a high-quality technical agenda and to have FUN. We hope you agree<br />

that we met all our objectives- our successes are due entirely to the excellent and talented<br />

volunteer organizing committee for this conference- who started work over two years ago.<br />

Many thanks to the organizing committee (led by Lesley Veale, Nataliya Tkach, Peter<br />

Gray, Tiffany Svensson, and Cailin Hillier), and to the technical co-chairs Chris Neville<br />

and Dick Jackson, and their team of session chairs.<br />

We are extremely grateful for the support of our sponsors and exhibitors. Please take the<br />

time to visit the sponsor and exhibitor booths (open throughout the conference) and show<br />

your appreciation for their participation. We could not hold the conference without them.<br />

The technical program includes three plenary sessions: on October 28th, Dr. Rainer Helmig<br />

will present the National Ground Water Association 2015 Darcy Lecture. Dr. John<br />

Cherry will present the plenary lecture on October 29. The morning of Friday, October<br />

30th opens with a plenary lecture by Dr. Ian Clark followed by a special plenary session<br />

chaired by Dr. Cathy Ryan and including presentations by Dr. Richard Jackson, Dr. Jim<br />

Barker, Dr. Emil Frind, Dr. Robert Gillham, Dr. William Alley, and Dr. Garth van der<br />

Kamp. And we hope all attendees will join us on the afternoon of October 30, for the<br />

annual Farvolden Day event at the University of Waterloo, featuring Dr. David Rudolph<br />

as the Farvolden Lecturer.<br />

The IAH-CNC has put priority on support for students and young professionals in hydrogeology.<br />

Our thanks go to the YP volunteers who have been working to create a welcoming<br />

environment for our early career colleagues. To those of us who are merely “young at<br />

heart”, we hope you take the chance to connect with the YP contingent at the conference.<br />

Please enjoy the conference!<br />

Tammy Middleton<br />

Region of Waterloo<br />

Stephen Di Biase<br />

Aquatech Dewatering Company Inc.<br />

IAH-CNC 2015 WATERLOO CONFERENCE<br />

3


GREETINGS FROM THE IAH CNC<br />

It is my pleasure to be able to welcome hydrogeologists from across<br />

Canada and beyond to IAH-CNC Waterloo 2015 on behalf the<br />

International Association of Hydrogeologists - Canadian National<br />

Chapter (IAH CNC). This is the first time in many decades that<br />

the IAH CNC held a meeting without other national or international<br />

partner organizations. This represents another step forward<br />

for our national chapter, following on our recent success with hosting<br />

the 39th International Congress. This congress is the result of<br />

a great deal of hard work from our local organizing committee in<br />

Waterloo and I hope that their work inspires other groups across Canada to organize more<br />

IAH events.<br />

This conference also represents a homecoming of sorts for many of us. For the last fifty<br />

years, The University of Waterloo has been a centre for groundwater research and education.<br />

I count myself among the many IAH CNC members who passed through the University<br />

of Waterloo as part of their adventure in hydrogeology. I am excited that the IAH<br />

CNC has the opportunity to return to Waterloo to participate in the Farvolden Day as part<br />

of the Department of Earth and Environmental Sciences 50th anniversary.<br />

Grant Ferguson<br />

President, IAH CNC<br />

4 IAH-CNC 2015 WATERLOO CONFERENCE


GREETINGS FROM THE IAH<br />

Welcome to Waterloo!<br />

I’d like to add my warm welcome to the 2015 Canadian Chapter<br />

Conference of the International Association of Hydrogeologists.<br />

The writer Mark Twain once quipped, “Go to heaven for the good<br />

climate, to hell for the good company.” Being from southern Nevada<br />

where our summertime temperatures often exceed 45 degrees C,<br />

I consider myself a connoisseur of good company. And there is very<br />

good company at this conference. Our good company includes many<br />

world-class and expert hydrogeologists, hydrologists, scientists, engineers,<br />

consultants, agency officials, and scholars lined up to give inspired and insightful<br />

presentations on groundwater.<br />

We live in remarkable times of important challenges. Going to heaven for the good climate<br />

as Twain suggested would be okay if the climate of paradise were not changing. The year<br />

2014 saw the highest temperatures averaged over land and sea since record keeping began<br />

in 1880 (excepting maybe 2015 so far) and the lowest water levels in some of our reservoirs<br />

in drought plagued areas. I can speak of these challenges first hand, coming from an area<br />

with falling water tables, subsiding land surfaces, and declining hopes for a sustainable<br />

groundwater supply. Canada has significant challenges and perhaps opportunities as well<br />

as it injects increasing amounts of wastewaters into deep subsurface systems, which may<br />

irrevocably alter their future use for fresh water resources. Throughout the world groundwater<br />

systems are increasingly stressed, with very real human and ecological consequences.<br />

But beyond a shadow of a drought, there is hope for continuing clean groundwater supply,<br />

and much of that hope lies with you, the dedicated members of IAH. Canada has been an<br />

undisputed world leader in groundwater research, innovation, and hydrophilanthropy, and<br />

this meeting brings together hydrogeologists on the forefront of fundamental advances in<br />

the field. The unparalleled level of original research and novel technological approaches<br />

which will be presented at the IAH-CNC 2015 Waterloo Conference will undoubtedly<br />

assist all those who attend. I’m excited, as I hope you are, to gain new perspectives and<br />

techniques to help improve the world’s human and ecological condition.<br />

Dave Kreamer<br />

North American Vice President<br />

International Association of Hydrogeologists<br />

IAH-CNC 2015 WATERLOO CONFERENCE<br />

5


PLATINUM SPONSORS<br />

MAXXAM - is the Canadian market leader in analytical services and solutions and a member<br />

of the Bureau Veritas Group of companies – a world leader in testing, inspection and<br />

certification services.<br />

Our customers come from a wide variety of industries, ranging from the oil & gas sector,<br />

to the environmental and food industries, to pharmaceutical and DNA. The thread that<br />

unites Maxxam’s lines of business is our relentless drive to create value for all customers and<br />

to help them be successful in their business.<br />

OUR SCIENCE<br />

We are a science company that is passionately committed to delivering good science<br />

through exceptional service. Maxxam’s scientists are leaders in the development of analytical<br />

methods and services to address the challenges of new and emerging compounds<br />

of concern.<br />

Our commitment to “Success through Science” is supported by three core initiatives:<br />

1. Contribute to the state of knowledge in our industries through continuous<br />

Research and Development efforts<br />

2. Provide advanced technical support to our customers through scientific<br />

and regulatory expertise<br />

3. Enhance the scientific knowledge of our customers and staff by offering<br />

training and education<br />

OUR PEOPLE<br />

Maxxam has one of the most stable, experienced teams in the industry and our success is<br />

built on the countless contributions of our employees.<br />

We support critical decisions made by our customers through the application of rigorous<br />

science and the knowledge and expertise of our over 2,500 employees.<br />

6 IAH-CNC 2015 WATERLOO CONFERENCE


BGC - is an applied earth sciences and engineering consulting services company. It is a Canadian<br />

corporation registered in 1990 and 100% owned by its staff. The company was originally<br />

founded by Drs. Iain Bruce, P.Eng., P.Geo., and Wayne Savigny, P.Eng., P.Geo., both of<br />

whom believed that engineering geology principles could be better integrated into geotechnical<br />

engineering assessments. Currently, BGC has approximately 280 staff in nine offices, at the<br />

following locations; Vancouver and Kamloops, BC; Edmonton and Calgary, AB; Toronto, ON;<br />

Fredericton, NB; Halifax, NS; Golden (CO), USA; and Santiago, Chile.<br />

BGC provides specialist services in applied earth sciences with emphasis on the following disciplines:<br />

• Geotechnical engineering<br />

• Geoenvironmental engineering,<br />

(soil and rock mechanics)<br />

contaminated site management and<br />

• Permafrost and cold regions engineering remediation design and management<br />

• Terrain analysis, geohazard assessment • Mine closure planning, design and<br />

and engineering geology<br />

construction monitoring<br />

• Hydrogeology, hydrology and surface • Engineering risk assessment.<br />

water assessments<br />

BGC offers consulting services to private and publicly-traded companies and government<br />

agencies, as well as sub-consulting services to prime consultants, in the following industries:<br />

• Mining<br />

• Water resources<br />

• Oil sands<br />

• Waste management<br />

• Pipelines<br />

• Transportation (road and rail)<br />

• Forestry<br />

• Energy / Hydroelectric<br />

power<br />

BGC’s assignments vary from scoping and pre-feasibility level studies to detailed design, routing<br />

evaluations, construction inspection, contract management, and independent third-party<br />

review. BGC has also coordinated environmental impact statements, and prepared containment<br />

and control reports for regulatory authorities.<br />

BGC is first and foremost a specialist in applied earth sciences and numerous staff have both<br />

professional engineering and geology designations. BGC employs numerous geoscientists,<br />

geomorphologists and hydrologists to complement our engineering skill sets. As a result of<br />

our familiarity with geology and its implications for engineered structures, BGC has a sincere<br />

appreciation of the drivers of success (and failure) within mining projects, especially for mine<br />

design and scoping to feasibility studies.<br />

BGC is an employee-owned company with a flat management structure. All of BGC works<br />

together as one team, with no profit centers or technical divisions. This ‘One Team’ approach<br />

gives every client access to all of BGC’s resources, and allows us to assemble the best team of<br />

professional and support staff for each and every project, regardless of the project location. We<br />

are of sufficient size to offer a full range of services, while maintaining one-to-one contact between<br />

our senior consultants and the client.<br />

IAH-CNC 2015 WATERLOO CONFERENCE<br />

7


GOLD SPONSOR<br />

GHD - is a leading international professional services company operating in<br />

the global markets of water, energy and resources, environment, property and<br />

buildings, and transportation. We provide engineering, environmental and<br />

construction services to private and public sector clients.<br />

Established in 1928, GHD operates across five continents – Asia, Australia,<br />

Europe, North and South America – with 8500 people. Our employee-owned business is driven<br />

by a client-service led culture; we connect the knowledge, skill and experience of our people with<br />

innovative practices, technical capabilities and robust systems to create lasting community benefits.<br />

In July 2014, GHD merged with Conestoga-Rovers & Associates (CRA), bolstering our<br />

combined North America presence to more than 4000 employees (900+ in Ontario). Most<br />

important to us is our shared culture and values of teamwork, respect and integrity. We share<br />

an unrelenting commitment to maintaining an industry leadership position in safety and client<br />

service. For more information, visit www.ghd.com<br />

SILVER SPONSORS<br />

AGAT - AGAT Laboratories is a highly specialized Canadian-based<br />

company that provides full-service laboratory solutions to the Environmental,<br />

Agri-Food, Life Sciences, Energy, Mining, Industrial and<br />

Transportation sectors. AGAT Laboratories is proud to set the standard for the laboratory<br />

industry, with world-class facilities and state-of–the-art instrumentation ensuring validity<br />

and accuracy of methodologies through our extensive quality assurance and quality control<br />

programs. Our qualified personnel adhere to AGAT Laboratories’ mission statement, delivering<br />

“Service Beyond Analysis”.<br />

GOLDER - As a global, employee-owned organization, Golder Associates<br />

is driven by our purpose to engineer earth’s development<br />

while preserving earth’s integrity. We help our clients find sustainable<br />

solutions by providing a range of independent consulting, design and<br />

construction services in our specialist areas of earth, environment and energy. Our global<br />

network of physical and contaminant hydrogeologists, geochemists, numerical modellers,<br />

environmental scientists and engineers has been solving groundwater challenges for over 40<br />

years. More information at golder.com.<br />

STANTEC - The Stantec community unites more than 15,000 employees<br />

working in over 250 locations. We collaborate across disciplines and<br />

industries to bring buildings, energy and resource, and infrastructure<br />

projects to life. Our work—professional consulting in planning, engineering, architecture, interior<br />

design, landscape architecture, surveying, environmental sciences, project management, and<br />

project economics—begins at the intersection of community, creativity, and client relationships.<br />

8 IAH-CNC 2015 WATERLOO CONFERENCE


BRONZE SPONSORS<br />

KEYNOTE SPONSOR<br />

LANYARD SPONSOR<br />

USB SPONSOR<br />

DELEGATE BAG SPONSOR<br />

IAH BANQUET SPONSOR<br />

SOCIAL NIGHT SPONSOR<br />

POSTER RECEPTION SPONSOR<br />

LUNCH SPONSOR<br />

IAH-CNC 2015 WATERLOO CONFERENCE<br />

9


EXHIBITORS<br />

AQUANTY INC. - a hydrological science and research spin-off<br />

company from the University of Waterloo, was founded in 2012<br />

by the key developers of HydroGeoSphere and provides cutting<br />

edge hydrogeological computer modelling software and services.<br />

AQUATECH DEWATERING COMPANY - has established<br />

itself as a leader in the dewatering and pumping industry.<br />

Built on the mandate to form a true and comprehensive provider<br />

of quality and environmentally conscious dewatering<br />

and pumping services in Ontario, Aquatech strives to meet<br />

the changing needs of the industry every day.<br />

AQUATIC LIFE - is a Canadian company based in Pinawa,<br />

Manitoba. Aquatic Life Ltd supports and services Canada, representing<br />

the highest quality suppliers of environmental monitoring<br />

instrumentation. We are committed to the development<br />

and design of remote real time water quality monitoring systems.<br />

DHI - is a research, development and consultancy organization dedicated<br />

to solving the world’s toughest challenges in water environments.<br />

For the past 30 years DHI has been making our research<br />

and expertise available via a comprehensive suite of water modelling<br />

software products including MIKE SHE and FEFLOW.<br />

EARTHFX - is a leading provider of advanced software and<br />

consulting services for integrated surface water/groundwater<br />

modelling, environmental data management, geologic and geophysical<br />

data analysis.<br />

HWB - is a registered Canadian charity that builds local capacity<br />

in emerging regions to provide safe, sustainable groundwater<br />

supplies by strengthening the role of hydrogeology within the<br />

water supply and sanitation sector.<br />

IAH-CNC - International Association of Hydrogeologists is a<br />

scientific and educational organization which exists to promote<br />

the study and knowledge of hydrogeological science and its<br />

application for common good throughout the world.<br />

ISOTOPE TRACER TECHNOLOGIES INC. - (IT 2 ) is a stateof-the-art<br />

facility that offers a large variety of isotopic analyses<br />

on different materials. IT 2 offers excellent services to government<br />

agencies and consulting companies as well as research institutions<br />

with high quality data and fast turn-around time (TAT).<br />

10 IAH-CNC 2015 WATERLOO CONFERENCE


NGWA - is the leading worldwide advocate for professionals<br />

teaming to provide, protect, manage, and remediate groundwater,<br />

and delivers a range of resources contributing to member<br />

success through relationships, leading edge and emerging practices,<br />

and new ideas and solutions.<br />

ONTARIO GEOLOGICAL SURVEY - carries out field-based<br />

investigations to understand geological processes and map earth<br />

resources, such as groundwater. The OGS is the steward of Ontario’s<br />

public geoscience data and information, providing free<br />

access.<br />

RWDI’S ENVIRONMENTAL GROUP - has developed a strong<br />

reputation with clients in the provision of environmental services.<br />

Our Geoscience experts focus on water resources assessments,<br />

contaminant hydrogeology, and waste management for a<br />

wide array of market sectors.<br />

SiREM - was founded in 2001 to provide high quality products<br />

and services to the environmental remediation industry. SiREM<br />

is widely recognized as a leader in bioaugmentation and benchscale<br />

treatability testing for a wide range of contaminants and<br />

remediation technologies.<br />

SkyTEM - a Danish helicopter-borne geophysical system, is<br />

employed globally to map aquifers. SkyTEM data, from the<br />

near surface to depths of 500 m, are used to create detailed 3D<br />

geological representations and reliable hydrogeological models.<br />

SOLINST - In business for over 35 years, Solinst is dedicated to<br />

providing clients with high quality groundwater and surface water<br />

monitoring instrumentation, including Levelogger water level<br />

dataloggers, water level meters, groundwater samplers, and multilevel<br />

monitoring systems.<br />

UWEILAB - is a world class facility that develops and applies<br />

isotope technology to the environment using state of the art<br />

mass spectrometers specializing in environmental isotopes including<br />

H/C/N/O/S/Cl/Br/Sr.<br />

WATERLOO HYDROGEOLOGIC AND VAN ESSEN - provide<br />

the highly reliable and cost-effective tools for groundwater and<br />

environmental projects from data acquisition to data management<br />

and analysis.<br />

IAH-CNC 2015 WATERLOO CONFERENCE<br />

11


HOTEL FLOOR PLANS<br />

12 IAH-CNC 2015 WATERLOO CONFERENCE


The Viennese Ballroom<br />

TO UPPER LOBBY<br />

(REGISTRATION)<br />

The Regent Room<br />

CONFERENCE LUNCHEONS &<br />

THURSDAY POSTER SESSION<br />

TRADE SHOW EXHIBITION, RECEPTIONS<br />

& WEDNESDAY/THURSDAY BREAKS<br />

IAH-CNC 2015 WATERLOO CONFERENCE<br />

13


SOCIAL PROGRAM<br />

In addition to the comprehensive technical program, IAH-CNC 2015 Waterloo will provide<br />

numerous opportunities for delegates to meet, mingle and get to know their professional<br />

colleagues in a relaxed setting, outside of the technical and business streams. Partners<br />

and guests are welcome at all of these events – extra tickets are available online or at<br />

the registration desk.<br />

The program of IAH-CNC 2015 Waterloo social events includes the following:<br />

Tuesday, October 27<br />

Opening “Icebreaker” and Exhibitor Reception<br />

Regent Room: 17:00 – 19:30<br />

Come and meet up with old acquaintances, or introduce yourself to new colleagues from<br />

across the country, as we gather for complimentary beverages and hors d’oeuvres in the<br />

Trade Show Hall.<br />

Wednesday, October 28<br />

IAH-CNC 2015 Waterloo Conference Banquet<br />

Regent Room (Cocktail Reception) 18:15 – 18:45<br />

Viennese Ballroom (Dinner): 19:00 – 21:30<br />

At the end of our first full conference day, come join us for a banquet<br />

dinner and continue to socialize with new and old friends. Our featured<br />

after-dinner speaker will be Kevin Callan who will regal us with stories<br />

on canoeing and the outdoors within Ontario’s Grand River Watershed.<br />

You may be familiar with Kevin as he is the author of “The Happy Camper” and is a regular<br />

guest speaker on radio and television.<br />

Thursday, October 29<br />

Oktoberfest Fun Night<br />

Concordia Club: 19:00 – 22:00<br />

(Shuttle buses from the Waterloo Inn begin at 18:30)<br />

Kitchener, Ontario is well known for its annual Oktoberfest,<br />

the largest Oktoberfest outside of Munich, and<br />

includes multiple festhalles throughout the city offering<br />

traditional Bavarian food, drink, music and dancing. In<br />

keeping with this theme, IAH-CNC 2015 Waterloo has organized an Oktoberfest-inspired<br />

evening at the Concordia Club. Come and enjoy this social highlight with friends<br />

and colleagues and experience a taste of Oktoberfest – with your souvenir Oktoberfest hat,<br />

traditional food and local beverages, everyone is sure to have a good time. Transportation<br />

will be provided between the Waterloo Inn and the Concordia Club for your safe Oktoberfest<br />

enjoyment.<br />

Be sure to join us at these popular IAH-CNC 2015 Waterloo social events!<br />

14 IAH-CNC 2015 WATERLOO CONFERENCE


WEDNESDAY PLENARY SESSION<br />

NGWA Darcy Lecture<br />

Evaluating the Competitive Use of the<br />

Subsurface: The Influence of Energy Storage<br />

and Production in Groundwater<br />

Rainer H. Helmig, Ph.D.<br />

Department of Hydromechanics and Modelling of Hydrosystems<br />

- Faculty of Civil and Environmental Engineering,<br />

University of Stuttgart, Germany<br />

Gain insight on how advanced numerical models may be used to analyze<br />

and predict the mutual influence of subsurface projects and their impact<br />

on groundwater reservoirs, and the increasing need to do so, during this<br />

presentation.<br />

The subsurface is being increasingly utilized both as a resource and as an<br />

energy and waste repository. With increasing exploitation, resource conflicts<br />

are becoming increasingly common and complex, such as thermal<br />

energy storage and the effects surrounding hydraulic fracturing in both<br />

geothermal and shale gas production.<br />

During this lecture you will learn about:<br />

• Possible utilization conflicts in subsurface systems and how the groundwater<br />

is affected<br />

• Fundamental properties and functions of a compositional multiphase system<br />

in a porous medium; basic multiscale and multiphysics concepts will<br />

be introduced and conser vation laws formulated<br />

• Large-scale simulation that shows the general applicability of the modeling<br />

concepts of such complicated natural systems, especially the impact<br />

on the groundwater of simultaneously using geothermal energy and storing<br />

chemical and thermal energy, and how such real large-scale systems<br />

provide a good environment for balancing the efficiency potential and<br />

possible weaknesses of the approaches discussed.<br />

IAH-CNC 2015 WATERLOO CONFERENCE<br />

15


HENRY DARCY<br />

DISTINGUISHED LECTURE SERIES IN GROUNDWATER SCIENCE<br />

Thank you for attending today’s Darcy Lecture in Groundwater Science presentation at<br />

________________________________ on __________________ made possible by the<br />

National Ground Water Research and Educational Foundation. To aid us in growing this<br />

series, please answer the following questions after the lecture. If you forget to give it to<br />

the lecture host, please fax your completed response to Rachel Geddes at 614.898.7786,<br />

or e-mail it to her at rgeddes@ngwa.org.<br />

I am (check one)<br />

❏ An undergraduate student<br />

❏ A graduate student (full-time)<br />

❏ A faculty and/or research scientist<br />

❏ Employed by a hydrogeologic or<br />

engineering consulting firm<br />

❏ Employed by a government agency<br />

other than an educational institution<br />

❏ Employed by a commercial business<br />

other than a consulting firm<br />

❏ Employed in some other way<br />

(please specify)<br />

_________________________________<br />

_________________________________<br />

I am<br />

❏ 20 to 25 years old<br />

❏ 26 to 30<br />

❏ 31 to 35<br />

❏ 36 to 45<br />

❏ 46 to 55<br />

❏ 56 or older<br />

I have been in the groundwater industry<br />

❏ Attending school ❏ 6 to 10 years<br />

❏ Less than 5 years ❏ 10 to 20 years<br />

❏ More than 20 years<br />

The lecture was useful in my future<br />

career preparation.<br />

❏ Agree ❏ Disagree ❏ No opinion<br />

The lecture was useful to my personal<br />

specific groundwater interests, research,<br />

or specialization.<br />

❏ Agree ❏ Disagree ❏ No opinion<br />

The lecture has inspired me to further<br />

my groundwater knowledge in general.<br />

❏ Agree ❏ Disagree ❏ No opinion<br />

The lecture has inspired me to further<br />

my groundwater knowledge relating to<br />

the lecture topic.<br />

❏ Agree ❏ Disagree ❏ No opinion<br />

I will recommend to a colleague that<br />

they attend the lecture.<br />

❏ Agree ❏ Disagree ❏ No opinion<br />

I would attend another Darcy Lecture<br />

presentation on a different topic.<br />

❏ Agree ❏ Disagree ❏ No opinion<br />

What one concept in the lecturer’s<br />

presentation did you find most valuable<br />

or intriguing?<br />

___________________________________<br />

___________________________________<br />

___________________________________<br />

___________________________________<br />

Do you have a suggestion for a future<br />

Darcy Lecture topic or person to be the<br />

Darcy Lecturer?<br />

___________________________________<br />

___________________________________<br />

___________________________________<br />

May we contact you? If so, please provide the following information.<br />

Name __________________________________________________________________<br />

Telephone ___________________________ E-mail _____________________________<br />

16 IAH-CNC 2015 WATERLOO CONFERENCE


THURSDAY PLENARY SESSION<br />

40 Years of Contaminant Hydrogeology<br />

John A. Cherry<br />

Distinguished Emeritus Professor, University of Waterloo,<br />

Waterloo, Ontario, Canada<br />

Forty years have passed since the earth-science sub-discipline<br />

of ‘contaminant hydrogeology’ began to use this designation.<br />

The term “Contaminant hydrogeology” was introduced into the<br />

literature in an overview article published in Geoscience Canada 1 .<br />

Part 2 of this article on the relevant chemical processes was not<br />

completed until much later 2 .<br />

This presentation examines what was known and not known when<br />

this term was introduced and how our thinking has evolved with<br />

some confusion and muddled thinking along the way, the path to<br />

understanding of dispersion being a good example. It also examines the<br />

current state of understanding; some aspects of hydrogeologic science<br />

have matured while others are still in early stages. The initial article<br />

focused on the physical processes in contaminant transport and fate was<br />

based on the sparse groundwater contamination literature up to that time,<br />

which concerned field studies of radionuclides from experimental reactor<br />

accidents in the 1950’s, leachate from municipal landfills, sewage from<br />

septic systems, petroleum hydrocarbons and the early problems caused by<br />

the mobile versions of detergents.<br />

Groundwater contamination by chlorinated solvents and the importance<br />

of DNAPLS for groundwater contamination was unknown until the early<br />

1980’s. The concept of contaminant plumes in groundwater was established<br />

by the mid-1960’s but the belief was widely held until the early 1980’s that<br />

the substantial groundwater contamination would remain minimal due to<br />

the robust assimilation capacity of the subsurface environment. This would<br />

have been correct if it were not for the widespread releases of many types of<br />

halogenated organic chemicals such as chlorinated solvents. These began<br />

entering groundwater in the 1950’s only to be discovered decades later. The<br />

warning signs of the potential for mobile recalcitrant organic chemicals<br />

of common use to cause substantial groundwater contamination occurred<br />

in the early 1960’s when detergents from septic systems were commonly<br />

found in shallow domestic wells in suburbs but this problem subsided with<br />

a change in the detergent formulation in 1963. The larger significance of<br />

this evidence concerning anthropogenic organic chemical in groundwater<br />

went unrecognized.<br />

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Since the first big surprise on finding the common occurrence of<br />

chlorinated in groundwater in the 1980’s, a never ending series of<br />

‘surprises’ has unfolded concerning the new types of contaminants<br />

being found such as MTBE, perchlorate, 1,4 dioxane and most<br />

recently pharmaceuticals, food additives and flame retardants and<br />

the widespread occurrence of nitrate in many aquifers. In Canada the<br />

occurrence of pristine groundwater in aquifers used for domestic and<br />

municipal water supply is now rare.<br />

All of this does not mean that groundwater is a hazardous source of<br />

drinking water relative to the alternatives, but it does demonstrate that<br />

hydrogeologic science has only been used reactively and not proactively<br />

in the broader realm of water management and land use regulations<br />

and planning as a source of knowledge and expertise. This may be best<br />

for the employment of hydrogeologists but not for the well-being of<br />

the environment and society-at-large.<br />

1 <br />

Cherry, J.A., Gillham, R.W. and Pickens, J.F., 1975, Contaminant Hydrogeology:<br />

Part 1: Physical Processes, Geoscience Canada 2(2): 76-84.<br />

2 <br />

Cherry, J.A., Gillham, R.W., and Barker, J.F., 1984, Contaminants in<br />

Groundwater: Chemical Processes. In: Groundwater Contamination, Studies in<br />

Geophysics, US National Research Council, National Academy Press, Washington<br />

DC, pp. 46-64.<br />

18 IAH-CNC 2015 WATERLOO CONFERENCE


FRIDAY PLENARY SESSIONS<br />

The Future of Isotope Hydrogeology<br />

Ian D. Clark, Department of Earth Sciences, University of Ottawa<br />

In 1971, Peter Fritz carried the torch of isotope hydrology from<br />

the crucible of Professor Gonfiantini’s lab in Pisa to Waterloo via<br />

the University of Alberta. Those early days of hard-won isotope<br />

measurements on a fully manual dual inlet VG602 generated<br />

fundamental insights into the use of these tracers in hydrogeology.<br />

Half a century of technological developments has produced<br />

new instruments that provide orders of magnitude more data at<br />

unprecedented temporal and spatial resolution.<br />

What have we done with these new capabilities and what new questions<br />

are we addressing? Have our innovations and applications kept pace?<br />

We’ve seen advances on many fronts from questions of origin, age and<br />

renewability of groundwater resources to tracing contaminant transport<br />

and remediation. Our challenge in the coming decades will be to more fully<br />

engage industry and government in the routine use of isotopes to address<br />

a range of issues spawned by our improving stewardship of water and the<br />

environment.<br />

Insightful Moments in Hydrogeology –<br />

Hydrogeologists without Borders and<br />

the ‘GW2.0 Initiative’<br />

This session celebrates the hydrogeology textbook<br />

initiative GW2.0 of Hydrogeologists without<br />

Borders (HWB) to provide an updated version of<br />

the 1979 Freeze and Cherry text Groundwater as a<br />

training tool that will be available worldwide and in<br />

multiple languages.<br />

HWB is a Canadian charity focused on linking hydrogeology to the water,<br />

sanitation and hygiene (WASH) sector. Although much of the regions<br />

of critical need worldwide are increasingly groundwater dependent, and<br />

a significant part of the international aid sector drills water wells, projects<br />

are often lacking in their hydrogeological component especially sustainable<br />

well construction. Major efforts to provide improved water supply in<br />

developing countries are thwarted because of the inability to find and<br />

develop groundwater resources - often due to the lack of hydrogeological<br />

expertise.<br />

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In this final plenary session, some of our favourite hydrogeology teachers<br />

will share their most memorable ‘moments of insight’ by means of short<br />

talks that may address:<br />

• an ‘aha!’ moment in teaching or research;<br />

• a concept that is particularly difficult that they have mastered the<br />

teaching of;<br />

• a concept or fact that they think every hydrogeology practitioner<br />

should understand;<br />

• bringing to light a little-known, but important manuscript; or<br />

• posing a challenging research question to the ‘next generation’.<br />

Our speakers will include:<br />

• M. Cathryn Ryan, Geoscience, University of Calgary<br />

• Richard E. Jackson, Geofirma Engineering Ltd<br />

• William M. Alley, National Ground Water Association,<br />

• Robert W. Gillham, Department of Earth and Environmental Sciences,<br />

University of Waterloo<br />

• James Barker, Department of Earth & Environmental Sciences,<br />

University of Waterloo<br />

• Emil Frind, Department of Earth and Environmental Sciences, University<br />

of Waterloo<br />

• Garth van der Kamp, Water Science and Technology, Environment<br />

Canada<br />

20 IAH-CNC 2015 WATERLOO CONFERENCE


CONFERENCE PROGRAM & TIMETABLE<br />

All events will take place at the Waterloo Inn unless otherwise noted<br />

Tuesday, October 27, 2015<br />

AM Short Courses: 8:30 - 12:00<br />

• Advanced Construction Dewatering (Rosedale)<br />

• Aquitard Characterization and Monitoring: From Source Water Protection to<br />

Remediation (Bloomingdale)<br />

Technical Tour: 10:00 - 16:00 (Meet in the Waterloo Inn lobby at 9:45)<br />

• The Waterloo Moraine and Waterloo Region<br />

PM Short Courses: 13:30 - 17:00<br />

• Contaminated Groundwater: Innovative Remediation Techniques and Case<br />

Studies (Rosedale)<br />

• Integrated Watershed Hydrology Modelling – An Introduction for Hydrogeologists<br />

(St. Jacobs)<br />

• Contaminant Behaviour in Fractured Sedimentary Rock: New Techniques for<br />

Improved Site Conceptual Models (Bloomingdale)<br />

Delegate Registration: 12:00 - 19:30 (Upper Lobby – Viennese Ballroom pre-function)<br />

Opening Reception in the Trade Exhibition Hall: 17:00 - 19:30 (Regent Room)<br />

Wednesday, October 28, 2015<br />

Delegate Registration: 7:00 - 19:00 (Upper Lobby – Viennese Ballroom Pre-function)<br />

Wednesday Speakers’ Breakfast: 7:15 - 7:45 (Lower Regent)<br />

Opening Plenary Session: 8:00 - 9:30 (Viennese Ballroom)<br />

• Opening and Welcoming Remarks<br />

• NGWA Darcy Lecture, Dr. Rainer Helmig - Evaluating the Competitive Use of the<br />

Subsurface: The Influence of Energy Storage and Production in Groundwater<br />

Trade Exhibition: 9:30 - 18:45 (Regent)<br />

Wednesday AM Technical Sessions: 10:10 - 11:50<br />

• Groundwater/Surface Water Interaction 1 (Strauss)<br />

• Road Salt Impacts on Groundwater (Wagner)<br />

• Innovation in the Remediation of Contaminated Sites 1 (Schubert)<br />

• Groundwater Aspects of Deep Geological Repositories (Heritage)<br />

Conference Luncheon: 11:50 - 13:00 (Regent Room)<br />

Wednesday PM1 Technical Sessions: 13:00 - 14:40<br />

• Groundwater/Surface Water Interaction 2 (Strauss)<br />

• Regional Groundwater Systems 1 (Wagner)<br />

• Innovation in the Remediation of Contaminated Sites 2 (Schubert)<br />

• Surficial Geology of Southern Ontario (Heritage)<br />

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Wednesday PM2 Technical Sessions: 15:20 - 17:00<br />

• Agricultural Impacts on Groundwater 1 (Strauss)<br />

• Regional Groundwater Systems 2 (Wagner)<br />

• Flow and Transport in Fractured Rock (Schubert)<br />

• Vadose Zone Hydrogeology (Heritage)<br />

IAH-CNC Annual General Meeting: 17:15 - 18:15 (Heritage)<br />

IAH-CNC 2015 Waterloo Banquet: 18:30 - 21:30<br />

• Cocktail Reception: 18:30 - 19:00 (Trade Show – Regent Room)<br />

• Dinner and Presentations: 19:00 - 21:30 (Viennese Ballroom)<br />

Thursday, October 29, 2015<br />

Delegate Registration: 7:00 - 19:00 (Upper Lobby – Viennese Ballroom Pre-function)<br />

Thursday Speakers’ Breakfast: 7:45 - 8:15 (Lower Regent)<br />

Thursday Plenary Session: 8:30 - 9:40 (Viennese Ballroom)<br />

• Dr. John Cherry - 40 Years of Contaminant Hydrogeology<br />

Trade Exhibition: 9:40 - 18:45 (Regent Room)<br />

Thursday AM Technical Sessions: 10:10 - 11:50<br />

• Groundwater/Surface Water Interaction 3 (Strauss)<br />

• Sustainability of Groundwater Resources 1 (Wagner)<br />

• Groundwater Issues from Oil and Gas Exploration & Production 1 (Schubert)<br />

• Advanced Techniques for Site Characterization (Heritage)<br />

Conference Luncheon: 11:50 - 13:00 (Regent Room)<br />

Thursday PM1 Technical Sessions: 13:00 - 14:40<br />

• Groundwater/Surface Water Interaction 4 (Strauss)<br />

• Sustainability of Groundwater Resources 2 (Wagner)<br />

• Innovation in the Remediation of Contaminated Sites 3 (Schubert)<br />

• Groundwater Issues from Mining & Aggregates (Heritage)<br />

• Workshop on Groundwater Policy 1 (Bloomingdale)<br />

Thursday PM2 Technical Sessions: 15:00 - 16:40<br />

• Groundwater Issues from Oil and Gas Exploration & Production 2 (Strauss)<br />

• Regional Groundwater Systems 3 (Wagner)<br />

• Agricultural Impacts on Groundwater 2 (Schubert)<br />

• Workshop on Groundwater Policy 2 (Bloomingdale)<br />

IAH-CNC 2015 Waterloo Poster Session: 16:40 - 18:30 (Regent)<br />

Oktoberfest Night at the Concordia Club (429 Ottawa St S, Kitchener): 18:30 - 22:00<br />

(Shuttle bus service from the Waterloo Inn begins at 18:30)<br />

22 IAH-CNC 2015 WATERLOO CONFERENCE


Friday, October 30, 2015<br />

Delegate Registration: 7:00 - 13:00 (Upper Lobby – Viennese Ballroom Pre-function)<br />

Conference Breakfast: 7:15 - 8:00 (Viennese Ballroom)<br />

Friday Plenary Session: 8:00 - 9:05 (Viennese Ballroom)<br />

• Dr Ian Clark - The Future of Isotope Hydrogeology<br />

Special Plenary Session - Insightful Moments in Hydrogeology: 9:05 - 11:45<br />

(Viennese Ballroom)<br />

Closing Ceremonies 11:45 - 12:00 (Viennese Ballroom)<br />

Shuttle Service to Farvolden Days at University of Waterloo 12:30 - 13:30 (from outside<br />

hotel lobby)<br />

IAH-CNC 2015 WATERLOO CONFERENCE<br />

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WEDNESDAY PROGRAM AT A GLANCE<br />

Wednesday, October 28, 2015<br />

8:00 - 8:30<br />

Opening Ceremony<br />

8:30 - 9:30<br />

Opening Plenary: NGWA Lecturer, Dr. Rainer Helmig - Evaluating the Competitive Use of the Subsurface:<br />

The Influence of Energy Storage and Production in Groundwater<br />

9:30 - 10:10<br />

AM Break - Trade Show Hall (Regent)<br />

Strauss Wagner Schubert Heritage<br />

10:10 - 11:50<br />

Groundwater/Surface Water<br />

Interaction 1<br />

Road Salt Impacts on<br />

Groundwater<br />

Innovation in the Remediation<br />

of Contaminated Sites 1<br />

Groundwater Aspects of Deep<br />

Geological Repositories<br />

11:50 - 13:00<br />

Conference Luncheon - Regent Room<br />

Strauss Wagner Schubert Heritage<br />

13:00 - 14:40<br />

Groundwater/Surface Water<br />

Interaction 2<br />

Regional Groundwater<br />

Systems 1<br />

Innovation in the Remediation<br />

of Contaminated Sites 2<br />

Surficial Geology of Southern<br />

Ontario<br />

14:40 - 15:20<br />

PM Break - Trade Show Hall (Regent)<br />

Strauss Wagner Schubert Heritage<br />

15:20 - 17:00<br />

Agricultural Impacts of<br />

Groundwater 1<br />

Regional Groundwater<br />

Systems 2<br />

Flow and Transport in<br />

Fractured Rock<br />

Vadose Zone Hydrogeology<br />

17:15 - 18:15<br />

IAH-CNC Annual General Meeting - Heritage Room<br />

18:30 - 19:00<br />

Banquet Reception - Trade Show Hall (Regent)<br />

19:00 - 22:00 IAH-CNC 2015 Waterloo Banquet - Viennese Ballroom<br />

24 IAH-CNC 2015 WATERLOO CONFERENCE


WEDNESDAY PROGRAM AT A GLANCE<br />

Time/Heure<br />

10:10 - 10:15<br />

10:15 - 10:34<br />

10:34 - 10:53<br />

10:53 - 11:12<br />

11:12 - 11:31<br />

11:31 - 11:50<br />

Wednesday, October 28, 2015<br />

Strauss Wagner Schubert Heritage<br />

Groundwater/Surface Water<br />

Interaction 1<br />

pp 34-37<br />

Road Salt Impacts on<br />

Groundwater<br />

pp 38-41<br />

Innovation in the Remediation<br />

of Contaminated Sites 1<br />

pp 42-45<br />

Groundwater Aspects of Deep<br />

Geological Repositories<br />

pp 46-50<br />

Introduction and<br />

poster program overview<br />

201 - A Physically-Based Modelling<br />

Approach to Assess the Impact of<br />

Climate Change on Surface and<br />

Groundwater Resources within the<br />

Grand River Watershed<br />

224 - Strategies for Integrated Model<br />

Calibration<br />

Introduction and<br />

poster program overview<br />

211 - Recent field data confirm previous<br />

predictions that Toronto’s groundwater<br />

faces a serious decline in water quality<br />

due to road salt<br />

181 - Halton Region's Salt Management<br />

Strategy<br />

Introduction and<br />

poster program overview<br />

132 - Electrokinetically-Enhanced<br />

Remediation: An Innovative Solution to<br />

Vexing Challenges for Source Area<br />

Remediation<br />

190 - Integrating Risk Management into<br />

Redevelopment of an Urban Brownfield<br />

Site<br />

Introduction and<br />

poster program overview<br />

228 - Deep Geologic Repositories:<br />

Developing a Geoscientific Basis for<br />

Long-Term Safety<br />

154 - Hydrogeochemical<br />

Characterization of Porewater in Low-<br />

Permeability Sediments<br />

227 - Deep-Seated Aquiclude<br />

Groundwater Systems: Advances in In<br />

Situ Hydraulic Testing<br />

199 - Importance of Incorporating<br />

Peatlands and Winter Processes into<br />

Integrated Surface-subsurface Models of<br />

the Athabasca River Basin<br />

244 - Quantifying the impact of road salt<br />

management practices on water quality<br />

in public supply wells within the Region<br />

of Waterloo<br />

214 - Treatment of manufactured gas<br />

plant residuals using alkaline activated<br />

persulfate: A pilot-scale trial<br />

170 - Pore Fluid Pressures in the<br />

Ordovician Sediments at the Bruce site<br />

near Kincardine, Ontario: Potential<br />

Causes and Analysis<br />

225 - Integrated surface<br />

water/groundwater modelling to simulate<br />

drought and climate change impacts from<br />

the reach to the watershed scale<br />

122 - Assessment of Road Salt Impacts<br />

to Four Priority Well Fields in the Region<br />

of Waterloo<br />

116 - The Effect of Injection Methods on<br />

the Distribution of Remedial Compounds<br />

350 - Diffusion research in support of the<br />

Canadian nuclear waste management<br />

program<br />

272 - Balancing Near-Surface Water 121 - Salt Assessment of a low Demand,<br />

Rural Well Field<br />

249 - Enhanced in situ Bioremediation of<br />

Chlorinated Solvents in Canada<br />

273 - Coupled groundwater flow and<br />

reactive transport simulations of the<br />

evolution of groundwater chemistry for a<br />

deep geologic repository in shield rocks<br />

IAH-CNC 2015 WATERLOO CONFERENCE<br />

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WEDNESDAY PROGRAM AT A GLANCE<br />

Time/Heure<br />

13:00 - 13:05<br />

13:05 - 13:24<br />

13:24 - 13:43<br />

13:43 - 14:02<br />

14:02 - 14:21<br />

14:21 - 14:40<br />

Wednesday, October 28, 2015<br />

Strauss Wagner Schubert Heritage<br />

Groundwater/Surface Water<br />

Interaction 2<br />

pp 51-54<br />

Regional Groundwater<br />

Systems 1<br />

pp 54-58<br />

Innovation in the Remediation<br />

of Contaminated Sites 2<br />

pp 59-62<br />

Surficial Geology of Southern<br />

Ontario<br />

pp 63-67<br />

Introduction and<br />

poster program overview<br />

135 - Pressure pulses as an indication of<br />

recharge to a buried esker-aquifer<br />

Eastern Ontario<br />

Introduction and<br />

poster program overview<br />

140 - Groundwater Residence Times in<br />

Chaudière-Appalaches, Québec: Closing<br />

the Loop Between Flow and Regional<br />

Geochemistry<br />

Introduction and<br />

poster program overview<br />

203 - Dissolution of Light Non-Aqueous<br />

Phase Liquid from Smear Zones<br />

Containing Trapped Air<br />

Introduction and<br />

poster program overview<br />

231 - Regional buried bedrock valleys,<br />

infill sediments and stratigraphy in<br />

southern Ontario: a review<br />

247 - Subsurface water flow from<br />

wetlands to the riparian zone induced by<br />

evapotranspiration<br />

189 - Uniform-density, ‘full-matrix’<br />

hydrogeochemical mapping of southern<br />

Ontario<br />

156 - Nature, Nurture and Sustainable<br />

Remediation: Case Study From a Major<br />

Hydrocarbon Release in a Sensitive<br />

Urban Riverine Environment<br />

230 - The pre-Late Wisconsin<br />

stratigraphy of Simcoe County, southern<br />

Ontario<br />

139 - Detecting hyporheic exchange<br />

using electrical resistivity tomography<br />

along a fractured sedimentary bedrock<br />

river: Eramosa River, Guelph, Ontario<br />

207 - A study of flow system dynamics<br />

utilizing a diverse set of isotopic and<br />

geochemical methods; Oak Ridges<br />

Moraine, Ontario<br />

178 - Simulation of Persulfate Oxidation<br />

Coupled with Enhanced Bioremediation<br />

as an Emerging Remediation Strategy for<br />

Petroleum Impacted Sites<br />

288 - Geological and hydrogeological<br />

models of the ‘Yonge Street’ aquifer,<br />

south-central Ontario<br />

246 - A method for utilizing data from<br />

extreme hydrological events to trigger<br />

enhanced monitoring and sampling in<br />

watersheds<br />

185 - Groundwater Resources and Use<br />

in York Region – Lessons Learned from<br />

Source Water Protection<br />

200 - A Comprehensive Environmental<br />

Assessment Tool for Estimating the<br />

Design and Performance of Permeable<br />

Reactive Barriers<br />

177 - Hydrostratigraphy of the Interlobate<br />

Orangeville Moraine, Southwestern<br />

Ontario, Canada<br />

255 - Estimating depression-focussed<br />

recharge in the Prairies using a onedimensional<br />

model<br />

179 - Operational Experiences of<br />

Implementing ASR System in the Region<br />

of Waterloo<br />

305 - In Situ Remediation of Coal Tar by<br />

STAR: Self-Sustaining Propagation<br />

Across Clean Sand Gaps<br />

308 - Origin and Sedimentological<br />

Context of Large Sand and Gravel<br />

Aquifers – Belleville, Trenton and<br />

Brighton Areas<br />

26 IAH-CNC 2015 WATERLOO CONFERENCE


WEDNESDAY PROGRAM AT A GLANCE<br />

Time/Heure<br />

15:20 - 15:25<br />

15:25 - 15:44<br />

15:44 - 16:03<br />

16:03 - 16:22<br />

16:22 - 16:41<br />

16:41 - 17:00<br />

Wednesday, October 28, 2015<br />

Strauss Wagner Schubert Heritage<br />

Agricultural Impacts of<br />

Groundwater 1<br />

pp 68-71<br />

Regional Groundwater<br />

Systems 2<br />

pp 72-76<br />

Flow and Transport in<br />

Fractured Rock<br />

pp 77-80<br />

Vadose Zone Hydrogeology<br />

pp 81-84<br />

Introduction and<br />

poster program overview<br />

155 - Addressing groundwater nitrate<br />

contamination associated with intensive<br />

agricultural production systems: The<br />

Abbotsford-Sumas Aquifer case study<br />

Introduction and<br />

poster program overview<br />

176 - A Continental-Scale Groundwater<br />

Flow Model Calibrated to Groundwater<br />

Age<br />

Introduction and<br />

poster program overview<br />

300 - Hydrogeology and sequence<br />

stratigraphy correlations<br />

Introduction and<br />

poster program overview<br />

307 - Implications of thick vadose zone<br />

infiltration and a falling water table for<br />

recharge estimations beneath an<br />

irrigated field<br />

241 - Predicting the impact of surface<br />

sources on an aquifer: The role of<br />

dispersion<br />

229 - Investigating Deep Basalt<br />

Groundwater Supplies in the Interior<br />

Plateau Region of British Columbia<br />

292 - Parameter Estimation in a Regional<br />

Groundwater Flow Model<br />

258 - Applicability of the chloride mass<br />

balance method for an evaluation of the<br />

depression-focussed recharge in the<br />

Canadian prairies<br />

206 - Trends of nitrate concentrations in<br />

groundwater for variable geological<br />

settings in agricultural watersheds<br />

245 - Regional groundwater flow in the<br />

inter-till and buried-valley aquifers,<br />

southwestern Manitoba<br />

286 - Advances in the Application of<br />

Thermal Logging Techniques<br />

283 - Simulated mechanical compression<br />

of regenerated Sphagnum moss<br />

potentially accelerates the return of<br />

hydrological functionality in restored<br />

bogs<br />

112 - Implementing Source Water<br />

Protection – Developing a Tool to<br />

Support Site-Specific Risk Management<br />

Planning<br />

318 - Glacial retreat effects and transport<br />

in the Milk River Transboundary Aquifer<br />

210 - Palaeo-hydrogeological evolution<br />

of a fractured-rock aquifer<br />

277 - Assessing soil water content &<br />

temperature under conventional tillage &<br />

no-tillage for drought adaptation<br />

188 - Long term assessment of BMPs<br />

impact on nitrate load at the Thornton<br />

Well Field using RZWQM<br />

219 - Current results and outcomes of<br />

the regional groundwater knowledge<br />

acquisition program in Québec<br />

213 - Nano-scale Colloid Particles<br />

Transport in Variable-aperture Sandstone<br />

Rock Fracture<br />

205 - Modelling nitrate concentrations in<br />

the shallow subsurface for variable<br />

hydrogeological settings in agricultural<br />

watersheds<br />

IAH-CNC 2015 WATERLOO CONFERENCE<br />

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THURSDAY PROGRAM AT A GLANCE<br />

8:30 - 9:40<br />

9:40 - 10:10<br />

10:10 - 11:50<br />

11:50 - 13:00<br />

13:00 - 14:40<br />

14:40 - 15:00<br />

15:00 - 16:40<br />

16:40 - 18:30<br />

18:30 - 19:00<br />

19:00 - 22:00<br />

Thursday, October 29, 2015<br />

Thursday Plenary Session: Dr. John Cherry - 40 Years of Contaminant Hydrogeology<br />

AM Break - Trade Show Hall (Regent)<br />

Strauss Wagner Schubert Heritage Bloomingdale<br />

Groundwater/Surface Water<br />

Interaction 3<br />

Sustainability of Groundwater<br />

Resources 1<br />

Groundwater Issues from Oil<br />

and Gas E&P 1<br />

Advanced Techniques for Site<br />

Characterization<br />

Conference Luncheon - Regent Room<br />

Strauss Wagner Schubert Heritage Bloomingdale<br />

Groundwater/Surface Water<br />

Interaction 4<br />

Sustainability of Groundwater<br />

Resources 2<br />

Innovation in the Remediation<br />

of Contaminated Sites 3<br />

Groundwater Issues from<br />

Mining & Aggregates<br />

Workshop on Groundwater<br />

Policy 1<br />

PM Break - Trade Show Hall (Regent)<br />

Strauss Wagner Schubert Heritage Bloomingdale<br />

Groundwater Issues from Oil<br />

and Gas E&P 2<br />

Regional Groundwater<br />

Systems 3<br />

Agricultural Impacts on<br />

Groundwater 2<br />

Workshop on Groundwater<br />

Policy 2<br />

Poster Session - Lower Regent Room and Trade Show Hall<br />

Shuttle Buses Depart<br />

Oktoberfest Fun Night - Concordia Club<br />

28 IAH-CNC 2015 WATERLOO CONFERENCE


THURSDAY PROGRAM AT A GLANCE<br />

Time/Heure<br />

10:10 - 10:15<br />

10:15 - 10:34<br />

10:34 - 10:53<br />

10:53 - 11:12<br />

11:12 - 11:31<br />

11:31 - 11:50<br />

Thursday, October 29, 2015<br />

Strauss Wagner Schubert Heritage<br />

Groundwater/Surface Water<br />

Interaction 3<br />

pp 85-88<br />

Sustainability of<br />

Groundwater Resources 1<br />

pp 89-93<br />

Groundwater Issues from Oil<br />

and Gas E&P 1<br />

pp 94-98<br />

Advanced Techniques for Site<br />

Characterization<br />

pp 98-102<br />

Introduction and<br />

poster program overview<br />

223 - Integrated groundwater/surface<br />

water modelling to assess urban<br />

development and detailed stormwater<br />

design – Babcock Ranch Community<br />

Development, Lee County, Florida<br />

209 - The Influence of storm sewers on<br />

groundwater-surface water interaction<br />

Introduction and<br />

poster program overview<br />

163 - Using numerical groundwater<br />

models as a land use planning tool –<br />

Town of Torbay, NL<br />

234 - Occurrence of viruses, other<br />

pathogens, and organic wastewater<br />

indicators, in seven First Nation<br />

Communities in Southern BC<br />

Introduction and<br />

poster program overview<br />

275 - Lessons learned in a case study of<br />

water well interference by CBM fracking<br />

138 - Local study of the environmental<br />

risk of hydrocarbon exploration<br />

Introduction and<br />

poster program overview<br />

136 - Definition of granular aquifer<br />

heterogeneity for large sites<br />

204 - Comparison of hydraulic tests used<br />

to charaterize aquifer heterogeneity<br />

240 - Enhanced Field Methodologies for<br />

Quantifying the Vulnerability of Public<br />

Supply Wells to Surface Contamination<br />

238 - Groundwater: A sustainable water<br />

source for Waterloo Region<br />

160 - A study of potential links between<br />

the Utica Shale and shallow aquifers in<br />

St-Édouard, southern Quebec, Canada<br />

262 - Real-Time High-Resolution Site<br />

Characterization of the Subsurface Using<br />

and MIP, LIF and HPT<br />

198 - Monitoring of event-based,<br />

depression focussed recharge to a<br />

shallow unconfined aquifer near a<br />

municipal well in the Alder Creek<br />

Subwatershed, SW Ontario<br />

191 - Assessment of the Long-term<br />

Sustainability of Groundwater Aquifers in<br />

the Waterloo Moraine and Surrounding<br />

Areas<br />

182 - Three-dimensional Reactive<br />

Transport Simulations of Methane Gas<br />

and Brine Migration from<br />

Decommissioned Shale Gas Wells into<br />

Shallow Aquifers<br />

266 - Estimating specific storage of an<br />

aquifer using borehole geophysics,<br />

barometric efficiency, and laboratory core<br />

testing<br />

281 - Cumulative impacts of groundwater<br />

extraction on seasonal flows of a<br />

regulated stream, Cowichan River, BC<br />

172 - Region of Waterloo Tier Three<br />

Water Budget - Now What?<br />

319 - Baseline Water Well Testing in Oil<br />

and Gas Development Areas of Alberta<br />

301 - Versatile Monitoring Completions<br />

for Bedrock Vadose Zone VOC Gas<br />

Sampling<br />

IAH-CNC 2015 WATERLOO CONFERENCE<br />

29


THURSDAY PROGRAM AT A GLANCE<br />

Time/Heure<br />

13:00 - 13:05<br />

13:05 - 13:24<br />

13:24 - 13:43<br />

13:43 - 14:02<br />

14:02 - 14:21<br />

14:21 - 14:40<br />

Thursday, October 29, 2015<br />

Strauss Wagner Schubert Heritage Bloomingdale<br />

Groundwater/Surface Water<br />

Interaction 4<br />

pp 103-107<br />

Sustainability of<br />

Groundwater Resources 2<br />

pp 107-111<br />

Innovation in the Remediation<br />

of Contaminated Sites 3<br />

pp 111-115<br />

Groundwater Issues from<br />

Mining & Aggregates<br />

pp 115-119<br />

Workshop on Groundwater<br />

Policy 1<br />

pp 120-123<br />

Introduction and<br />

poster program overview<br />

239 - Artificial sweeteners track septic<br />

system effluent in rural Ontario<br />

groundwater<br />

Introduction and<br />

poster program overview<br />

202 - The global volume, distribution, and<br />

lifespan of young and old groundwater<br />

Introduction and<br />

poster program overview<br />

212 - Full Scale Application of In Situ<br />

STAR to Treat Residual Coal Tar<br />

Introduction and<br />

poster program overview<br />

134 - Protecting water resources with a<br />

groundwater recharge well system at the<br />

Dufferin Aggregates Milton Quarry<br />

Introduction and<br />

poster program overview<br />

144 - Whither Groundwater Policy -<br />

Challenges and Opportunities of a<br />

Paradigm Shift?<br />

217 - Hydrogeological characterization of<br />

a waste site at Chalk River, Ontario<br />

166 - Sustainable Groundwater<br />

Management for Municipal Water Supply<br />

in the Township of Langley, Canada<br />

284 - Two-Dimensional Numerical<br />

Modelling of STAR to Optimize<br />

Smouldering Combustion for NAPL<br />

Remediation<br />

282 - Evaluating mining impacts on<br />

groundwater quality in Lake Poopó basin,<br />

Bolivia using geochemical and isotope<br />

tracers<br />

187 - Assessing the Impacts of<br />

Contaminated Groundwater Discharges<br />

to the Surface Waters of the Canadian<br />

Great Lakes Basin: Science Needs and<br />

Data Gaps<br />

235 - Evaluating the influence of regional<br />

stratigraphic architecture on hydraulic<br />

conductivity variability in Early Silurian<br />

carbonate rock aquifers, Guelph Region,<br />

southern Ontario<br />

164 - Feasibility of liquid phase metal<br />

catalyzed reductive dechlorination of<br />

1,2DCA by sodium borohydride<br />

171 - Evaluating the Effects of Increased<br />

Lithium Brine Extraction from the Salar<br />

de Atacama: Conceptual and Numerical<br />

Groundwater Models<br />

124 - Implementing Source Protection in<br />

York Region<br />

158 - Factors influencing the<br />

accumulation and transport of E. coli<br />

near the shoreline at freshwater beaches<br />

153 - Arkell Spring Grounds Adaptive<br />

Management Program and Operational<br />

Testing Program in Support of Increased<br />

Water Taking<br />

296 - In-Situ Subsurface Remediation of<br />

Tetrachloroethylene (PCE) Using Soil<br />

Mixing Technology with Zero-Valent Iron<br />

(ZVI) and Clay<br />

131 - A Conceptual Model for Pore Water<br />

Release from Coal Waste Rock Piles in<br />

the Elk Valley, British Columbia, Canada<br />

216 - Application of Source Water<br />

Protection Models and Policy<br />

Implementation<br />

149 - Using Sea Water/Groundwater<br />

Interaction for Calibration of Variable-<br />

Density Groundwater Flow Model<br />

294 - The impact of climate change on<br />

the sustainability of municipal water<br />

supplies and groundwater / surface water<br />

interactions<br />

173 - Field trials of subsurface chaotic<br />

advection<br />

110 - Characterisation of physical mass<br />

transport through oil sands fluid fine<br />

tailings in an end pit lake: a multi-tracer<br />

study<br />

183 - Development of a Risk Reduction<br />

Process to address Groundwater Safety<br />

in Northern Canada<br />

30 IAH-CNC 2015 WATERLOO CONFERENCE


THURSDAY PROGRAM AT A GLANCE<br />

Time/Heure<br />

15:00 - 15:05<br />

15:05 - 15:24<br />

15:24 - 15:43<br />

15:43 - 16:02<br />

16:02 - 16:21<br />

16:21 - 16:40<br />

Thursday, October 29, 2015<br />

Strauss Wagner Schubert Bloomingdale<br />

Groundwater Issues from Oil<br />

and Gas E&P 2<br />

pp 124-126<br />

Regional Groundwater<br />

Systems 3<br />

pp 127-131<br />

Agricultural Impacts on<br />

Groundwater 2<br />

pp 132-136<br />

Workshop on Groundwater<br />

Policy 2<br />

pp 136-140<br />

Introduction and<br />

poster program overview<br />

220 - Injection Wells in the Western<br />

Canada Sedimentary Basin<br />

Introduction and<br />

poster program overview<br />

313 - Sequence Stratigraphic and Karstic<br />

controls of Regional Groundwater Flow<br />

Zones - Early Silurian Lockport Group of<br />

Niagara Escarpment, Ontario<br />

Introduction and<br />

poster program overview<br />

221 - Matrix diffusion effects on nitrate<br />

transport and fate in a sedimentary<br />

bedrock aquifer<br />

Introduction and<br />

poster program overview<br />

147 - Groundwater and Aboriginal<br />

People: Should the Winters Doctrine<br />

apply in Canada, and if so, what would it<br />

look like?<br />

267 - Assessing water quality of shallow<br />

groundwater near a tailings pond in the<br />

Athabasca oil sands region<br />

180 - The Use of Mass Balance<br />

Modelling to Assess Production Well<br />

Capture Zones<br />

194 - Decadal scale groundwater nitrate<br />

concentrations in Western Prince Edward<br />

Island<br />

242 - Water Sustainability Act:<br />

development of legislation related to the<br />

diversion and use of groundwater in<br />

British Columbia, Canada<br />

128 - Considerations for Deep Saline<br />

Aquifer Management in Northeast British<br />

Columbia<br />

168 - Deep groundwater systems in<br />

southern Ontario: Base of fresh water,<br />

water types, and flow directions<br />

304 - Simulating Integrated Water<br />

Management for Irrigation in the Lower<br />

Republican River Basin, Kansas<br />

127 - BC Oil and Gas Commission<br />

Regulatory Framework, Groundwater<br />

Initiatives, and Key Groundwater<br />

Research Topics<br />

259 - Assessment of Non-saline water<br />

Use in Alberta’s Upstream Oil and Gas<br />

Sector between 2004 and 2013:<br />

Implications on Forecasted Water Use<br />

117 - Stable Isotope Contents of the<br />

Carbonate and Sandstone Aquifers in<br />

Winnipeg, Manitoba – A 40 Year Review<br />

of Changing Water Supply Development<br />

Conditions<br />

130 - Evaluating innovative techniques<br />

for in situ, real-time remote monitoring of<br />

nitrate in groundwater<br />

320 - Development of Groundwater<br />

Policy for Alberta’s Oil Sands Region<br />

303 - Creation of a comprehensive<br />

database to characterize surface and<br />

groundwater quality in the Peace River<br />

Regional District, North East BC,<br />

Canada<br />

256 - Geostatistical Characterization of<br />

Hydrofacies in a Heterogeneous Aquifer<br />

Considering Uncertainty in Hard Data<br />

114 - Validating effects of spring plowing<br />

forages on nitrate leaching reduction<br />

250 - Groundwater Monitoring for policy<br />

support under AEMERA<br />

IAH-CNC 2015 WATERLOO CONFERENCE<br />

31


FRIDAY PROGRAM AT A GLANCE<br />

7:15 - 8:00<br />

8:00 - 9:05<br />

9:05 - 11:45<br />

11:45 - 12:00<br />

12:30 - 13:30<br />

14:30 - 17:00<br />

Friday, October 30, 2015<br />

Continental Breakfast - Viennese Ballroom Pre-function<br />

Friday Plenary 1: Dr. Ian D. Clark - The Future of Isotope Hydrogeology<br />

9:05 - 9:20 9:20 - 9:35 9:35 - 9:50<br />

274 - M. Cathryn Ryan<br />

Hydrogeologists without Borders<br />

and the “GW2.0 Initiative”<br />

Friday Plenary 2: M.C. Ryan, R.E. Jackson, W.M. Alley, R.W. Gillham,<br />

J. Barker, E. Frind, G. van der Kamp - Insightful Moments in Hydrogeology<br />

126 - R.E. Jackson<br />

Groundwater redox processes:<br />

incorporating chemical<br />

thermodynamics into<br />

hydrogeology in the 1970s<br />

115 - W.M. Alley<br />

Temporal Scales in Groundwater<br />

Science: The Challenge to<br />

Hydrogeologists<br />

Coffee Break - Viennese Ballroom Pre-function (9:50 - 10:20)<br />

10:20 - 10:35 10:35 - 10:50 10:50 - 11:05 11:05 - 11:45<br />

248 - R.W. Gillham<br />

Laboratory demonstration of<br />

confined and unconfined aquifer<br />

storage characteristics<br />

159 - J. Barker<br />

Training the Next Generation of<br />

Hydrogeologists<br />

237 - E. Frind<br />

Groundwater Flownets: “This is<br />

where I first understood<br />

groundwater flow systems”<br />

311 - G. van der Kamp<br />

Unstated assumptions – a<br />

challenge for students and hidden<br />

traps for the unwary<br />

IAH-CNC 2015 Waterloo Closing Remarks<br />

Shuttle Buses to University of Waterloo - Farvolden Days<br />

Farvolden Lecture @ 2:30pm (University of Waterloo)<br />

Dr. David Rudolph - A Renaissance in Regional Hydrogeology: In the Footsteps of Farvolden<br />

32 IAH-CNC 2015 WATERLOO CONFERENCE


ABSTRACT TABLE OF CONTENTS<br />

Groundwater/Surface Water Interaction 1....................................................................34<br />

Road Salt Impacts on Groundwater..............................................................................38<br />

Innovation in the Remediation of Contaminated Sites 1...............................................42<br />

Groundwater Aspects of Deep Geological Repositories................................................46<br />

Groundwater/Surface Water Interaction 2....................................................................51<br />

Regional Groundwater Systems 1................................................................................54<br />

Innovation in the Remediation of Contaminated Sites 2...............................................59<br />

Surficial Geology of Southern Ontario..........................................................................63<br />

Agricultural Impacts on Groundwater 1........................................................................68<br />

Regional Groundwater Systems 2................................................................................72<br />

Flow and Transport in Fractured Rock.........................................................................77<br />

Vadose Zone Hydrogeology..........................................................................................81<br />

Groundwater/Surface Water Interaction 3....................................................................85<br />

Sustainability of Groundwater Resources 1..................................................................89<br />

Groundwater Issues From Oil and Gas Exploration & Production 1...............................94<br />

Advanced Techniques for Site Characterization ..........................................................98<br />

Groundwater/Surface Water Interaction 4 .................................................................103<br />

Sustainability of Groundwater Resources 2 ...............................................................107<br />

Innovation in the Remediation of Contaminated Sites 3 ............................................ 111<br />

Groundwater Issues from Mining & Aggregates ........................................................ 115<br />

Workshop on Groundwater Policy 1 ..........................................................................120<br />

Groundwater Issues From Oil and Gas Exploration & Production 2.............................124<br />

Regional Groundwater Systems 3 .............................................................................127<br />

Agricultural Impacts on Groundwater 2 .....................................................................132<br />

Workshop on Groundwater Policy 2 ..........................................................................136<br />

POSTER SESSION: Advanced Techniques for Site Characterization...........................141<br />

POSTER SESSION: Agricultural Impacts on Groundwater..........................................144<br />

POSTER SESSION: Flow and Transport in Fractured Rock.........................................148<br />

POSTER SESSION: Groundwater Issues from Mining & Aggregates...........................152<br />

POSTER SESSION: Groundwater Issues from Oil and Gas Exploration & Production..154<br />

POSTER SESSION: Groundwater/Surface Water Interaction......................................156<br />

POSTER SESSION: Innovation in the Remediation of Contaminated Sites..................164<br />

POSTER SESSION: Regional Groundwater Systems...................................................168<br />

POSTER SESSION: Surficial Geology of Southern Ontario..........................................176<br />

POSTER SESSION: Sustainability of Groundwater Resources....................................180<br />

POSTER SESSION: Vadose Zone Hydrogeolgy...........................................................183<br />

POSTER SESSION: Workshop on Groundwater Policy................................................188<br />

Moments of Insight in Hydrogeology..........................................................................189<br />

IAH-CNC 2015 WATERLOO CONFERENCE<br />

33


ABSTRACTS<br />

Groundwater/Surface Water Interaction 1<br />

Wednesday, October 28, 10:10 – 11:50<br />

Chair: Colby Steelman<br />

Room: Strauss<br />

201 - A Physically-Based Modelling Approach to Assess the<br />

Impact of Climate Change on Surface and Groundwater Resources<br />

within the Grand River Watershed, Ontario, Canada<br />

E.A. Sudicky, S.K. Frey, H.-T. Hwang & Y.-J. Park<br />

Aquanty, Inc., Waterloo, Ontario, Canada<br />

Department of Earth and Environmental Sciences, University of Waterloo, Waterloo,<br />

Ontario, Canada<br />

Climate change will greatly impact the availability and quality of Earth’s water resources<br />

over the next century. The expected increase in mean temperature may have a severe impact<br />

on the water cycle, not only through changing precipitation patterns and amounts,<br />

but also through an increase in the severity and frequency of extreme events. Unforeseen<br />

changes in rainfall patterns and shifting temperatures will exacerbate water management<br />

in the Grand River watershed, thus affecting the programs and operations of the Grand<br />

River Conservation Authority (GRCA). The main objective of this study is to analyze the<br />

impact of climate change forecasts on the surface and subsurface water resources within<br />

the Grand River Watershed, which is one of the more heavily populated water basins in<br />

Canada. A high-resolution 3D integrated surface-subsurface hydrological model, Hydro-<br />

GeoSphere (HGS), is first calibrated against the extensive surface and subsurface hydrologic<br />

data collected within the watershed over the past decades. Next using dynamically<br />

downscaled climate projections to drive HGS, the calibrated integrated hydrologic model<br />

is used to assess the impacts of climate change on both the surface and subsurface flow<br />

regimes within the Grand River Watershed over the next century.<br />

224 - Strategies for Integrated Model Calibration<br />

J.D.C. Kassenaar, E.J. Wexler, P.J. Thompson & M.G.S. Takeda<br />

Earthfx Incorporated, Toronto, Ontario, Canada<br />

Integrated modelling has emerged as the preferred approach to address complex watershed<br />

management, cumulative impact and engineering-scale problems such as mine or<br />

quarry development. As groundwater scientists, using an integrated model requires us to<br />

re-evaluate our assumptions and simplifying approaches previously used for surface water<br />

analysis and shallow sub-surface interactions. In a related initiative, the surface water<br />

community recently completed a 10 year effort to assess strategies and approaches for<br />

predictions in ungauged basins (PUB). In a summary of this initiative, Hrachowitz et. al.<br />

(2014) noted the need for “a major paradigm shift in scientific hydrology, traditionally rooted<br />

in empiricism and…data- and calibration focused methods to methods that are more strongly<br />

based on theoretical insights into physical processes and system understanding”. Our experience,<br />

34 IAH-CNC 2015 WATERLOO CONFERENCE


ased on the construction of more than 10 integrated GSFLOW models, is consistent<br />

with these PUB recommendations and their emphasis on basin “form and function”. For<br />

example, in a groundwater-only modelling study, model layer geometry is rarely adjusted<br />

during calibration. Our experience with GSFLOW, however, indicates that shallow system<br />

representation, including layering, soil zones, surficial geology, weathering, unsaturated<br />

zone, perched and water table feedback require that the geologist, hydrogeologist and<br />

hydrologist work closely to refine and even re-conceptualization all aspects of the shallow<br />

subsurface system during calibration. This is illustrated through examples, including a GS-<br />

FLOW simulation of the interconnection between a managed reservoir and a municipal<br />

wellfield. Shallow system process complexity means that estimates of average recharge,<br />

developed without groundwater feedback, may need to be discarded once integrated calibration<br />

has begun. Steady-state groundwater sub-models, constructed as an initial step<br />

during integrated model construction, may become obsolete once integrated model development<br />

is complete, particularly in wet season/dry season environments, fluctuating water<br />

table, or locations with significant winter processes. While integrated model development<br />

requires a larger and more diversely skilled modelling team, one of the significant benefits<br />

is that measured fluxes such as precipitation and total measured streamflow can be used<br />

as direct inputs and model calibration targets. This approach is consistent with the PUB<br />

recommendation to de-emphasize empirical flow partitioning methods such as baseflow<br />

separation, and more importantly, provide a common and consistent set of measured flow<br />

targets for both the surface water and groundwater modellers. To conclude, we feel that<br />

integrated models are more than ready to provide the key insights into basin form and<br />

function that the PUB scientists have identified.<br />

199 - Importance of Incorporating Peatlands and Winter<br />

Processes into Integrated Surface-subsurface Models of the<br />

Athabasca River Basin<br />

H.-T. Hwang, Y.-J. Park & E.A. Sudicky<br />

Aquanty, Inc., Waterloo, Ontario, Canada<br />

Department of Earth and Environmental Sciences, University of Waterloo, Waterloo,<br />

Ontario, Canada<br />

Anthropogenic water stresses including climate and land-use change, agriculture and<br />

mining activities in the Athabasca River Basin (ARB) can have significant impacts on<br />

the capacity and sustainability of the existing surface and groundwater resources within<br />

the Basin. An appropriate representation of the key surface and subsurface hydrological<br />

processes, including those relevant to peatlands and winter processes (snow accumulation<br />

and melting) is critical to improve the calibration and predictive ability of models to compute<br />

stream flow, groundwater levels and recharge rates throughout the seasons. The main<br />

objective of this study is to demonstrate the importance of the inclusion of peatland and<br />

cold-season hydrologic processes in integrated surface/subsurface models, with particular<br />

emphasis on the ARB. HydroGeoSphere (HGS), a fully-integrated surface-subsurface<br />

flow and solute transport simulator, is used here for this purpose. The high-resolution 3D<br />

HGS model of the ARB is constructed based on data from the Geological Atlas of the<br />

IAH-CNC 2015 WATERLOO CONFERENCE<br />

35


Western Canada Sedimentary Basin (Alberta Geological Survey) and the University of<br />

Maryland (UMD) global land cover classification dataset. Historical climate data maintained<br />

by the Climate Research Unit of the University of East Anglia was used to drive<br />

HGS for calibration against long-term average and transient surface flow and groundwater<br />

levels during the historic instrumental period. Based on the simulation results, it is shown<br />

that the peatland distributions and the seasonality of climatic conditions exhibit strong<br />

controls on the behaviour of the hydrologic system. In particular, the peatlands in the ARB<br />

exhibit a large influence on temporal groundwater storage and releases and evapotranspiration<br />

rates, and accounting for cold-season hydrologic processes improves the representation<br />

of the timing of peak stream flows.<br />

225 - Integrated Surface Water/Groundwater Modelling to<br />

Simulate Drought and Climate Change Impacts from the Reach to<br />

the Watershed Scale<br />

P.J. Thompson, E.J. Wexler, M.G.S. Takeda & J.D.C. Kassenaar<br />

Earthfx Incorporated, Toronto, Ontario, Canada<br />

Earthfx has developed multiple integrated surface water-groundwater models for assessing<br />

the watersheds that drain into Lake Simcoe, Ontario, Canada. The models were developed<br />

with the U.S. Geological Survey’s open-source GSFLOW code and cover a wide range<br />

of geological settings and land usage including moraine complexes, low-relief alvar plains,<br />

urban areas, and agricultural lowlands. Detailed topography and land-use data, distributed<br />

NEXRAD radar precipitation data, and a locally calibrated snowpack model allow processes<br />

to be simulated at a high spatial resolution. Model resolution varies from 100 m to<br />

200 m in the groundwater submodel and from 50 m to 100 m in the hydrologic submodel<br />

allowing for a detailed representation of the study watersheds. The study areas feature<br />

competing water uses from municipal drinking water systems, industrial and agricultural<br />

takers, quarries, gravel pits, and navigation canals which were all represented in the models.<br />

The models are run on a continuous basis and have been calibrated over multiple years to<br />

capture a wide range of climatic conditions.<br />

These projects have demonstrated the value of undertaking detailed drought assessments<br />

at the watershed scale. By considering the hydrologic and hydrogeologic systems together<br />

through an integrated modelling exercise, the overall watershed response to stress can be<br />

analyzed. The role of groundwater aquifers in mitigating extreme drought can be clearly<br />

identified and the resilience of key ecologically significant surface water features can be<br />

evaluated. Results show that drought sensitive features are often not in good contact with<br />

groundwater storage during extreme drought conditions.<br />

The assessment of the study watersheds under a changed climate was conducted using a<br />

“change field” method. Climate data for a 30-year period (2030-2060) obtained as output<br />

from a range of Global Climate Models (GCMs) were used to modify the actual observed<br />

(baseline) 30-year (1970-2000) time series. Results showed that drought sensitive areas<br />

were also stressed under future conditions where a warmer climate is predicted to reduce<br />

the amount of water stored during the summer.<br />

36 IAH-CNC 2015 WATERLOO CONFERENCE


Integrated modelling exercises can help explain the linkages between the groundwater<br />

system and surface water features. Understanding the role that geology plays in controlling<br />

both the flow and storage of water is an important exercise that can be undertaken in any<br />

sensitive watershed. This functional, hydrologic knowledge can provide the insight necessary<br />

to develop both drought and climate change adaptation strategies.<br />

272 - Balancing Near-Surface Water<br />

Eric Soulis, James Craig, Bryan Tolson, Amin Haghnegahdar & Mateusz Tinel<br />

Department of Civil and Environmental Engineering – University of Waterloo, Waterloo,<br />

Ontario, Canada<br />

The importance of lateral near-surface flow through weathered bedrock layers in hillslopes<br />

or active layers in permafrost regions requires that, to be complete, a hydrologic model,<br />

or a land surface scheme must have an interflow algorithm. Conceptual power law<br />

extensions of a vertical drainage equation, such as Campbell or Brooks-Corey, generally<br />

poorly parameterised interflow. The equations require several parameters that are difficult<br />

to calibrate. At the opposite extreme of the complexity spectrum, are numerical solutions<br />

of Richards Equation that are too cumbersome for meso-scale modelling.<br />

This presentation will demonstrate a cleaner, easier approach: a power law expression using<br />

effective saturation approximates the modeled outflow from a sloping confined aquifer.<br />

The solution is a weighted combination of an expression for pure saturated and pure unsaturated<br />

flow from the seepage base of the aquifer. The weighting coefficient is determined<br />

from the soil pore-size distribution. The result is a Weibull-like expression that requires<br />

only the SCS sand and clay fractions, along with valley slope and length. These parameters<br />

are available in most models.<br />

The method, called the Tilted Landscape Element (TILE) approach is suitable for surface<br />

element in groundwater models or land-surface schemes. TILE has been implemented in<br />

StandAlone— Modélisation Environmentale–Surface et Hydrologie (SA-MESH). The<br />

method will be illustrated with examples from its use in SA-MESH.<br />

IAH-CNC 2015 WATERLOO CONFERENCE<br />

37


Road Salt Impacts on Groundwater<br />

Wednesday, October 28, 10:10 – 11:50<br />

Chair: Rachel Vaillancourt<br />

Room: Wagner<br />

211 - Recent Field Data Confirm Previous Predictions That<br />

Toronto’s Groundwater Faces a Serious Decline in Water Quality<br />

due to Road Salt<br />

Ken W.F. Howard & Max Stone<br />

University of Toronto Scarborough, Ontario, Canada<br />

Nader Mansour<br />

ENSTA ParisTech, Paris, France<br />

Research undertaken in Toronto during the mid- to late-1980s drew attention to the serious<br />

impacts of road salt on groundwater quality. Shallow springs sampled along the Lake<br />

Ontario shoreline showed chloride concentrations as high as 2800 mg/L, while a water<br />

sample collected several metres below surface, close to an urban highway, revealed chloride<br />

as high as 14000 mg/L. A subsequent salt balance study conducted in the Highland Creek<br />

catchment in the eastern suburbs of Toronto suggested that over 50% of salt applied each<br />

year to urban catchments is released to groundwater and thus takes many decades to leave<br />

the basin. Based on estimated groundwater travel times, it was forecast that chloride in<br />

groundwater discharging as baseflow in the Highland Creek Catchment would increase<br />

from its existing value of around 140 mg/L, to over 400 mg/L within a 20 year time frame.<br />

Recent follow-up studies in the basin have largely confirmed the earlier predictions. Salt<br />

balance studies conducted between 2005 and 2008 demonstrate that baseflow concentrations<br />

of chloride now vary from around 500 mg/L in the late spring to around 250-300<br />

mg/L in the early fall, a summer season trend that is interpreted to represent a gradual<br />

draining of the “urban karst”. Over the three-year period, end of season chloride concentrations<br />

showed a significant annual increase. A recent re-sampling of springs along the<br />

Lake Ontario shoreline also confirms the long-term decline of urban groundwater quality<br />

that was predicted in the 1980’s. In 1985, 39 spring samples collected as they emerged<br />

from eastern Toronto’s deeper aquifer system showed an average chloride concentration of<br />

88 mg/L, with nearly two thirds containing


Road salt is impacting surface and groundwater drinking water sources, vegetative and<br />

aquatic biota, soil matrices and infrastructure life cycles. The Ministry of the Environment<br />

and Climate Change (MOECC) has prescribed application, handling and storage<br />

of road salt as a significant threat to municipal drinking water under the Clean Water Act,<br />

2006 (CWA). In response to the CWA, Source Protection Committees have conducted<br />

technical studies that determined that the application, handling, and storage of road salt is<br />

deteriorating sources of municipal drinking water.<br />

Halton Region completed a review of all municipal drinking water threat activities and<br />

estimated their respective potential contributions to salt loading within their Cedarvale<br />

Wellhead Protection Area. This study concluded that 85% of total salt loading within<br />

their Wellhead Protection Area is attributed to the application of road salt on private parking<br />

lots. Further research concluded that there are no Minimum Maintenance Standards<br />

contractor’s responsible for winter maintenance on private lots, most winter maintenance<br />

contracts are based on amount of salt applied and there are no parking lot design standards<br />

that optimize road salt application within Ontario.<br />

Halton Region is collaborating with their lower tier municipalities to develop a Salt Management<br />

Strategy (SMS) in response to both Regional Council and the MOECC’s direction<br />

to protect municipal drinking water sources from the application, handling, and<br />

storage of road salt within vulnerable areas throughout Halton Region. While maintaining<br />

public safety, the SMS provides salt optimization parking lot design guidelines to municipal<br />

staff responsible for approval new large parking lots within vulnerable areas, and<br />

provides awareness through education and outreach materials the impacts of road salt to<br />

municipal drinking water sources.<br />

244 - Quantifying the Impact of Road Salt Management Practices<br />

on Water Quality in Public Supply Wells within the Region of<br />

Waterloo<br />

D. L. Rudolph 1 , J. Melchin 2 , M. Stone 1 & G. Sarwar 1<br />

1<br />

University of Waterloo, Waterloo, Ontario, Canada<br />

2<br />

Matrix Solutions Inc, Breslau, Ontario, Canada<br />

Long-term road salt application has increased sodium and chloride concentrations in<br />

drinking water wells in many cold climate communities. The Regional Municipality of<br />

Waterloo (RMOW) implemented various road salt best management practices (BMPs)<br />

designed to reduce the impact of the winter deicers on public supply wells. During the<br />

winter 2004-2005, the RMOW set a 25% reduction target in the amount of NaCl applied<br />

to city streets in wellhead protection areas and a 10% reduction target for all other city<br />

streets within the vicinity of the Greenbrook Well Field where elevated levels of sodium<br />

and chloride had been observed. Prior to the implementation of these reductions, in 2001-<br />

2002, pre-BMP estimates of road salt loading to the water table were made by quantifying<br />

the mass loading along various representative road types by tracking the salt mass flux<br />

through the vadose zone. Salt transport was evaluated through the analysis of replicate core<br />

samples collected along curbs at selected field sites over several annual cycles. Post-BMP<br />

IAH-CNC 2015 WATERLOO CONFERENCE<br />

39


estimates of road salt loading to the water table were made by repeating the earlier field<br />

program from 2008 to 2010. The data indicate that the average pore water Cl concentration<br />

had reduced by approximately 65% and the average cumulative stored chloride mass in<br />

the vadose zone had reduced by approximately 30%. The average mass loading to the water<br />

table was estimated to have reduced by over 40% following the reduction in the road salt<br />

application rates. Water table monitoring wells installed at each of the field locations confirmed<br />

a progressive reduction in chloride concentration over time. To our knowledge, this<br />

is the first study of its kind to quantitatively assess the effects of best management practices<br />

to reduce the impacts of road salt to ground water by directly comparing pre-BMP and<br />

post-BMP chloride levels. The results suggest that the road salt management practices<br />

involving the reduction in the application rate of the deicers implemented by the RMOW<br />

can significantly reduce the loading to the water table and subsequently result in a progressive<br />

decrease in groundwater chloride concentrations ultimately leading to improved water<br />

quality in the public supply wells.<br />

122 - Assessment of Road Salt Impacts to Four Priority Well Fields<br />

in the Region of Waterloo<br />

Michael L. Duchene, Tiffany Svensson & Ian Macdonald<br />

BluMetric Environmental Inc., Kitchener, Ontario, Canada<br />

Rachel Vaillancourt & Geoff Moroz<br />

Hydrogeology and Source Water, Regional Municipality of Waterloo, Kitchener, Ontario,<br />

Canada<br />

The Regional Municipality of Waterloo obtains approximately 75% of its drinking water<br />

supply from 122 groundwater supply wells. The on-going assessment of the water quality<br />

has shown that sodium and chloride concentrations are close to or have exceeded the<br />

drinking water objectives at four priority well fields, William Street, Greenbrook, Parkway<br />

and Middleton Street. Assessments on the issue of elevated chloride and sodium levels in<br />

these well fields have been ongoing since the 1990s. This assessment was an update and<br />

expansion of previous assessments.<br />

The primary assessment tool used was a mass balance model developed by the Region.<br />

The model predicts the mass loading in the extracted groundwater by integrating the chloride<br />

loading (portion of road salt that infiltrates to the groundwater) and factoring in the<br />

advective travel time to the production well based on the capture zone delineation. Salt<br />

application on both roadways and parking lots was input into the model. The mass of salt<br />

applied to roads was reported by the cities. The mass of road salt applied to parking lots<br />

was estimated by determining the total area of parking lots in each wellhead protection<br />

area and estimating the application rate.<br />

Currently there are no guidelines and little published data for the application of salt on<br />

parking lots. Two surveys completed by others were obtained and a survey was completed<br />

as part of this assessment to quantify the salt applications used on parking lots. The results<br />

indicate that the general range of salt application on parking lots is between 50 g/m 2 and<br />

75 g/m 2 .<br />

40 IAH-CNC 2015 WATERLOO CONFERENCE


It was estimated that between 50% and 80% of the salt applied in the WHPAs was applied<br />

on the roads with the remainder applied to parking lots. The inclusion of the loading from<br />

parking lots resulted in the estimation of the portion of salt applied to the surface that<br />

infiltrates being about one half of previous estimates completed considering only the salt<br />

applied to roads.<br />

The model was calibrated to historical data and used to predict salt concentrations in the<br />

supply wells using current application rates of road salt. The concentrations of sodium and<br />

chloride in two of the well fields are predicted to continue to meet the drinking water objectives.<br />

Reduction in salt loadings of 25% and 40% are required to achieve drinking water<br />

objectives in the other two well fields.<br />

121 - Salt Assessment of a Low Demand, Rural Well Field IAH-CNC<br />

2015 Waterloo Conference<br />

M.J. Fraser, R. Byer-Coward & R. Freymond<br />

Stantec Consulting Ltd., Kitchener, Ontario, Canada<br />

R. Vaillancourt & E. Hodgins<br />

Regional Municipality of Waterloo, Kitchener, Ontario, Canada<br />

The Regional Municipality of Waterloo (RMOW) was alerted by elevated chloride concentrations<br />

at one of their rural well fields and recognized that work was required to evaluate<br />

potential sources and future chloride trends. The source of chloride was not as clearly<br />

understood as in the urban environment where road salt is generally the primary contributor.<br />

The rural well field supplied a small community where waste water was treated using<br />

residential septic systems. The water supplied by the bedrock aquifer was hard, meaning<br />

many residents were using water softeners. In addition, supply from this well field was minor,<br />

about 14,000 m 3 /year, resulting in a limited well field capture zone. The low pumping<br />

rate and small capture zone meant that a relatively small amount of salt could result in<br />

increased concentrations of chloride at the production wells.<br />

A salt assessment was undertaken to assess the current extent of chloride within the aquifer<br />

system, evaluate future trends in chloride concentrations, and evaluate potential BMPs<br />

and/or well field operation and monitoring strategies with the objective of reducing chloride<br />

concentrations at the wells. Preliminary calculations indicated that chloride loading<br />

from water softeners and road salt may both be significant sources of chloride at the production<br />

wells.<br />

IAH-CNC 2015 WATERLOO CONFERENCE<br />

41


Innovation in the Remediation of<br />

Contaminated Sites 1<br />

Wednesday, October 28, 10:10 – 11:50<br />

Chair: Jason Gerhard<br />

Room: Schubert<br />

132 - Electrokinetically-Enhanced Remediation: An Innovative<br />

Solution to Vexing Challenges for Source Area Remediation<br />

Evan Cox 1 , David Reynolds 2 & James Wang 3<br />

1<br />

Geosyntec Consultant, Waterloo, Ontario, Canada<br />

2<br />

Geosyntec Consultant, Kingston, Ontario, Canada<br />

3<br />

Geosyntec Consultant, Columbia, Maryland, USA<br />

Charlotte Riis & Martin Bymose<br />

NIRAS A/S, Alleroed, Denmark<br />

David Gent<br />

US Army Engineer R&D Center, Vicksburg, Mississippi, USA<br />

Mads Terkelsen<br />

Capital Region, Hilleroed, Denmark<br />

Contaminants in clays and silts are long-term sources of pollutants to groundwater, requiring<br />

costly remediation and monitoring over many decades. Significant advances have been<br />

made in the past few years in the area of electrokinetically (EK) enhanced amendment<br />

delivery to treat contaminant source areas in low permeability (low K) and highly heterogeneous<br />

subsurface materials. EK is an innovative approach that uses electrokinetic mechanisms<br />

to promote migration of amendments through clays/silts through electromigration,<br />

electroosmosis and/or electrophoresis. EK approaches are not dependent on hydraulic conductivity,<br />

and can therefore achieve uniform and rapid distribution of amendments in clays<br />

and silts. Amendments can include electron donors (e.g., lactate), electron acceptors (e.g.,<br />

nitrate), and/or bacteria (e.g., Dehalococcoides, Dehalobacter) for in situ bioremediation<br />

(EK-BIO), or oxidants such as permanganate for in situ chemical oxidation (EK-ISCO).<br />

A recent novel addition to the EK toolbox is EK-thermally activated persulfate (EK-TAP)<br />

which uses the same infrastructure to both deliver persulfate through clays and silts (using<br />

DC current), followed by heating of the soils (using AC current, which is the basis for electrical<br />

resistance heating), to heat the soils to ~40 o C to activate the persulfate and destroy<br />

contaminants in situ.<br />

This presentation will discuss how and where each of these EK remediation technologies<br />

works, and will present results from multiple field applications, including a large full-scale EK-<br />

BIO application at a site in Denmark, a second EK-BIO field application at a United States<br />

Navy site in Florida, and several field applications of EK-TAP, EK-ISCO, and EK-ZVI at<br />

chlorinated solvent sites in the United States and Canada. The results of these field applications<br />

show that EK enhanced amendment delivery can be a cost-effective and sustainable means of<br />

accelerating remediation of source areas in low K and heterogeneous materials.<br />

42 IAH-CNC 2015 WATERLOO CONFERENCE


190 - Integrating Risk Management into Redevelopment of an<br />

Urban Brownfield Site<br />

Bradley Carew & Sandra Pilgrim<br />

City of Ottawa, Ottawa, Ontario, Canada<br />

J. David Miller<br />

Department of Chemistry – Carleton University, Ottawa, Ontario, Canada<br />

Kevin Hicks<br />

AMEC Foster Wheeler, Ottawa, Ontario, Canada<br />

Stuart Bailey<br />

AMEC Foster Wheeler, Mississauga, Ontario, Canada<br />

Lansdowne Park is owned by the City of Ottawa. The 16 ha site has been used since<br />

1888 as a fairground and for sports events. The lands were also used as staging areas for<br />

the military during the Boer War and WWI and WWII. The redevelopment plan included<br />

a new underground parking garage, residential, retail, a stadium, and recreational<br />

areas. Bounded on one side by the historic Rideau Canal, the site is surrounded by mature<br />

residential housing, shops and restaurants. As portions of the site were being changed to<br />

a more sensitive land use, Records of Site Condition (RSC) under Ontario Regulation<br />

153/04 were required.<br />

During the early development of the site, portions of inlets adjacent to the Rideau Canal<br />

were filled with landfill waste. Coal heating was used to heat some of the buildings dating<br />

back to 1896. Unsurprisingly, the environmental investigations identified soil contaminated<br />

by PAHs and metals. To minimize the environmental impact, all contaminated soils<br />

were kept on-site and appropriate risk management measures developed to ensure no impacts<br />

to human health or the environment.<br />

To facilitate the redevelopment, the site was split into three distinct zones. Zone A consisted<br />

of the new parking garage, retail and residential buildings. Zone B consisted of the existing<br />

hockey arena and football stadium and two existing buildings. Zone C encompassed<br />

a new municipal park including an orchard, large open greenspace, skating rink, public art<br />

pieces and pathways.<br />

In total, 30,000 m 3 of contaminated soils were excavated from the new parking structure and<br />

used construct an earthen berm. This strategy eliminated the environmental costs and public<br />

nuisance of transporting the contaminated soil off site. To address community concerns, air<br />

monitoring was conducted to document the management of dusts during the remedial work.<br />

The future parkland portion of the site (Zone C) contained the historic landfill which was<br />

approximately 50,000 m 3 in size. Park features were designed to allow this to remain in<br />

place and also accommodate the relocated contaminated soils from Zone A. This resulted<br />

in savings of >$8 million. Innovative risk management strategies for the future park included<br />

selection of shallow rooting tree species and hard and soft caps above the contaminated<br />

soils. In 2014, a risk-based RSC was filed for the parkland portion of the site (Zone C).<br />

The innovative soil management strategy, risk assessment and staged development were<br />

keys factors that lead to a successful brownfield redevelopment project.<br />

IAH-CNC 2015 WATERLOO CONFERENCE<br />

43


214 - Treatment of Manufactured Gas Plant Residuals Using<br />

Alkaline Activated Persulfate: A Pilot-Scale Trial<br />

Felipe Solano 1 , Neil R. Thomson 1 & Ramon Aravena 2<br />

1<br />

Department of Civil and Environmental Engineering, University of Waterloo, Waterloo,<br />

Ontario, Canada<br />

2<br />

Department of Earth and Environmental Sciences, University of Waterloo, Waterloo,<br />

Ontario, Canada<br />

Remediation of dense non-aqueous phase liquids (DNAPLs) in subsurface environments<br />

is a significant challenge. The presence of tars associated with former manufactured gas<br />

plants (MGPs) magnifies this challenge due to their complex chemical composition.<br />

In situ chemical oxidation (ISCO) has emerged as an effective remediation method for<br />

groundwater contaminated with compounds associated with MGP residuals; however, the<br />

science-base to support the treatment of MGP residuals is lacking. In addition, the interpretation<br />

of aqueous concentration data alone is often insufficient to quantify remediation<br />

efficiency. The use of compound specific stable isotope analysis to complement concentration<br />

data can be very helpful in distinguishing between chemical oxidation and non-oxidation<br />

processes, and therefore in appropriately quantifying the efficiency of chemical<br />

oxidation.<br />

The aim of this research effort is to evaluate the efficiency and effectiveness of using alkaline<br />

activated persulfate to treat MGP residuals present at a former MGP site, and to<br />

assess the potential application of compound specific isotope analysis (CSIA) as a tool to<br />

monitor the treatment performance. This is a multi-year research effort involving source<br />

area characterization, bench-scale experiments, push-pull tests, installation of oxidant delivery<br />

infrastructure, and a pilot-scale trial followed by a long-term monitoring program.<br />

Based on the results of the site characterization, bench-scale experiments and push-pull<br />

tests, this pilot-scale trial focuses on a portion of the identified source zone (target treatment<br />

zone – TTZ) in which shallow (4.5 m bgs) MGP residuals<br />

have been observed. Two injection episodes to satisfy oxidant dosing requirements are prescribed.<br />

Twelve permanent wells were used to ensure complete sweep of the TTZ was possible.<br />

To supplement the extensive monitoring network already present, seven multi-level<br />

monitoring wells were installed within and slightly downgradient of the TTZ to capture<br />

oxidant distribution and downgradient concentration changes. A resistivity probe network<br />

was used to provide real-time changes in the electrical conductivity within the TTZ. To<br />

assess treatment performance, dissolved phase concentrations, contaminant mass in the<br />

TTZ, and mass discharge across a downgradient transect are being used in conjunction<br />

with CSIA, residual persulfate, sulfate, and sulfide data. Results from this un-biased performance<br />

assessment will be used to generate a comprehensive data set that will demonstrate<br />

the capabilities of alkaline activated persulfate to treat MGP residuals in situ.<br />

44 IAH-CNC 2015 WATERLOO CONFERENCE


116 - The Effect of Injection Methods on the Distribution of<br />

Remedial Compounds<br />

Rick McGregor<br />

InSitu Remediation Services Ltd, St. George, Ontario, Canada<br />

The application of in situ methods for treating contaminants within groundwater and soil<br />

has increased over the past decade. The understanding of how contaminants are remediated<br />

using a variety of compounds is fairly well understood and demonstrated. However,<br />

numerous studies/project using in situ remediation have resulted in incomplete realization<br />

of the remedial objectives. In order for in situ methods to be effective, the injected compounds<br />

must interact directly or indirectly with the contaminant. Site specific factors such<br />

as geology, hydrogeology, geochemistry, contaminant distribution, etc. play an important<br />

role in controlling the design of any in situ program, as does understanding the role of<br />

advection and diffusion in the delivery and transport of the compounds to the contaminant.<br />

Unfortunately very few studies have been completed in the field to look at the actual<br />

distribution of compounds.<br />

A field study was conducted in an unconsolidated, unconfined aquifer to evaluate various<br />

injection and delivery methods for a variety of oxidants and reductants including persulfate,<br />

percarbonate, hydrogen peroxide and emulsified vegetable oil. Delivery methods examined<br />

for each oxidant included injection through vertical wells, injection by direct push technology<br />

using drop point and side tool technologies. The results of the study indicated that the<br />

delivery method has a significant impact on the distribution of the compound within the<br />

subsurface whereas the type of compound also impacted the distribution geometry within<br />

the aquifer tested. Direct push technology offered superior distribution compared to injection<br />

of the compounds into vertical wells with injection through side tools showing better<br />

vertical and lateral distribution than drop point methodology. These results suggest that<br />

the choice of delivery method is a key design parameter for any in situ remedial program<br />

and that the delivery method needs to be customized based on site-specific factors to the<br />

choice of remedial compound being used.<br />

249 - Enhanced in situ Bioremediation of Chlorinated Solvents in<br />

Canada<br />

Jeff Roberts, Phil Dennis, Sandra Dworatzek & Peter Dollar<br />

SiREM, Guelph, Ontario, Canada<br />

Bioremediation of chlorinated solvents, including perchloroethene (PCE) and trichloroethene<br />

(TCE), in groundwater is a proven and cost effective remedial approach. KB-1 ® , a<br />

bioaugmentation culture that promotes the complete dechlorination of chlorinated ethenes<br />

to ethene has been used extensively for bioremediation projects around the world. KB-<br />

1® is the only anaerobic bioaugmentation culture to receive Federal regulatory acceptance<br />

through the New Substance Notification (NSN) regulation process and was added to the<br />

Domestic Substances List in 2008. Since then KB-1 ® has been applied successfully at<br />

several sites in Canada.<br />

IAH-CNC 2015 WATERLOO CONFERENCE<br />

45


Geological and geochemical conditions commonly found in Canada that should be considered<br />

when implementing a bioremediation approach include: low groundwater temperatures,<br />

low permeability matrices and fractured rock. Recent experience implementing<br />

bioremediation remedies under these conditions have provided insights and lessons<br />

learned for optimizing bioremediation of chlorinated solvents in Canada.<br />

Groundwater temperatures defined as cold (i.e., below 10 º C) are commonly found north<br />

of 45 degrees latitude. Understanding the feasibility of bioremediation of chlorinated solvents<br />

and the practical limits of bioremediation under cold conditions is important in<br />

remedy selection and expectation management for high latitude bioremediation projects.<br />

Examples of successful bioremediation at sites in Alaska, Denmark and Canada, will be<br />

presented with a focus on degradation half-lives, concentrations of dechlorinating bacteria<br />

(Dehalococcoides [Dhc]) and remediation outcomes.<br />

Low permeability strata are common in some of the most highly industrialized areas of<br />

Canada; notably in Southern Ontario and Quebec. Originally conceived as an oil and<br />

gas extraction technology, hydraulic fracturing can also be used to improve distribution of<br />

bioremediation amendments thereby improving bioremediation outcomes. Examples of<br />

successful implementation of hydraulic fracturing and other approaches for bioremediation<br />

in clay strata and fractured rock environments will be discussed. One such site, in the<br />

Toronto area, with groundwater concentrations of PCE, TCE and cis-1,2-dichloroethene<br />

(cDCE) above regulatory limits will be presented. A high pressure grout pump was used<br />

to inject EHCTM electron donor and KB-1 ® . After KB-1 ® application, a 10,000-fold<br />

increase in Dhc abundance was observed from pre to post bioaugmentation in less than<br />

one year. cDCE concentrations declined concurrently to below detection limits, reaching<br />

Ontario regulatory standards (Table 3) and site remedial objectives in the target monitoring<br />

wells for all chlorinated compounds within 1.5 years of bioaugmentation.<br />

Groundwater Aspects of Deep Geological<br />

Repositories<br />

Wednesday, October 28, 10:10 – 11:50<br />

Chair: Mark Jensen<br />

Room: Heritage<br />

228 - Deep Geologic Repositories: Developing a Geoscientific<br />

Basis for Long-Term Safety<br />

M.R. Jensen & M. Hobbs<br />

Nuclear Waste Management Organization, Toronto, Ontario, Canada<br />

The Nuclear Waste Management Organization (NWMO) is responsible for implementing<br />

the Adaptive Phased Management (APM) Program, Canada’s approach for the longterm<br />

management of its nuclear used fuel. The APM program, approved by the federal<br />

government in June 2007, envisions that nuclear used fuel would be placed within a<br />

46 IAH-CNC 2015 WATERLOO CONFERENCE


multi-barrier Deep Geologic Repository (DGR) in a suitable crystalline or sedimentary<br />

bedrock formation at a nominal depth of 400 to 700 m. As part of APM, a technical<br />

program is directed by the NWMO to advance the understanding of fractured crystalline<br />

and sedimentary groundwater systems as they related to assessing site-specific suitability<br />

for implementation of the DGR concept and, ultimately, the passive safety of a selected<br />

site on timescales of 1 Ma (NWMO 2015). The Geoscience program is multi-disciplinary<br />

with a focus on geology, geochronology, structural geology, seismicity, hydrogeochemistry,<br />

isotope hydrology, physical hydrogeology, numerical groundwater system analysis, reactive<br />

transport simulation, sorption, microbiology, paleohydrogeology, geomechanics and glaciation.<br />

A motivation for the work is the characterisation of deep-seated aquitard/aquiclude<br />

systems typified by low permeability (


227 - Deep-Seated Aquiclude Groundwater Systems: Advances in<br />

In Situ Hydraulic Testing<br />

Richard L. Beauheim<br />

Consulting Hydrogeologist, Grand Junction, Colorado, USA<br />

Randall M. Roberts<br />

HydroResolutions LLC, Parshall, North Dakota, USA<br />

John D. Avis<br />

Geofirma Engineering Ltd., Ottawa, Ontario, Canada<br />

Mark Jensen<br />

Nuclear Waste Management Organization, Toronto, Ontario, Canada<br />

A key aspect of groundwater studies in deep-seated aquiclude systems relates to the estimation<br />

of formation-scale physical hydrogeological properties. Within such extremely<br />

low permeability (>10 -20 m 2 ), low storage (S s<br />

≈10 -6 m -1 ), and typically saline groundwater<br />

systems, this presents unique challenges. As part of site-characterization activities for a<br />

proposed Deep Geologic Repository (DGR) for low- and intermediate-level radioactive<br />

waste at the Bruce nuclear site, 90+ straddle-packer (30-m interval) tests were performed<br />

in Silurian- and Ordovician-age shale and carbonate sediments intersected by 6,<br />

150-mm-diameter vertical or dipping (60-65° from horizontal) boreholes separated by<br />

approximately 1200 m. Estimates of in situ horizontal rock mass hydraulic conductivity<br />

(K) within these Paleozoic-age sediments ranged between 2x10 -16 and 4x10 -8 m/s. The<br />

tests were performed with a purpose-built straddle-packer assembly that included a surface-actuated<br />

downhole valve and a fixed-volume downhole pulse generator. A typical test<br />

sequence in the lower permeability sediments required a 3-day cycle involving multiple<br />

pulses with real-time analysis to assess adequacy of data for detailed analysis. In addition<br />

to hydraulic conductivity, estimates of static formation hydraulic heads were obtained that<br />

indicated the presence of abnormal formation underpressure (≈250 m+) conditions within<br />

the Ordovician sediments, since confirmed by Westbay multi-packer installations in the<br />

boreholes. Estimates of K derived from the field tests of the low-permeability Cobourg<br />

Formation compare favorably to estimates from laboratory tests on core samples (≈10 cm)<br />

and to natural analogue formation-scale (≈100+ m) data. This presentation will describe<br />

the borehole testing methodology and a comparison of test results to complementary measurements<br />

in establishing a basis to assess aquiclude hydraulic properties.<br />

170 - Pore Fluid Pressures in the Ordovician Sediments at<br />

the Bruce site near Kincardine, Ontario: Potential Causes and<br />

Analysis<br />

Stefano D. Normani, Yong Yin & Jonathan F. Sykes<br />

Department of Civil and Environmental Engineering – University of Waterloo, Waterloo,<br />

Ontario, Canada<br />

Site-specific analogues provide a unique means to assess groundwater system properties<br />

and behaviour at time and space scales not otherwise achievable. Formation pressure head<br />

measurements within low permeability Silurian to Cambrian age sediments on the east-<br />

48 IAH-CNC 2015 WATERLOO CONFERENCE


ern flank of the Michigan basin have revealed abnormal vertical head distributions and<br />

gradients inconsistent with hydrostatic conditions. Westbay pressure data from the DGR<br />

boreholes at the Bruce site indicate that the Cambrian sandstone and the Silurian Guelph<br />

Formation are significantly over-pressured relative to fluid density corrected hydrostatic<br />

levels while within the intervening 360 m sequence of Ordovician limestone and shale,<br />

heads are significantly under-pressured. This study investigates various physical processes<br />

in the interpretation of the pressures as relevant to understanding formation scale hydraulic<br />

properties on geologic timescales. Three physically based numerical models were developed<br />

to investigate the evolution of pore fluid pressures: glacial loading without crustal<br />

flexure, exhumation of post Devonian sediments, and the presence of a non-wetting gas<br />

phase in the rock. Using the computational models FRAC3DVS-OPG and TOUGH2-<br />

MP, the parameter estimation model PEST, and a one-dimensional conceptual model, all<br />

models could describe the under-pressures. A fourth physically based numerical model was<br />

developed to assess the effect of crustal flexure on the generation of in-situ pore fluid pressures<br />

at the Bruce site. Both flexural stresses and vertical stresses, imposed by the weight of<br />

an ice-sheet, affect the formation of in-situ pore fluid pressures through hydro-mechanical<br />

coupling. A two-dimensional finite element poroelastic simulator was written to support<br />

this analysis; verification to analytical solutions yielded an excellent match. Multiple lines<br />

of evidence, including in-situ hydraulic testing (Beauheim, 2014), geochemical analyses<br />

(Al et al., 2015; Clark et al., 2013), and numerical modelling (Sykes et al., 2011), support<br />

the conclusion that the Cobourg Formation and the shales of the Ordovician age sediments<br />

are of very low permeability and have sustained their very low permeabilities over<br />

geologic time.<br />

350 - Diffusion research in support of the Canadian nuclear waste<br />

management program<br />

Tom Al 1 , Mark Jensen 2 , & Ian Clark 1<br />

1<br />

Earth Sciences, University of Ottawa, Ottawa, Ontario, Canada<br />

2<br />

Nuclear Waste Management Organization, Toronto, Ontario, Canada<br />

The requirement to understand the diffusive properties of rocks is fundamental to site<br />

characterization for geologic repositories. Recent research in this area has resulted in the<br />

development of new magnetic-resonance imaging (MRI) and radiation-imaging (RI)<br />

methods for measurement of diffusion and reaction properties including pore- and effective-<br />

diffusion coefficients (D p<br />

and D e<br />

), tracer-accessible porosity (φ tr<br />

), cation-exchange<br />

capacity (CEC) and ion selectivity coefficients (e.g. logK Cs_Na<br />

). The RI techniques are rapid<br />

and versatile, involving either an X-ray or a gamma source ( 241 Am) source. The experiments<br />

are conducted principally with iodide as a conservative tracer and weakly sorbed<br />

cesium for reactive transport experiments. Site investigations for the DGR proposed by<br />

OPG for low- and intermediate-level waste at the Bruce nuclear site in Ontario provided<br />

opportunity to apply the new measurement methods, and to investigate effects of specific<br />

tracers, anisotropy, confining pressure and scale. One hundred and thirteen measurements<br />

were conducted across 700 m of Paleozoic stratigraphy by a combination of X-ray radiography<br />

and the conventional through-diffusion technique. With the exception of a few<br />

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samples from the Upper Silurian, the D e<br />

values (iodide tracer) are 10 -12 m 2 /s or lower. The<br />

D e<br />

values obtained with tritiated water (HTO) tracer are on average 1.9 times greater<br />

(range 0.8 to 4.9) than measured with iodide due to anion exclusion. The sample-scale<br />

anisotropy ratios (D e<br />

parallel versus D e<br />

normal to bedding) are 0.9 to 4.9 for iodide and<br />

1.1 to 7.0 for HTO. Diffusion measurements were conducted with confining pressure up<br />

to 17.4 MPa. For measurements with HTO tracer, increasing confining pressure results<br />

in decreases in D e<br />

up to -34%, and with iodide tracer the decreases were as large as -44%.<br />

Comparison of numerical simulations to measured depth profiles for naturally occurring<br />

porewater tracers allowed for assessment of diffusion coefficients at the formation scale.<br />

Using best available estimates for boundary and initial conditions, simulated tracer profiles<br />

do not match the measured profiles unless the diffusion coefficients are decreased relative<br />

to the laboratory-measured values by a factor between five and ten for chloride, and between<br />

one and three for 18 O. Future efforts will focus on measurement of diffusion coefficients<br />

for dissolved gases (e.g. CH 4<br />

, CO 2<br />

and He) and refinement of the RI methods to<br />

improve tracer detection so that the method can be applied to rocks with very low porosity,<br />

and to expand the range of tracers for both conservative and reactive transport.<br />

273 - Coupled Groundwater Flow and Reactive Transport<br />

Simulations of the Evolution of Groundwater Chemistry for a Deep<br />

Geologic Repository in Shield Rocks<br />

Lee Hartley, Steve Joyce, & Hannah Woollard<br />

Amec Foster Wheeler, Harwell Oxford, Didcot, Oxfordshire, United Kingdom<br />

Niko Marsic, & Magnus Sidborn<br />

Kemakta Konsult AB, Stockholm, Sweden<br />

Björn Gylling & Ignasi Puigdomenech<br />

Svensk Kärnbränslehantering AB, Stockholm, Sweden<br />

Lasse Koskinen<br />

Posiva Oy, Olkiluoto, Eurajoki, Finland<br />

SKB, Swedish Nuclear Fuel and Waste Management Company, has submitted a license<br />

application for a spent nuclear fuel repository at Forsmark sited in crystalline rocks of the<br />

Fennoscandian shield. In support of this application various quantitative assessments were<br />

made to demonstrate the long-term safety of the proposed repository. One such assessment<br />

involved simulation of the long-term evolution of groundwater chemistry as a factor<br />

affecting performance of the disposal system, since this requires geochemical conditions<br />

are maintained within specified limits, specifically relating to salinity, pH and redox conditions.<br />

In the reference case the current temperate period lasts until 12,000 AD. A case of<br />

prolonged meteoric infiltration to 60,000 AD is also considered resulting from e.g. global<br />

warming. This is to fulfil a regulatory request to assess whether extended dilute water<br />

infiltration might lead to a rise in redox potential and also to an increase in erosion of the<br />

bentonite barrier due to formation of colloids. In order to simulate long-term transient<br />

groundwater flow and solute transport with water-solute-rock interactions in 3D regional<br />

equivalent porous medium models, new tools have been developed to closely couple<br />

geochemical, groundwater flow and transport calculations, and perform these efficiently<br />

50 IAH-CNC 2015 WATERLOO CONFERENCE


using parallel computing techniques. In assessing this case, sensitivities are tested to the<br />

geochemical reaction schemes appropriate to the site. The results of this work predict the<br />

chemical environment at repository depth stabilises at around 20,000 AD and shows little<br />

change beyond that. The salinity of the groundwater is governed by the low permeability<br />

(ca. 10 -19 m 2 ) of the bedrock and rock matrix diffusion, resulting in relatively shallow and<br />

slow circulation of groundwater. The chemical reactions influence concentrations of reactive<br />

species, including pH and redox potential. In particular, the redox reactions thought<br />

to be relevant for the Forsmark site maintain reducing conditions at depth favourable to<br />

repository performance, even with infiltration at the ground surface of meteoric water with<br />

relatively high redox potential.<br />

Groundwater/Surface Water Interaction 2<br />

Wednesday, October 28, 13:00 – 14:40<br />

Chair: Steven Berg<br />

Room: Strauss<br />

135 - Pressure Pulses as an Indication of Recharge to a Buried<br />

Esker-Aquifer Eastern Ontario<br />

Jacques Sauriol<br />

Stantec Consulting Ltd., Ottawa, Ontario, Canada<br />

Recharge pressure pulses from significant rainfall events were correlated to near-synchronous<br />

hydraulic head responses in both the overlying muds and the buried Vars-Winchester<br />

esker aquifer in Eastern Ontario. These correlations were analyzed to gain a better understanding<br />

of the recharge processes in this paired-system. Although causation was only<br />

suggested, a correlation was nonetheless established between rainfall events and aquifer<br />

head response suggesting that there is a hydraulic connection between the mud and the<br />

esker units. Strong cross-correlations with short lag times were calculated (0.9 at lag times<br />

of between 0 and 3 hours). Furthermore, response sequencing for the radar precipitation<br />

events generated at the study site showed that the pressure pulses arrived in the overlying<br />

muds slightly before the underlying buried esker, indicating a downward migration of the<br />

pressure pulses. Mud layering deformation in seismic surveys had previously been observed<br />

in the over-esker muds. These disturbed stratigraphic elements provide an avenue for migrating<br />

water to transit through the muds. This paper hypothesizes that recharge pressure<br />

pulses can rapidly reach the buried esker across the over-esker unit transiting through<br />

preferential flow paths in deformed mud sediments. This revised model of understanding<br />

challenges the natural safeguard allegations of marine muds and defies the widespread acceptance<br />

of the mode of recharge of buried aquifer limited at esker outcrop. These findings<br />

have implications for Source Water Protection Strategies.<br />

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247 - Subsurface Water Flow from Wetlands to the Riparian Zone<br />

Induced by Evapotranspiration<br />

Masaki Hayashi 1 & Garth van der Kamp 2<br />

1<br />

Department of Geoscience, University of Calgary, Calgary, Alberta, Canada<br />

2<br />

Environment Canada, Saskatoon, Saskatchewan, Canada<br />

Subsurface interaction between wetlands and the surrounding riparian zone has significant<br />

effects on water balance and dissolved mass balance of wetlands. This is particularly important<br />

for relatively small wetlands that are not dominated by inflow and outflow streams,<br />

such as prairie wetlands. Summer water loss from prairie wetlands is strongly dependent<br />

on the ratio of the shoreline length to the area of water surface, suggesting that significant<br />

portion of water loss from the wetlands is due to evapotranspiration in the marginal area,<br />

where the water table within or is close to the root zones of riparian plants. The present<br />

study will examine the factors that control the subsurface flow of water from wetlands to the<br />

riparian zone using a simple numerical model and compare the results to the distribution<br />

of soil types in and around wetlands. The subsurface water flow consists of two processes.<br />

The first is the mostly horizontal flow from the surface water body to the saturated zone<br />

underlying the riparian vegetation. The hydraulic conductivity of saturated sediments is<br />

dominated by fractures and other macropores and is orders of magnitude higher than that<br />

of unsaturated sediments. Therefore, much of horizontal flow takes place in the saturated<br />

region below the water table. The second is the mostly vertical flow from the water table<br />

to plant roots, which is strongly dependent on soil water retention characteristics. The<br />

effective width of the riparian zone is determined by the hydraulic properties of sediments<br />

that control the two processes. In the prairie region, which is covered by clay-rich glacial<br />

tills, the effective width is expected to be in the order of 10 m, which is consistent with field<br />

observation of vegetation zones (i.e. willow ring) and soil type distribution. These results<br />

are quite general and may be used to study, for example, the interaction between streams<br />

and the riparian vegetation in most dry climates.<br />

139 - Detecting Hyporheic Exchange Using Electrical Resistivity<br />

Tomography along a Fractured Sedimentary Bedrock River:<br />

Eramosa River, Guelph, Ontario<br />

Colby M. Steelman 1 , Celia S. Kennedy 2 , Donovan Capes 1 & Beth L. Parker 1,2<br />

1<br />

School of Engineering – University of Guelph, Guelph, Ontario, Canada<br />

2<br />

School of Environmental Sciences – University of Guelph, Guelph, Ontario, Canada<br />

The Eramosa River located within the Grand River Watershed in Ontario, Canada, resides<br />

upon a densely fractured dolostone aquifer with abundant dissolution-enhanced<br />

channel features. While the bedrock aquifer represents a major component of the total water<br />

supply for the surrounding region, potential effects of increased groundwater extraction<br />

on surface water and surrounding ecosystems are not yet fully understood. In general,<br />

little is known about the nature of the interaction between surface water and groundwater<br />

along densely fractured sedimentary bedrock riverbeds. For instance, the timing and magnitude<br />

of groundwater - surface water exchange in a fractured carbonate rock environment<br />

52 IAH-CNC 2015 WATERLOO CONFERENCE


is expected to differ significantly from its alluvial channel analogs due to the presence<br />

of highly transmissive, planar and strongly orientated discrete fracture features that control<br />

flow. Non-invasive geophysical methods represent an opportunity to evaluate shallow<br />

groundwater dynamics with minimal environmental risk to biota and, ultimately enhance<br />

the interpretation of direct hydrogeologic data. A spatial electrical conductivity survey<br />

completed along a 200 m reach of the Eramosa River indicated a seasonally dynamic hyporheic<br />

response over a riffle-pool sequence. Subsequent time-lapse electrical resistivity<br />

measurements collected at a 2-3 week interval from July 2013 through June 2014 along<br />

two 50 m transects perpendicular to the river flow indicates a spatially dynamic response.<br />

The first transect was positioned over a section of intact bedrock with exposed vertical and<br />

horizontal fractures, while the second transect was positioned across a section of weathered<br />

bedrock with a thin layer of course sediment. These data provided snapshots of electrical<br />

resistivity distribution across the riverbed to a maximum depth of 6-8 m. Surface water,<br />

sub-riverbed (hyporheic zone), groundwater temperature and electrical conductivity were<br />

continuously monitored over the annual cycle. The apparent geoelectrical response will<br />

be examined in terms of hyporheic exchange as indicated by temperature and electrical<br />

conductivity variations.<br />

246 - A Method for Utilizing Data from Extreme Hydrological<br />

Events to Trigger Enhanced Monitoring and Sampling in<br />

Watersheds<br />

Andrew J. Wiebe<br />

Department of Earth and Environmental Sciences - University of Waterloo, Waterloo,<br />

Ontario, Canada<br />

Gabriele Perotti<br />

Department of Earth Sciences - Università degli studi di Roma “La Sapienza”, Rome, Italy<br />

David Rudolph & Ramon Aravena<br />

Department of Earth and Environmental Sciences - University of Waterloo, Waterloo,<br />

Ontario, Canada<br />

Water quality changes due to hydrological events may be difficult to capture given the<br />

dynamic nature of groundwater-surface water interactions. It is challenging to schedule<br />

manual sampling in order to capture peak flow rates or the first flush of event water (which<br />

could potentially carry anomalously high or low contaminant concentrations) to a stream<br />

or an aquifer. There is a need for automatic sampling at specific times of interest, and for<br />

near real-time data transmission to inform watershed managers that collected samples<br />

need to be picked up for analysis. It is hypothesized here that a characteristic “slope” in a<br />

given data set (e.g., a change in water level per unit time) could be used to detect events<br />

in incoming data at remote field stations, and to trigger automatic water sampling and in<br />

situ geochemical measurements. An advanced datalogging platform governing a system of<br />

sensors can be programmed to recognize different patterns during the year (e.g., recharge<br />

from snowmelt vs. a summer rainstorm), and to assess whether concentrations of certain<br />

chemical constituents or their indicators are increasing along with water levels. This<br />

method may be useful when compound triggers based on historical data are desired for<br />

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advanced, event-based sampling. Example data streams collected through the Southern<br />

Ontario Water Consortium’s Alder Creek Watershed facility will be used to demonstrate<br />

this approach and to illustrate the utility of adopting near real-time watershed monitoring<br />

for groundwater and surface water applications.<br />

255 - Estimating Depression-Focussed Recharge in The Prairies<br />

Using a One-Dimensional Model<br />

Saskia L Noorduijn, Masaki Hayashi & Laurence R. Bentley<br />

Department of Geoscience, University of Calgary, Calgary, Alberta, Canada<br />

The contribution of small topographic depressions to groundwater recharge in the northern<br />

prairie landscape has proven challenging to estimate. However, the aggregate recharge<br />

contributions of these small topographic depressions to the underlying aquifers may be<br />

considerable. Thus, accurately quantifying depression-focused recharge will aid in the development<br />

of sustainable groundwater management practice. Previous research has primarily<br />

focused on determining the hydrological fluxes at the scale of individual depressions.<br />

There has been a recent move towards increasing the scale of interest to investigate<br />

depression hydrological processes at scales ranging from 10’s of km up to the size of the<br />

entire watershed. At these larger scales, applicable models are subject to a trade-off between<br />

accuracy of the recharge estimate and computational demand. The least computationally<br />

demanding approach would be the use of a one-dimensional (1D) model for each<br />

grid cell. However, invoking the 1D assumption will likely produce considerable error in<br />

the estimated recharge when multiple topographic depressions are represented in one grid<br />

cell. An alternative approach is to categorize topographic depressions based on their surface<br />

area and density within one grid cell. The 1D model can then be applied to estimate<br />

recharge from each of these categories. The total estimated recharge for that grid cell is<br />

obtained as the summation of estimated recharge contributions from each category within<br />

that grid cell. This approach implemented within a 1D model is hypothesized to produce<br />

more realistic recharge estimation whilst limiting computational demand.<br />

Regional Groundwater Systems 1<br />

Wednesday, October 28, 13:00 – 14:40<br />

Chair: Tom Gleeson<br />

Room: Wagner<br />

140 - Groundwater Residence Times in Chaudière-Appalaches,<br />

Québec: Closing the Loop between Flow and Regional<br />

Geochemistry<br />

Debora Janos 1 , John Molson 1 , & René Lefebvre 2<br />

1<br />

Département de géologie et génie géologique – Université Laval, Québec City, Québec,<br />

Canada<br />

2<br />

Centre Eau Terre Environnement – INRS, Québec City, Québec, Canada<br />

54 IAH-CNC 2015 WATERLOO CONFERENCE


The regional basin-scale PACES projects in Québec, Canada, are comprehensive hydrogeological<br />

characterisation studies aiming to further the understanding of regional-scale<br />

groundwater flow dynamics and natural geochemical processes. As part of the PACES<br />

III project in the Chaudière-Appalaches region, south of Quebec City, the study herein<br />

presents insights into the extent to which regional groundwater quality is shaped by flow<br />

dynamics. In this context, several different numerical modelling approaches are applied<br />

including 2D and 3D regional flow modelling, geochemical evolution, density-dependent<br />

salt (brine) transport and groundwater age.<br />

The first of a three-step modelling approach consists of a vertical two-dimensional model<br />

along an assumed regional flow path. This 70-km section extends from the Appalachians<br />

highlands (Internal Humber Zone), to the south, to the St. Lawrence River, to the<br />

north. The model is calibrated using water levels from the extensive MDELCCC boring<br />

log database, and simulated residence times are compared with sampled 14 C water ages.<br />

Although some evidence for deeper regional flow exists, the area appears dominated by<br />

sub-regional flow systems on maximum scales of about 10-20 km, with significant flow<br />

through the shallow fractured sedimentary rock aquifer. This regional scale model is also<br />

used to help constrain the subsequent geochemical model, by providing indications regarding<br />

regional flow dynamics, including the maximum depth of active flow, the effects<br />

of water density and the extent to which deep basinal brines contribute to the regional<br />

flow. The second modelling step entails identifying dominant geochemical processes by<br />

performing mass balance analyses on characteristic water types found from recharge to<br />

discharge zones in the study area. Several important processes have been identified, including<br />

carbonate dissolution, Ca 2+ - Na + cation exchange and mixing with marine water<br />

and perhaps basinal brines. In the final step, PHREEQC is used to model the geochemical<br />

evolution of groundwater along a representative regional flow line identified in the first<br />

modeling step. Residence times derived from the flow model are also used to constrain the<br />

one-dimensional transport model. The use of residence times as the common parameter<br />

between flow dynamics and geochemical evolution helps verify the spacio-temporal coherence<br />

of the previously recognized geochemical processes by bounding them to a time-scale.<br />

189 - Uniform-density, ‘full-matrix’ hydrogeochemical mapping of<br />

southern Ontario<br />

Stewart Hamilton<br />

Ontario Geological Survey, Ontario, Canada<br />

Groundwater geochemical data are often collected and treated as ‘water quality data’ and<br />

compared against the benchmark of regulatory standards. This is not unreasonable since<br />

regional groundwater sampling programs are usually justified on a public health basis.<br />

However, this approach ignores the predictive value of appropriately collected aqueous<br />

geochemical data. Many groundwater processes, including those that affect public heath,<br />

can be revealed by studying the full geochemical matrix of water samples, irrespective of<br />

actual concentrations of individual parameters. Dissolved constituents never exist in isolation<br />

of each other, or of the host formation, and characterizing the geochemical matrix<br />

provides insights into factors such as solubility of hazardous constituents, flow history,<br />

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natural or anthropogenic hazards and water quality risk prediction. A minimum suite of<br />

parameters including the 7 major ions, pH, redox and certain dissolved gases, in addition<br />

to any health-related parameters of interest, provides much more information than the<br />

sum of their individual contributions.<br />

A full-matrix groundwater geochemical sampling program has been completed in southern<br />

Ontario at an unmatched scale, density and degree of analytical completeness. 2300<br />

samples collected at 1850 stations at a uniform sample density across the 96,000 km 2 area<br />

allows the mapping of groundwater geochemical regimes in most of southern Ontario for<br />

the first time. Dozens of phenomena and processes have been identified at all scales, many<br />

of which were previously unknown. A few examples of the processes Identified include: (1)<br />

wide regions of biogenic shale gas, (2) a 1400 km 2 breathing well zone expelling hypoxic<br />

gases, (3) stagnant flow zones, (4) provincial-scale patterns in the distribution of tritium in<br />

groundwater, (5) regions where iodine in potable water exceeds seawater by many times,<br />

(6) decadal-scale trends in aquifer recovery and depletion, (7) the replacement of ancient<br />

water in aquifers with modern water due to pumping, (8) provincial-scale regions of natural<br />

fluoride hazard (9) areas of systemic bacterial occurrence in aquifers, and (10) widespread,<br />

discreet zones of karstic groundwater flow. Most of these discoveries could not have<br />

been anticipated when the program began 8 years ago, which demonstrates the efficacy of<br />

primary data collection and geological mapping in the support of groundwater studies.<br />

207 - A study of flow system dynamics utilizing a diverse set of<br />

isotopic and geochemical methods; Oak Ridges Moraine, Ontario<br />

Lori Labelle & Shaun Frape<br />

Department of Earth and Environmental Science, University of Waterloo, Waterloo, Ontario,<br />

Canada<br />

Rick Gerber<br />

Oak Ridges Moraine Hydrogeology Program, Toronto, Ontario, Canada<br />

The Oak Ridges Moraine (ORM) is a 160-km long ridge a mixture of sand, silt and gravel<br />

deposits north of Lake Ontario, and extends west to east from the Niagara Escarpment to<br />

Peterborough and the Trent River. Understanding the complex flow system is complicated by<br />

the regional geology, which includes aquifers in the bedrock valleys, till aquifers, and eroded<br />

tunnel channels separated by aquitards. The Oak Ridges Moraine is recognized as a regionally<br />

significant groundwater recharge area and is an important source of domestic water for<br />

the Greater Toronto Region, along with providing base flow to hundreds of local streams.<br />

This regional study examines a diverse moraine complex, consisting of sediments ranging<br />

from earlier glaciations (~130k) to considerably younger materials from recent glacial<br />

events (~20k) (Barnett et al. 1998). This results in a very complex flow system within<br />

the Oak Ridges Moraine, consisting of multiple aquifer/aquitard units and end members<br />

causing multiple potential mixing scenarios. To assess this complicated hydrostratigraphy<br />

a diverse range of age dating and isotopic methods have been used in the study. Naturally<br />

occurring stable isotopes can be used to trace groundwater flow paths and provide direct<br />

evidence of the vulnerability of an aquifer; as well as provide insight into flow systems at<br />

56 IAH-CNC 2015 WATERLOO CONFERENCE


various scales within the moraine complex. Historically studies use environmental age tracers<br />

to examine flow and mixing in aquifers (Solomon et al. 1995), though on the scale of<br />

the Oak Ridges Moraine there have been few studies that have attempted to integrate such<br />

a diverse set of environmental isotopic and geochemical tracers to constrain groundwater<br />

pathways and ages.<br />

Stable isotopic results from this study have defined three distinct groundwater types;<br />

post-glacially recharged waters with no tritium and depleted oxygen isotopic signatures,<br />

a minority of samples are recharged from waters having undergone evaporative processes<br />

and represent monitoring wells with a direct connection to surface waters and finally the<br />

majority of samples have measurable tritium (up to 183.5 TU), suggesting a large component<br />

of recently recharged meteoric water. As with Fritz et al 1987 these samples show<br />

isotopic change with geographical distribution across the study region. Mixing between<br />

these groundwater groups is prevalent as a result of usage. Rare gas data combined with<br />

stable isotopes and environmental tracers will help to understand the different flow systems<br />

within the ORM, mean residence time, temperature at the time of recharge and mixing.<br />

185 - Groundwater Resources and Use in York Region – Lessons<br />

Learned from Source Water Protection<br />

Donald Ford<br />

Toronto and Region Conservation, Downsview, Ontario, Canada<br />

Tom Bradley<br />

Regional Municipality of York, Newmarket, Ontario, Canada<br />

The Clean Water Act, 2006 was created to ensure the protection of drinking water in Ontario<br />

through the development of watershed-based source protection plans. These plans<br />

are the first step in a multi-barrier approach to ensure safe drinking water for the residents<br />

of Ontario. The plans are based on technical assessments of the many different sources<br />

of drinking water and the potential quality and quantity threats to those sources. Part of<br />

these assessments is a comprehensive analysis of groundwater and surface water resources<br />

available as compared to the ecological and human uses of those resources.<br />

Water budgets show each part of a watershed’s hydrologic system, and use data to describe<br />

how much water enters a watershed, how much water is stored within it, and how<br />

much water leaves it through both natural and human processes. This information helps<br />

determine how much water is available for human use while ensuring sufficient water<br />

for key natural heritage features and functions. Groundwater forms a critical part of any<br />

water budget. Recharge in headwater areas or even outside of the surface catchment of a<br />

watershed, may support critical ecological functions and human abstraction in the middle<br />

and lower reaches.<br />

The Regional Municipality of York (York) and the Toronto and Region Conservation<br />

Authority (TRCA) have been working together with respect to water budget modeling<br />

since 2005. These efforts began with the development of a conceptual water budget for<br />

the entire TRCA jurisdiction and culminated in an integrated surface water/groundwater<br />

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numeric model that covered 80% of the TRCA jurisdiction plus a significant portion of<br />

York Region. The York Tier 3 project facilitated a review of all of the conceptual geologic<br />

models that have been developed in this geographic area, extending from Lake Simcoe<br />

to Lake Ontario. This paper documents how this integration of data and interpretation<br />

facilitated new ideas and stratigraphic interpretations and the lessons learned within the<br />

jurisdiction of the TRCA.<br />

179 - Challenges Implementing ASR in the Region of Waterloo<br />

Don Corbett, Tim Walton, Matt Bender & Joe Pereira<br />

Region of Waterloo, Kitchener, Ontario, Canada<br />

The Region of Waterloo (Region) is located in southern Ontario, Canada and provides<br />

drinking water to both urban and rural municipalities with a combined population of approximately<br />

560,000 people. The Region is the largest municipal user of groundwater in<br />

Canada with an average daily production of over 145 million litres and approximately 75%<br />

of the supply provided by ground water.<br />

The Region operates an Aquifer Storage and Recovery (ASR) system as part of its Integrated<br />

Urban Water Supply System. Like many fast growing communities in Canada,<br />

the Region has been assessing its sustainable long-term water supply options. The ASR<br />

program is an integral part of the Region’s long term water supply strategy.<br />

The concept underlying the ASR program is to store or “bank” treated surface water in<br />

the semi-confined sand and gravel aquifer formations below the Mannheim Water Treatment<br />

Plant (MWTP). During periods of low consumption, excess treated water from the<br />

MWTP is stored in the aquifer. Inversely, this water is recovered and enters the MWTP<br />

process when consumption is highest. With this in mind, a feasibility assessment and pilot<br />

study were completed in the 1990’s and justified moving forward with a full-scale Stage 1<br />

program in 2004.<br />

Currently, the capacity of the Region’s ASR system is approximately 20 million litres per<br />

day (6,000 acre-feet). Based on performance of Stage 1, the Region has developed plans<br />

for a Stage 2 program with another 20 million litres per day as part of the Region’s overall<br />

Long Term Water Supply Strategy.<br />

The hydrogeologic setting at the MWTP presents some unique challenges for ASR. The<br />

relatively thin saturated thickness of the Mannheim Aquifer, coupled with high aquifer<br />

transmissivities, means injected water flows to the surrounding aquifer relatively quickly<br />

making it difficult to store and completely recover the injected water within a limited<br />

timeframe. This is further compounded by pumping constraints imposed on the system by<br />

the regulatory Permit to Take Water.<br />

In terms of water quality, there are some unique challenges associated with the formation<br />

of disinfection by-products (DPBs) and maintaining acceptable water quality in the<br />

Mannheim Aquifer. The operational strategy for the ASR system has changed since inception<br />

and differs significantly from the original concept. Notwithstanding this change,<br />

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the ASR System provides much-needed stability and flexibility during periods of peak<br />

water demand.<br />

This paper will expand on the lessons learned with the Stage 1 ASR program over the last<br />

decade and how the Region will move forward with its Stage 2 program.<br />

Innovation in the Remediation of<br />

Contaminated Sites 2<br />

Wednesday, October 28, 13:00 – 14:40<br />

Chair: Jason Gerhard<br />

Room: Schubert<br />

203 - Dissolution of Light Non-Aqueous Phase Liquid from Smear<br />

Zones Containing Trapped Air<br />

M.H. Shojib & K.G. Mumford<br />

Department of Civil Engineering – Queen’s University, Kingston, Ontario, Canada<br />

Understanding the dissolution of non-aqueous phase liquid (NAPL) at contaminated sites<br />

is important for designing effective remediation and monitoring schemes. Smear zones of<br />

lighter-than-water NAPL (LNAPL) are created by fluctuations of the water table, which<br />

can trap both residual LNAPL and gas (atmospheric air) below the water table. NAPL<br />

is expected to distribute differently in the presence of water and gas than in the presence<br />

of water only, resulting in lower NAPL saturations and higher interfacial areas per unit<br />

volume available for NAPL dissolution. In this study, a series of one-dimensional (1D)<br />

column experiments were conducted to investigate the effect of trapped gas on the dissolution<br />

of residual LNAPL. The columns contained either toluene and water or air, toluene,<br />

and water, emplaced by sequential drainage and imbibition representative of a water table<br />

oscillation. Each column was flushed continuously with water, and aqueous samples of the<br />

column effluent were collected and analyzed during dissolution of the emplaced sources.<br />

Results showed that toluene dissolution was faster in the NAPL-water-gas experiments<br />

than in the NAPL-water experiments, with higher effluent concentrations being observed<br />

during early-stage dissolution followed by long tailing concentrations. Effluent toluene<br />

concentrations in the NAPL-water-gas experiments were higher than in the NAPL-water<br />

experiments even during the dissolution of similar toluene NAPL saturations, suggesting<br />

that the interfacial area-to-volume ratios in the NAPL-water-gas sources were higher<br />

due to the presence of the trapped air. Analysis of the results using existing empirical<br />

correlation models developed using NAPL-water experiments showed that these models<br />

over-predicted early toluene concentrations, and under-predicted later concentrations,<br />

when applied to the NAPL-water-gas experiments. These models also under-predicted<br />

the time required for dissolution of the NAPL source. The results of this study show that<br />

the dissolution of NAPL in the presence of trapped gas is substantially different than<br />

dissolution that occurs in the absence of gas and that predictions of natural attenuation<br />

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and remediation performance in smear zones containing trapped air that are made using<br />

existing two-phase correlation models could be misleading.<br />

156 - Nature, Nurture and Sustainable Remediation: Case Study<br />

From a Major Hydrocarbon Release in a Sensitive Urban Riverine<br />

Environment<br />

K.J. O’Shea, Tiana Robinson, Nathaniel Novosad, Karen Wright, Tereza Dan &<br />

Ulysses Klee<br />

Stantec Consulting Limited, Stoney Creek, Ontario, Canada<br />

Long-term, sustainable remedial solutions are often overlooked following a high-profile<br />

spill. Instead, there is a drive to fix the issue immediately, and remedial plans are often put<br />

into place without a sufficient understanding of subsurface conditions or consideration<br />

of other natural features. The rush to a solution can cause significant additional harm to<br />

the environment during implementation. This talk presents a case study of a hydrocarbon<br />

spill in a sensitive riverine environment, and describes how nurturing naturally occurring<br />

processes utilizing the physical characteristics of the site can result in an elegant and sustainable<br />

solution to a complex remedial problem.<br />

In 2010 a pipeline release of approximately 90,000 litres of petroleum hydrocarbons (PHC)<br />

occurred in a creek valley outside a major urban center in Ontario. The affected area was<br />

nearly 3.5 acres. The site is classified as an area of natural and scientific interest, is part of<br />

provincially significant wetland complex, is considered environmentally sensitive, and has a<br />

well-developed tree canopy. The site is home to wildlife such as by wild turkey, deer, beaver,<br />

and snapping turtles, and the creek is a popular recreational fishing area.<br />

From the time of the release, there was significant pressure from various interested parties to<br />

implement a full scale “dig and dump” strategy to manage the impacts at the site. If implemented,<br />

this would have resulted in complete removal of the vegetation at the site, as well as<br />

all overburden materials and shallow bedrock in the excavated area. The complete devastation<br />

of the biota, plus the slow recovery of the sensitive environment to current conditions would<br />

takes years. During the yearlong excavation program, significant construction traffic to local<br />

neighborhoods, and considerable costs, would be incurred. All stakeholders eventually recognized<br />

that while the dig and dump approach was viscerally satisfying, it was not practical or<br />

appropriate, given the relative health of the vegetation and wildlife in the affected area. Stantec<br />

completed additional site investigation and characterization activities, and developed a more<br />

sustainable remedial strategy for the site that was still protective of human health and the environment<br />

that also considered the social, economic, and environmental benefits of the approach.<br />

Stantec’s proposed solution to address remaining impacts at the site is currently being<br />

implemented, and was developed in consultation with the regulators and stakeholders. In<br />

the end, a multi-prong approach was selected that included risk assessment, phytoremediation,<br />

enhanced bioremediation and groundwater recovery. This solution will ultimately<br />

minimize the impacts to neighbourhood residents, recreational site users, and vegetative<br />

and wildlife communities.<br />

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178 - Simulation of Persulfate Oxidation Coupled with Enhanced<br />

Bioremediation as an Emerging Remediation Strategy for<br />

Petroleum Impacted Sites<br />

Mahsa Shayan, Neil R. Thomson & James F. Barker<br />

University of Waterloo, Waterloo, Ontario, Canada<br />

John Molson<br />

Department of Geology and Geological Engineering, Université Laval, Québec City, Québec,<br />

Canada<br />

Groundwater contamination by petroleum hydrocarbon (PHC) compounds, including<br />

the high impact, toxic and persistent monoaromatic compounds such as benzene, toluene,<br />

ethylbenzene and xylene (BTEX) poses a serious risk to human health and the environment.<br />

Innovative and efficient remediation strategies are required to mitigate such risks in<br />

a smart, and cost and time effective manner. The coupling or sequential use of different<br />

remediation technologies, also referred to as a “treatment train”, is an emerging remediation<br />

strategy that combines the strengths of each individual remediation technology to<br />

improve the overall treatment efficiency and minimize clean-up cost and time. Coupling<br />

in situ chemical oxidation (ISCO) and enhanced bioremediation (EBR) is an example of a<br />

plausible treatment train for the application at PHC-contaminated sites.<br />

Persulfate (S 2<br />

O 8<br />

2-<br />

) is a persistent but yet aggressive oxidant that has been successfully applied<br />

for the treatment of PHC-contaminated sites, and it also has a significant inherent<br />

advantage in the context of being an integral part in an ISCO/EBR treatment train. The<br />

reaction of persulfate with organic compounds leads to the production of sulfate, which<br />

along with the breakdown of complex organic compounds into simpler and more bioavailable<br />

organic substrates, can lead to enhanced biodegradation activity of a group of<br />

microorganisms known as sulfate reducing bacteria (SRB). Subsequently, the enhanced<br />

bioremediation under sulfate reducing conditions is expected to dominate the removal of<br />

the remaining contaminant mass following persulfate treatment.<br />

The effectiveness of a persulfate/EBR treatment train is dependent on the delivery and mixing<br />

of persulfate and sulfate in situ. Application of a modelling tool capable of simulating the intertwined<br />

physical, chemical and biological processes involved in a persulfate/EBR treatment train<br />

is useful to understand the influence of the key processes (e.g., flow and transport, reaction kinetics,<br />

design parameters) on treatment effectiveness. To date, there has been no reported effort<br />

made to simulate a persulfate-based ISCO treatment system or an ISCO/EBR treatment train.<br />

In this study, a modelling tool (BIONAPL/PS) was developed to simulate the coupled<br />

processes involved in a persulfate/EBR treatment train and to quantify the impact of various<br />

parameters on the performance of this treatment system. The key processes captured<br />

in this model include transient groundwater flow, multi-component advective-dispersive<br />

transport, persulfate decomposition, chemical oxidation of dissolved PHCs, and biodegradation<br />

under various redox conditions. The model also simulates the inhibitory impact<br />

of persulfate on subsequent sulfate reduction. The formulation of BIONAPL/PS was validated<br />

against an analytical solution, and observations from a series of laboratory column<br />

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experiments designed to mimic a persulfate/EBR treatment train. Data from a pilot-scale<br />

experiment conducted at the University of Waterloo Groundwater Research Facility at<br />

the Canadian Forces Base (CFB) Borden were used in a model benchmarking effort. The<br />

modelling tool was also used to evaluate opportunities for performance optimization of the<br />

combined remedy system.<br />

This presentation focuses on the development and application of the BIONAPL/PS model,<br />

and a discussion of the simulation results.<br />

200 - A Comprehensive Environmental Assessment Tool for<br />

Estimating the Design and Performance of Permeable Reactive<br />

Barriers<br />

H.-T. Hwang 1, 2 , S.-W. Jeen 3 , E.A. Sudicky 1, 2 & W.A. Illman 2<br />

1<br />

Aquanty, Inc., Waterloo, Ontario, Canada<br />

2<br />

Department of Earth and Environmental Sciences, University of Waterloo, Waterloo,<br />

Ontario, Canada<br />

3<br />

Department of Earth and Environmental Sciences & The Earth and Environmental Science<br />

System Research Center, Chonbuk National University, Jeonju-si, Jeollabuk-do, Republic of Korea<br />

The applicability of a multispecies chain-decay transport model (CMM; Sudicky et al.,<br />

2013) is examined by estimating the kinetic rate constants and branching ratios along<br />

the abiotic degradation pathways for trichloroethene (TCE) reduction by zero-valent iron<br />

(ZVI). The model is calibrated using multispecies concentration data obtained from longterm<br />

laboratory column experiments performed under different geochemical conditions,<br />

with the estimated reaction parameters being estimated using a Levenberg-Marquardt<br />

inversion procedure. Compared to the column receiving deionized water containing TCE,<br />

the column receiving TCE in a CaCO 3<br />

solution showed higher mean degradation rates<br />

for TCE and all of its degradation products. From the calculated branching ratios, it was<br />

found that TCE and cis-dichloroethene (cis-DCE) were dominantly dechlorinated to<br />

chloroacetylene and acetylene, respectively, through reductive elimination in both columns.<br />

In order to assess the long-term performance ZVI PRB’s, Monte Carlo probabilistic<br />

simulations were performed using the mean reaction parameter values and their uncertainties<br />

estimated from the inverse algorithm. Using a large number of realizations, the average<br />

concentrations of the six chlorinated ethenes were shown to decrease dramatically within<br />

a relatively short distance within the iron wall barrier. The probability of the contaminant<br />

concentrations exceeding drinking-water limits at the effluent end of the PRB also decreased<br />

dramatically as the flow path length through the PRB was increased.<br />

305 - In Situ Remediation of Coal Tar by STAR: Self-Sustaining<br />

Propagation across Clean Sand Gaps<br />

Joshua K. Brown, Jason I. Gerhard, Jose L. Torero & Gavin Grant<br />

Department of Civil and Environmental Engineering – University of Western Ontario,<br />

London, Ontario, Canada<br />

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Self-sustaining Treatment for Active Remediation (STAR) is an emerging remediation<br />

technique which utilizes a subsurface smouldering reaction to destroy non-aqueous phase<br />

liquids (NAPL) in situ. The reaction is self-sustaining in that, once started for a local ignition<br />

point (e.g., well), the destructive front will propagate outwards using only the energy<br />

embedded in the contaminant as long as there is sufficient contamination and delivery of<br />

air. Recent interest from industry has prompted research into lab-scale investigations of<br />

the efficacy of STAR for site specific conditions. Efforts to characterize the subsurface<br />

contamination at numerous former manufactured gas plants (MGPs) have shown that<br />

the coal tar can occur as both a continuous pool as well as in distinct seams separated by<br />

clean layers of varying thickness. STAR should be able to ‘jump’ across clean sand gaps and<br />

propagate a self-sustaining reaction in the contaminated region beyond if enough energy<br />

to reignite is transmitted across the gap. This experimental study evaluates the ability of<br />

STAR to cross clean sand gaps in coal tar contaminated porous media in both one- and<br />

two-dimensional systems. Sensitivity to various in situ and engineering control parameters<br />

are explored including: coal tar layer thickness, soil permeability, moisture content, NAPL<br />

saturation, and air injection flowrate. High resolution thermocouples reveal the progress<br />

of the reaction, continuous gas emissions analysis reveals when the reaction is active and<br />

dormant, and careful excavation map the extent of remediation and whether gaps were<br />

successfully jumped. This is coupled with thermal imaging videos which map the progress<br />

of the front across the gaps. The work has demonstrated that substantial gaps, much larger<br />

than previously anticipated, can indeed be jumped by the reaction (e.g., more than 35 cm,<br />

reaching the limit that can be measured in the laboratory). Also observed was the mobilization<br />

of pre-heated coal tar into some clean gaps and the reaction’s ability to propagate<br />

through and destroy coal tar beside and within the gaps. This work provides new insights<br />

into the robust nature of the technology for in situ applications, and explores the degree of<br />

heterogeneity required before the reaction is impeded and a new ignition location would<br />

be required.<br />

Surficial Geology of Southern Ontario<br />

Wednesday, October 28, 13:00 – 14:40<br />

Chair: David Sharpe<br />

Room: Heritage<br />

231 - Regional buried bedrock valleys, infill sediments and<br />

stratigraphy in southern Ontario: a review<br />

Cunhai Gao<br />

Ontario Geological Survey, Sudbury, Ontario, Canada<br />

Large buried bedrock valleys and depressions in the Great Lakes region have been studied<br />

since the late 19th century. In southern Ontario, they include, notably, broad bedrock<br />

troughs and gorge-like bedrock valleys, e.g., the Laurentian bedrock trough, Erigan valley,<br />

Milverton and Wingham bedrock gorges, and the Dundas valley among many other<br />

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e-entrant bedrock valleys on the Niagara Escarpment. Spencer’s pioneer work in the late<br />

19th century on buried bedrock valleys has had profound influence on the subsequent<br />

studies on these geologic features as to their origins and age. A commonly held view is that<br />

these bedrock valleys and depressions were carved by the Tertiary rivers and subject only to<br />

limited glacial modification in the Pleistocene. Many adopted this concept in subsurface<br />

mapping and their interpretation of such features in southern Ontario and elsewhere in<br />

the Great Lakes region. Consequently, the bedrock valleys and depressions are often interpreted<br />

as relic river channels with a dendritic planview and any deep bedrock depressions<br />

encountered locally in geotechnic and groundwater drilling are thought to be segments<br />

of such fluvial features. With the availability of large datasets of borehole records, advent<br />

of computer-aided contouring technology, and the advances in our understanding of the<br />

subglacial processes and hydrology, the regional buried bedrock valleys and depressions<br />

can be mapped and studied in a much detailed way. Recent bedrock topography mapping<br />

has shed new light onto these geologic features as to their orientation, planviews, spatial<br />

relationship, and internal geometry, e.g., longitudinal profiles. This work has also revealed<br />

for the first time, below Lake Erie, a glacially-scoured large bedrock valley named Long<br />

Point trench along the lake basin. The newly acquired information does not confirm the<br />

previously assumed relic river channels and drainage connections. Instead, it suggests that<br />

the bedrock valleys can best be explained in the context of glacial and subglacial meltwater<br />

erosion. To be specific, the deep bedrock gorges are likely of subglacial meltwater tunnel<br />

valley origin and those broad ones such as Laurentian and Ipperwash troughs are created<br />

through erosion by multiple glaciers over the Pleistocene. The glacial and subglacial meltwater<br />

processes have generated extensive clayey to gravelly deposits that fill the bedrock<br />

valleys and depressions with great thickness. Many of the gorge-like bedrock valleys likely<br />

developed during the Late Wisconsinan and they contain concentration of glaciofluvial<br />

sand and gravel deposits which are important regional aquifers.<br />

230 - The pre-Late Wisconsin stratigraphy of Simcoe County,<br />

southern Ontario<br />

Riley P.M. Mulligan & Andy F. Bajc<br />

Ontario Geological Survey, Sudbury Ontario, Canada<br />

Sediment drilling investigations by the Ontario Geological Survey in Simcoe County have<br />

identified thick sediment successions (>140 m) underlying Late Wisconsin glacial deposits.<br />

These sediments record environmental conditions that existed prior to and during the<br />

last build-up of the Laurentide Ice Sheet. Pre-Late Wisconsin sediments are subdivided<br />

into 5 stratigraphic units (SU’s). A lowermost glacial package directly overlies Paleozoic<br />

bedrock. It is composed of two distinct tills, a lower sandy till (SU1) and an upper silt-rich<br />

till (SU3), rarely separated by fine-grained glaciolacustrine deposits (SU2). The upper surface<br />

of the silt till is extensively weathered and, in places, leached of carbonate. This weathering<br />

records base levels up to 30 m below modern Lake Huron and represents a regional<br />

unconformity in the subsurface. Overlying the weathering surface are alluvial sand, silt and<br />

gravel deposits (SU4) rich in organic material. Preliminary analysis of pollen and plant<br />

macrofossils suggests a cold, dry, sub-arctic climate. A possible interglacial assemblage<br />

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was encountered in a single borehole. Multiple radiocarbon age determinations yield ages<br />

range between >52 801 and 37 850 14 C yr BP. Distal bioturbated glaciolacustrine silt and<br />

clay rhythmites passing upward into glacier-influenced rhythmites with interbedded sand<br />

packages (SU5) drape the underlying deposits. This unit is composed of up to 3, possibly<br />

correlatable, coarsening-upward successions up to 120 m thick. In places, there is abundant<br />

ice-rafted debris and sedimentary structures are intensely deformed by subaquatic<br />

slumping. Radiocarbon age determinations bracket SU5 between 37 850 and less than 28<br />

060 14 C yr BP. The stratigraphy is erosively overlain by Late Wisconsin Newmarket Till.<br />

The aforementioned succession is interpreted to record glacial advance during or prior<br />

to the Illinois Episode (SU 1-3) followed by lengthy non-glacial conditions (Sangamon-<br />

Early Wisconsin; SU4). The sharp transition from SU4 to SU5 records dramatic rises in<br />

regional base levels to accommodate deposition of SU5 prior to overriding by glacier ice<br />

during the Late Wisconsin. This succession is comparable to classic ‘type sections’ of Wisconsin<br />

deposits exposed along the Scarborough bluffs.<br />

Sands in SU5 represent significant local to sub-regional aquifers for domestic water supply.<br />

SU4 deposits host significant amounts of groundwater, but commonly contain high levels<br />

of methane and display poor overall water quality. Local coarse-grained units within the<br />

lower glacial complex (SU1-3) host water suitable for domestic supply. Thick regional<br />

aquitard units confine these water-bearing units except along the flanks of large surface<br />

valley features where these strata are exposed.<br />

288 - Geological and hydrogeological models of the ‘Yonge Street’<br />

aquifer, south-central Ontario.<br />

R. Gerber & S. Holysh<br />

Oak Ridges Moraine Hydrogeology Program, Toronto, Ontario, Canada<br />

H.A.J. Russell & D.R Sharpe<br />

Geological Survey of Canada, Ottawa, Ontario, Canada<br />

In the Aurora, Newmarket and Queensville areas of the Greater Toronto Area, south-central<br />

Ontario, municipal water supply is obtained from the ‘Yonge Street aquifer’ (YSA), an informal<br />

name long used to describe relatively deep sand and gravel deposits. These deposits were<br />

previously described as discontinuous, perhaps channelized and possibly associated with buried<br />

bedrock valleys, largely interpreted from data at a few municipal well fields. Despite much<br />

historical and recent geological and hydrogeological work, including numerical groundwater<br />

flow modelling, the fundamental geological and hydrogeological framework (i.e. conceptual<br />

model) for the YSA has not been clearly developed and documented.<br />

Based on high-quality geophysical and geological data (seismic profiles, continuously–<br />

cored, sedimentologically-logged boreholes, downhole geophysics, geological mapping<br />

and 3-D modeling) revised conceptual geological and hydrogeological models of the area<br />

are presented. The data reveal a sedimentary succession (e.g., ~140 m thickness at Aurora)<br />

that is truncated by a number of erosional unconformities characterized by deeply incised<br />

channels, locally extending to bedrock, with a ~NS to NE-SW orientation, both beneath<br />

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and above the regional Newmarket Till stratigraphic marker. Channels may occur stratigraphically<br />

stacked and nested with Newmarket Till locally filling depressions. Core and<br />

seismic data permit identification of channelized Thorncliffe Fm. eroded into older sand<br />

and mud Scarborough Fm. equivalents. The Thorncliffe Fm. consists of fining upward<br />

transitions from coarse gravel, to sand, to rhythmically bedded mud interpreted to be deposited<br />

within a channel-esker-subaqueous fan complex. The YSA aquifer is one component<br />

of a system of similar deposits recognized across the region beneath drumlinized<br />

Newmarket Till.<br />

The accompanying hydrogeological model benefits from a strong conceptual understanding<br />

of vertical and lateral facies changes (and connection to older aquifers) in the Thorncliffe<br />

Fm. depositional model. The subaqueous fan gravel-sand-mud, fining-upward facies<br />

succession provides a capping aquitard to YSA, in addition to the overlying Newmarket<br />

Till aquitard. Lateral coarse to fine facies transitions are very rapid perpendicular to paleoflow<br />

and explain relatively low-yield wells drilled near YSA municipal wells. Facies transitions<br />

are much longer along paleoflow, as supported by pumping tests in a similar aquifer<br />

system north of Markham which have high-yield hydraulic connections of ~1-10 kms.<br />

The conceptual models documented in this paper are critical to guiding groundwater exploration<br />

and management. Paramount to improved knowledge is collection of high-quality<br />

subsurface data (including hydraulic data) that aids in developing a geological framework<br />

that represents the sedimentary system of the basin and its internal flow system.<br />

177 - Hydrostratigraphy of the Interlobate Orangeville Moraine,<br />

Southwestern Ontario, Canada<br />

A.K. Burt<br />

Ontario Geological Survey, Sudbury, Ontario, Canada<br />

The Ontario Geological Survey is undertaking regional scale 3-D hydrostratigraphic mapping<br />

of glacial sediments in select areas of Southern Ontario to provide geoscience information for<br />

the identification, protection and sustainable use of the provincial groundwater resource. The<br />

Orangeville moraine 3-D project area, encompassing 1550 km 2 extending from north of the<br />

Waterloo moraine to the Niagara Escarpment, is centred on the Late Wisconsinan interlobate<br />

zone. A series of 43 continuously cored boreholes, ground gravity surveys and legacy datasets<br />

have been used to map the bedrock surface and overlying Quaternary sediments.<br />

The southwest-dipping Paleozoic bedrock surface is characterized by deep re-entrant buried-bedrock<br />

valleys that extend from the Niagara Escarpment and a series of shallower<br />

generally northward trending buried-bedrock valleys best delineated in the data-rich<br />

southern portion of the area. Bedrock and contact aquifers consisting of stratified sediments<br />

and highly weathered bedrock are primary targets for municipal and domestic wells<br />

within this region.<br />

Pre-Canning tills, Canning drift and localized coarse-textured stratified sediments, likely<br />

deposited during ice retreat, are concentrated in the western and central portions of the<br />

area and in protected locations such as buried-bedrock valleys. The uppermost stratified<br />

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deposits form a locally significant aquifer in the west central part of the region and an<br />

associated organic-rich alluvial deposit was dated at >50 ka BP.<br />

The main Late Wisconsinan Nissouri Phase Catfish Creek Till forms a key aquitard across<br />

the region. The till is an important stratigraphic marker in the northwestern and central<br />

portions of the area, but is not easily distinguished from later deposits in the southeast. Erie<br />

Phase aquifers, including Orangeville moraine glaciofluvial and subaquatic fan sediments,<br />

and fine-textured glaciolacustrine and diamicton aquitards were deposited during and following<br />

the break-up of Catfish Creek ice. Port Bruce Phase Tavistock, upper Maryhill<br />

and Port Stanley and upper sandy tills, deposited during lobate ice advances from the<br />

northwest, southeast and northeast, respectively form the upper aquitards across much of<br />

the region. Although aquifers within coarse-textured Orangeville moraine sediments and<br />

surface outwash deposits are exploited locally, their key role is for groundwater recharge.<br />

In the far southeast of the region, Mackinaw Phase Wentworth Till and debris flows form<br />

the Paris moraine and define the maximum extent of the Erie–Ontario ice lobe during this<br />

ice advance. Closed depressions within the granular deposits of the Paris moraine facilitates<br />

recharge ensuring a healthy groundwater flow system at the head of three watersheds.<br />

308 - Origin and Sedimentological Context of Large Sand and<br />

Gravel Aquifers – Belleville, Trenton and Brighton Areas<br />

George Gorrell<br />

BGC Engineering Inc.<br />

Numerous large, underfit valleys, which are oriented northeast to southwest and east to west,<br />

traverse the area from Belleville to Brighton. Large to moderately sized glaciofluvial deposits<br />

are found within some of these valleys. Geological mapping and site investigations in the<br />

last 10 years have determined that the thickness and lateral extent of the gravel deposits are<br />

significantly larger than was previously believed. Drilling and other site investigations which<br />

include seismic studies have found that the deposits, in many cases, are on the order of 60 m<br />

or more thick, rather than the 10 to 20 m previously believed, and that the sand and gravel is<br />

frequently buried and/or extends laterally to the uplands adjacent to the valleys. The deposits<br />

have been found to either encompass the majority of the upland and are buried by a veneer<br />

of till or are buried in wide deep channels that dissect the upland.<br />

The deposits have significant value for both the groundwater and the aggregate resource.<br />

The underlying Lindsay and Verulam bedrock formations in the area are notoriously poor<br />

aquifers, both for their low to negligible yield and their natural water quality. By contrast the<br />

surficial aquifers can yield quantities capable of supporting whole communities. Furthermore,<br />

since the Oak Ridges Moraine was designated an ecologically important geological landform,<br />

development upon the moraine has been severely restricted. Commercial interests such<br />

as bottled water companies, and public interests such as communities seeking a communal<br />

water supply, compete with aggregate operators for access to the resource. This has resulted in<br />

increased concern over conflicting land-use issues, particularly in the Belleville, Trenton and<br />

Brighton areas which are some of the more intensive development areas.<br />

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Agricultural Impacts on Groundwater 1<br />

Wednesday, October 28, 15:20 – 17:00<br />

Chair: Cathy Ryan<br />

Room: Strauss<br />

155 - Addressing groundwater nitrate contamination associated<br />

with intensive agricultural production systems: The Abbotsford-<br />

Sumas Aquifer case study<br />

Bernie J. Zebarth<br />

Potato Research Centre, Agriculture and Agri-Food Canada, Fredericton, New Brunswick,<br />

Canada<br />

M. Cathryn Ryan<br />

Geoscience, University of Calgary, Calgary, Alberta, Canada<br />

Gwyn Graham<br />

Pacific & Yukon Region, Environment Canada, Vancouver, British Columbia, Canada<br />

Tom A. Forge & Denise Neilsen<br />

Pacific Agri-Food Research Centre, Agriculture and Agri-Food Canada, Summerland,<br />

British Columbia, Canada<br />

The Abbotsford-Sumas Aquifer is arguably the most studied case in Canada of groundwater<br />

nitrate contamination associated with agricultural production. Underlying some of the<br />

most productive agricultural land in Canada, this highly vulnerable trans-boundary aquifer<br />

provides a unique case study on the opportunities and challenges of addressing water quality<br />

issues. A groundwater monitoring program initiated in the early 1990s has been important<br />

in tracking spatial and temporal variation in groundwater nitrate concentration. However,<br />

small land parcels with spatially and temporally variable land use and management practices,<br />

and sub-horizontal flow in this highly permeable sand and gravel aquifer, make it difficult<br />

to relate groundwater monitoring results to specific agricultural practices. Isotopic and nitrogen<br />

budget approaches pointed to the historical over-application of N relative to crop<br />

requirement (primarily as manure used to increase soil organic matter during replanting but<br />

also as a nutrient source during production). Despite changes in agricultural practices, and<br />

programs aimed at raising grower awareness, no appreciable change in average groundwater<br />

nitrate concentration has occurred over the monitoring period. On individual land parcels,<br />

nitrate contamination may be reduced through development and adoption of an integrated<br />

suite of BMPs to improve N fertilization, irrigation and alley vegetation management, and<br />

in particular to eliminate application of any organic soil amendment such as untreated manure<br />

in which the N has not been stabilized (e.g., by composting). However, the substantial<br />

N imbalance on a regional scale, and the lack of an effective on-going consultative process<br />

among stakeholders, remain major barriers to the development, demonstration and adoption<br />

of BMPs. The lack of an on-going consultative process among stakeholders, the lack of a<br />

concerted research and development effort conducted in collaboration with growers, and the<br />

lack of objective metrics of the efficacy and adoption of BMPs, remains a major barrier to the<br />

development, demonstration and adoption of BMPs.<br />

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241 - Predicting the impact of surface sources on an aquifer: The<br />

role of dispersion<br />

Michael Frind 1 , Marcelo Sousa 1 , John Molson 2 , Emil Frind 1 & David Rudolph 1<br />

1<br />

University of Waterloo, Waterloo, Ontario, Canada<br />

2<br />

Université Laval, Québec City, Québec, Canada<br />

Predicting the impact of contamination sources or BMPs (Beneficial Management<br />

Practices) on aquifer systems in agricultural areas frequently involves three-dimensional<br />

groundwater flow/transport modelling. Most transport models are based on the standard<br />

advection-dispersion equation, with controlling parameters being one longitudinal<br />

and two transverse dispersivities, horizontal and vertical. The longitudinal dispersivity is<br />

generally chosen in relation to the aquifer length scale on the assumptions that dispersion<br />

is related to travel distance and that flow is predominantly horizontal. This poses a<br />

problem if the system includes a vadose zone where flow is predominantly vertical and<br />

highly transient, and where aquifer-scale dispersivities would not be appropriate. Thus,<br />

a dilemma can arise in the choice of the appropriate longitudinal dispersivity under the<br />

standard dispersion formulation. A better way is to apply a new dispersion formulation<br />

that is based on two longitudinal dispersivities, horizontal and vertical, in addition to two<br />

transverse dispersivities, also horizontal and vertical. This approach was first proposed by<br />

Lichtner et al. (2002) but has not seen much use since first publication. We show that for<br />

multilayer systems, the alternative approach will give more realistic results compared to<br />

the conventional approach with a single aquifer-scale longitudinal dispersivity, which can<br />

under certain conditions lead to a significant underestimation of travel time. The practical<br />

significance of this phenomenon in an agricultural context lies in the predictive accuracy<br />

of BMP impact assessments for agricultural areas. It is therefore imperative in predictive<br />

modelling to use an appropriate dispersion model with reasonable dispersivity values.<br />

206 - Trends of nitrate concentrations in groundwater for variable<br />

geological settings in agricultural watersheds<br />

Nishant Mistry, Jana Levison & Beth Parker<br />

School of Engineering – University of Guelph, Guelph, Ontario, Canada<br />

Ralph C. Martin<br />

Plant Agriculture – University of Guelph, Guelph, Ontario, Canada<br />

Ramon Aravena<br />

Earth and Environmental Sciences – University of Waterloo, Ontario, Canada<br />

Shoaib Saleem, Elisha Persaud & Scott Gardener<br />

School of Engineering – University of Guelph, Guelph, Ontario, Canada<br />

Groundwater is the main source of drinking water for rural communities and many urban<br />

cities surrounded by agricultural fields in Ontario. Intensification of agriculture in recent<br />

years combined with climatic changes (including extreme weather events) pose threats to<br />

groundwater quality. Over application of fertilizers can result in leaching of excess nutrients<br />

below the root zone to aquifers. Therefore, a comprehensive understanding of evolving<br />

cropping systems and their potential impacts on groundwater quality in various geological<br />

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conditions is necessary to ensure rural water supplies are protected for agricultural and<br />

potable water uses. Groundwater quality was investigated bimonthly (every two months)<br />

starting in June 2014 in different hydrogeological settings (fractured sedimentary bedrock<br />

aquifers with thin overburden, sedimentary bedrock aquifers with thicker overburden, and<br />

sandy aquifers) under different agricultural land-uses. The field data were collected from<br />

over twenty groundwater monitoring locations in southern Ontario (Region of Halton,<br />

City of Guelph, and Norfolk County). The collected groundwater samples were analyzed<br />

for various field parameters (pH, conductivity, temperature, dissolved oxygen, redox potential)<br />

and nitrate, nitrite, chloride, alkalinity, sulfate, dissolved organic carbon, dissolved<br />

elements, total iodine, iodide and isotopes of hydrogen, oxygen and nitrogen (N).<br />

Observed nitrate concentrations at the three sites range from 0.1 to 24 mg/L. Time series<br />

of nitrate concentrations are used to examine the nitrate response in various aquifer units<br />

over time. Isotopic fingerprinting of nitrate was used to determine source of nitrogen in<br />

groundwater (that is, manure/septic or synthetic fertilizer). Other geochemistry data was<br />

used to interpret the age of groundwater, and to understand various mechanisms affecting<br />

the various transport mechanisms of nitrate in groundwater. Of the three studied locations,<br />

the preliminary results indicate that overburden wells located in Guelph are most vulnerable<br />

to nitrate contamination. Certain wells in sandy plain aquifers in Norfolk County displayed<br />

heterogeneous geochemical characteristics, within the same aquifer unit. Local flow<br />

systems and land use patterns can influence the nitrate behaviour in groundwater. The data<br />

will be collected bimonthly until April 2016 to examine temporal term trends of nitrate in<br />

groundwater in the three diverse hydrogeological settings. The field data will feed into a<br />

numerical groundwater modelling effort that will be conducted to examine the impacts of<br />

variable land use and climate stressors on groundwater quality. The results of this research<br />

can be applied by relevant provincial ministries (MOECC, OMAFRA) and local water<br />

managers for improved source water protection in rural locations.<br />

112 - Implementing Source Water Protection – Developing a Tool<br />

to Support Site-Specific Risk Management Planning<br />

Hugh C. Simpson<br />

Ontario Ministry of Agriculture, Food and Rural Affairs, Guelph, Ontario, Canada & School<br />

of Environmental Design and Rural Development, University of Guelph, Ontario, Canada<br />

& Water Policy and Governance Group, University of Waterloo, Ontario, Canada<br />

John Fitzgibbon<br />

School of Environmental Design and Rural Development, University of Guelph, Ontario,<br />

Canada & Ontario Farm Environmental Coalition, Guelph, Ontario, Canada<br />

Charles Lalonde<br />

CJ Agren Consulting Inc., Guelph, Ontario, Canada<br />

James P. Myslik<br />

JPM Consulting, Guelph, Ontario, Canada<br />

Source water protection is the first of a five-part multi-barrier approach for municipal<br />

drinking water supplies. Source Protection Planning is an approach to source water pro-<br />

70 IAH-CNC 2015 WATERLOO CONFERENCE


tection that is being implemented in Ontario under the authority of the Clean Water Act,<br />

2006. Central to this approach is the management of water quality and quantity threats<br />

posed by land use activities adjacent to municipal drinking water sources. One policy option<br />

being advanced is the negotiation of site-specific Risk Management Plans (RMPS)<br />

between local Risk Management Officials (RMO) and individual landowners that will<br />

stipulate measures that must be implemented to mitigate identified threats.<br />

A critical problem associated with the negotiation of RMPs is what approach will be used<br />

when determining their format and content. One option is the traditional expert-driven<br />

approach, where the regulator determines risk management requirements and then informs<br />

the landowner how and when they will be implemented. Unfortunately, this approach<br />

is ill-suited for addressing complex environmental problems such as protecting and<br />

managing groundwater resources.<br />

An alternative are collaborative approaches to decision-making, where the regulator is part<br />

of a risk management process in which outcomes are discussed and requirements are negotiated.<br />

Collaborative approaches can provide a forum for integrating different types of expert<br />

science, local knowledge, and community beliefs and values. This can assist regulators<br />

who may have little or no knowledge of the science concerning a complex environmental<br />

problem, and the effectiveness and relative cost or operational considerations associated<br />

with risk management alternatives. As a result, collaborative approaches are well suited for<br />

helping RMOs to negotiate RMPs that will protect and manage groundwater resources.<br />

The agricultural community has had substantial involvement with collaborative approaches<br />

to protecting and managing groundwater resources that are critical for environmentally<br />

and economically sustainable farm operations. A key role has been educating regulators<br />

concerning the complexities of environmental management concerning activities that<br />

operate in an open environment and must respond to the changing conditions of that<br />

environment. This paper describes the development of a Farm Source Water Protection<br />

Plan (FSWPP) framework and workbook developed by the Ontario Farm Environmental<br />

Coalition. The FSWPP provides a tool to help farmers to identify on-farm risk management<br />

measures, and serve as the basis for negotiating RMPs. Conversely, the FSWPP can<br />

provide the RMO with an inventory of risk reduction measures that could be considered<br />

for the RMP and guidance concerning appropriate levels of risk management for a particular<br />

farm operation.<br />

188 - Long term assessment of BMPs impact on nitrate load at<br />

the Thornton Well Field using RZWQM<br />

Sara Esmaeili & Neil R. Thomson<br />

Department of Civil and Environmental Engineering, University of Waterloo, Waterloo,<br />

Ontario, Canada<br />

David L. Rudolph<br />

Department of Earth and Environmental Sciences, University of Waterloo, Waterloo,<br />

Ontario, Canada<br />

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Faced with increasing nitrate concentration in the Woodstock municipal supply wells (located<br />

in Ontario, Canada), mandatory agricultural best management practices (BMPs) were<br />

implemented in a farmland located within the capture zone in 2003 to reduce nitrate leaching.<br />

Early field investigations suggest that the impact of the BMPs on nitrate leaching was<br />

gradual and not consistent across the capture zone as a result of the different soil stratigraphy,<br />

and current and historical agricultural management practices. In this study, the long-term<br />

(i.e., over 10 years) reduction of nitrate load to the groundwater as a result of BMP implementation<br />

was simulated for different locations within the capture zone. These locations<br />

represent the most dominant cropping practices within the farmland, and each has distinctive<br />

geologic characteristics. To adapt the model to the field conditions, selected soil hydraulic,<br />

organic matter and crop growth parameters were calibrated using a heuristic optimization algorithm.<br />

The simulation results indicated that the long-term impact of the BMPs on nitrate<br />

leaching was different at various locations and ranged from a 54% reduction to a 9% increase<br />

over the 10-year period. Post-BMP annual nitrate leaching, in some years, was shown to<br />

be similar or even greater than the loading prior to the implementation of the BMPs. This<br />

finding was consistent with field observations and implies that BMP effectiveness needs to<br />

be averaged over a long period of time and single field measurements can be misleading. No<br />

relationship was found between soil nitrate content and nitrate leaching, suggesting that soil<br />

nitrate content should not be used as a BMP effectiveness index. The anticipated effects of<br />

two alternative BMP scenarios on nitrogen balance (yield, loss and storage) from a farmland<br />

under conventional agricultural practice will also be discussed.<br />

Regional Groundwater Systems 2<br />

Wednesday, October 28, 15:20 – 17:00<br />

Chair: Tom Gleeson<br />

Room: Wagner<br />

176 - A Continental-Scale Groundwater Flow Model Calibrated to<br />

Groundwater Age<br />

Mark Ranjram<br />

Department of Civil Engineering – McGill University, Montreal, QC, Canada<br />

Tom Gleeson<br />

Department of Civil Engineering – University of Victoria, Victoria, BC, Canada<br />

Throughout its distinguished history, the science of hydrogeology has developed elegant<br />

models of site- and local-scale groundwater flow. Although the work of Tóth and others<br />

provide an elegant theoretical framework for regional-scale groundwater flow, more complex<br />

methods are needed to account for regional heterogeneities and limited observational<br />

data at regional scales. These problems are further exacerbated when considering groundwater<br />

flow at continental scales. In this study, we develop a groundwater flow and transport<br />

model beneath the continental United States and relate our current continental-scale<br />

permeability, porosity, dispersion, and recharge estimates to observed values of water table<br />

72 IAH-CNC 2015 WATERLOO CONFERENCE


depth and, for the first time, tracer-based estimates of groundwater age. The results of this<br />

study provide higher quality input data for future continental-scale research, while also<br />

demonstrating the feasibility of groundwater age data as a model calibration parameter.<br />

229 - Investigating deep basalt groundwater supplies in the<br />

Interior Plateau region of British Columbia – District of 100 Mile<br />

House, B.C.<br />

Douglas Geller & Ryan Rhodes<br />

Western Water Associates Ltd. Vernon, British Columbia, Canada<br />

David Underwood<br />

TRUE Consulting Group, Kamloops, British Columbia, Canada<br />

Philip Strain<br />

District of 100 Mile House, 100 Mile House, British Columbia, Canada<br />

Located in the Interior Plateau region of British Columbia along the historic Cariboo<br />

Gold Rush trail, the District of 100 Mile House (pop. Approximately 2,500) presently obtains<br />

the majority of its water supply needs from Bridge Creek, augmented by groundwater<br />

from a single 175 metre deep well installed in 2004. In 2013, grant funding was awarded<br />

to complete comprehensive studies to guide long term water system planning. In light of<br />

evolving water treatment requirements and concerns over the security of the Bridge Creek<br />

source driven by land use and climate changes, increasing reliance on groundwater resources<br />

was identified as the preferred long-term water supply option. Before moving forward<br />

with this plan to make groundwater a primary water source for the community, detailed<br />

hydrogeological investigations were carried out. These included: completing a source water<br />

assessment, confirming aquifer and well capacity, assessing pathogen risks, assessing<br />

groundwater quality, Aquifer Storage and Recovery feasibility, and determining feasibility<br />

of securing additional groundwater supplies from the deep regional basalt aquifer system.<br />

The aquifer sourced by the District of 100 Mile House is somewhat unique in B.C.. Analogous<br />

to the prolific Columbia River Basalts of the Northwestern United States, the aquifer<br />

forms in layered lava flows and is highly productive and characterized by good water<br />

quality. The aquifer is also secure: deep, confined and thus isolated from the effects of land<br />

use at the surface, the groundwater resource is not at risk of containing pathogens or under<br />

influence from surface water. Although the aquifer is regional in extent, underlying thousands<br />

of square kilometres, evidence from the few wells that penetrate deeply into the basalt<br />

section suggest highly variable aquifer properties, the explanation for which is provided in<br />

the hydrogeological conceptual model developed for this project. The hydrogeological conceptual<br />

model borrows from the more extensively studied Columbia River Basalt Group of<br />

the northwestern United States. Technical topics addressed in the presentation include the<br />

relatively elevated total organic carbon present in the deep aquifer, the implications of high<br />

aquifer transmissivity and relatively low well specific capacity on well field designs, regional<br />

groundwater recharge mechanisms, and the potential for expanded use of the resource for<br />

municipal, industrial and agricultural supply including the potential application of Aquifer<br />

Storage and Recovery.<br />

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This paper outlines the District’s plan for transition to increased reliance on groundwater,<br />

including the implementation of microbiological manganese removal, additional source development,<br />

and water treatment requirements in the context of the recently released Drinking<br />

Water Treatment Objectives for Groundwater Supplies in B.C. The deep basalt aquifer will also<br />

be discussed in the context of basalt hydrogeology fundamentals, as it is a little known but<br />

regionally extensive aquifer system that is not heavily developed in Interior of B.C.<br />

245 - Regional groundwater flow in the inter-till and buried-valley<br />

aquifers, southwestern Manitoba<br />

Hinton, M.J., Logan, C.E., Oldenborger, G.A. & Pugin, A.J.-M.<br />

Geological Survey of Canada, Natural Resources Canada, Ottawa, Ontario, Canada<br />

Inter-till and buried-valley aquifers are among the main sources of groundwater in the<br />

Prairies. The Spiritwood buried-valley aquifer system extends from Manitoba and across<br />

North Dakota where it has been a significant source for groundwater supply for decades<br />

yet its resource potential in Manitoba has not been evaluated. The Geological Survey of<br />

Canada (GSC) has been studying the regional geology and hydrogeology of the Spiritwood<br />

buried-valley aquifer in southwestern Manitoba. Helicopter time domain electromagnetic<br />

(HTEM) and high resolution seismic reflection (HRSR) surveys permitted<br />

detailed mapping of inter-till and buried-valley aquifers within the study area. The main<br />

buried valley is a broad 10-15 km wide and 60-70 m deep valley cut into Cretaceous Pierre<br />

shale. A series of nested channels of different age, origin, dimensions and orientations<br />

are cut into bedrock and within the sand/silt till. Where these channels are filled with<br />

coarse sediment, they form aquifers: deep buried-valley aquifers (60-100 mbgs) incised<br />

into shale below the base of the broad buried valley, and inter-till aquifers within the till.<br />

A 3D numerical geological model of the regional bedrock surface and sediments was developed,<br />

using Leapfrog Hydro geological modelling software. A significant feature of<br />

the geological model is that the nested channels and fans that form inter-till aquifers together<br />

with the fractured bedrock surface may provide more permeable pathways to deep<br />

buried-valley aquifers. Another significant finding is the discovery that the buried-valley<br />

aquifer outcrops in incised surface valleys where sustained baseflow was measured during<br />

a period of extended drought.<br />

Regional groundwater flow generally follows topography but is perpendicular to the orientation<br />

of the main buried valley. However, flow also occurs along the deep buried valley<br />

which acts as a regional drain towards the incised surface valleys. Both hydraulic and<br />

HTEM results suggest that there are no transverse hydraulic boundaries within the deep<br />

buried-valley aquifer. A steady state finite element numerical groundwater model has been<br />

developed from the geological model to: i) assess the different flow pathways within the<br />

inter-till and deep buried-valley aquifers, and ii) constrain the estimates of groundwater<br />

flow. The numerical flow model replicates the regional flow patterns, discharge zones and<br />

the groundwater divide in the deep buried-valley aquifer. Results to date suggest that,<br />

despite the presence of preferred hydraulic pathways, natural replenishment of the deep<br />

buried-valley aquifer is small. © Her Majesty the Queen in right of Canada 2015.<br />

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318 - Glacial retreat effects and transport in the Milk River<br />

Transboundary Aquifer<br />

Alfonso Rivera 1 , André Guy Tranquille Temgoua 1 & Marie-Amélie Pétré 1, 2<br />

1<br />

Geological Survey of Canada, Québec City, Québec, Canada<br />

2<br />

INRS-ETE, Québec City, Québec, Canada<br />

René Lefebvre<br />

INRS-ETE, Québec, Canada<br />

Many hypotheses have been formulated regarding the study of the Milk River Transboundary<br />

Aquifer (MRTA) straddling the international Canada-USA border (Province<br />

of Alberta – State of Montana). These include groundwater flow across aquifers and<br />

aquitards, groundwater ages, GW/SW interactions, recharge zones, transboundary fluxes,<br />

discharge mechanisms, erosional rebound, sub-hydrostatic pressures, vertical macroscopic<br />

dispersion across layers, and others.<br />

This presentation tries to clarify two of the adopted assumptions in what is a more complete<br />

and unified three-dimensional ongoing study of the MRTA (Pétré et al., 2015a,<br />

2015b). Based on one-dimensional solutions of the hydraulic diffusivity and dispersion<br />

equations, we analyze scenarios on the effect of pore pressure dissipation from the weight<br />

of glaciers and the potential dispersive flow between the aquifer (MRTA) layer and aquitards<br />

located above and below the aquifer.<br />

Scoping calculations to evaluate pressure release as a function of time, after the last glaciation<br />

in the Milk River region, are performed using the hydrostatic rebound formulation<br />

of Terzaghi in 1D. Conceptually, the presence of glaciers can induce fluid pressure changes<br />

in the rock matrix attributed to geomechanical factors due to glacial retreat. Furthermore,<br />

stress-induced pressure changes may cause modifications in Darcy fluxes during the loading<br />

and unloading of glaciers generating a long-term transient flow occurring in the low<br />

permeable layers above and below the MRTA.<br />

By observing the enrichment in δD, δ 18 O, and Cl - concentration down-gradient in the<br />

Milk River aquifer, some researchers have proposed that dispersion would be the controlling<br />

process because the spatial distribution of several chemical parameters is controlled<br />

by aquifer transmissivity. They call it megascopic (or macroscopic) dispersion. They argue<br />

that this is caused by large formational heterogeneities: The Milk River aquifer receives<br />

inflow of more saline, isotopically heavier water from the shale unit immediately below<br />

the aquifer (Colorado formation). In order for this 1D vertical transport to take place,<br />

two conditions must be met: a) a hydraulic vertical gradient between the MR aquifer and<br />

the aquitard must exist; and b) a concentration gradient between the aquitard and the<br />

MR aquifer must exist so that concentration is higher in the aquitards and lower in the<br />

aquifer. In this partial study, we consider a simple 1-D vertical case where C(z,t) is to be<br />

determined. We analyzed two cases: 1) vertical transport between the Milk River aquifer<br />

and the Colorado aquitard; and 2) vertical transport between the Milk River aquifer and<br />

the Pakowki aquitard.<br />

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219 - Current results and outcomes of the regional groundwater<br />

knowledge acquisition program in Québec<br />

Alain Rouleau 1 , Thomas Buffin-Bélanger 2 , Stéphane Campeau 3 , Gwénaëlle<br />

Chaillou 2 , Romain Chesnaux 1 , Vincent Cloutier 4 , Marie Larocque 5 , René Lefebvre 6 ,<br />

John Molson 7 & Éric Rosa 4<br />

1<br />

Université du Québec à Chicoutimi (UQAC), Saguenay, Québec, Canada<br />

2<br />

Université du Québec à Rimouski (UQAR), Rimouski, Québec, Canada<br />

3<br />

Université du Québec à Trois-Rivières (UQTR), Trois-Rivières, Québec, Canada<br />

4<br />

Université du Québec en Abitibi-Témiscamingue (UQAT), Amos, Québec, Canada<br />

5<br />

Université du Québec à Montréal (UQAM), Montréal, Québec, Canada<br />

6<br />

Institut national de la recherche scientifique, centre Eau, Terre et Environnement<br />

(INRS-ETE), Québec City, Québec, Canada<br />

7<br />

Université Laval, Québec City, Québec, Canada<br />

We present a summary of the current results and outcomes of the Groundwater Knowledge<br />

Acquisition Program (Programme d’acquisition des connaissances sur les eaux souterraines<br />

– PACES) in Quebec, initiated in 2008 by the Quebec Ministry of the Environment<br />

(Ministère du Développement durable, de l’Environnement et de la Lutte contre les changements<br />

climatiques – MDDELCC), in order to provide a sound basis for groundwater protection<br />

and management over the entire municipal territory of the Province. PACES projects are<br />

carried out by universities in collaboration with regional authorities and stakeholders, such<br />

as Regional Conferences of Elected Officials (Conférences régionale des élus – CRÉ), Regional<br />

County Municipalities (Municipalités régionales de comté – MRC), and Regional<br />

Watershed Organizations (Organismes de bassin versant - OBV). PACES projects involve<br />

an exhaustive inventory of preexisting data and the acquisition of complementary field and<br />

laboratory data. Deliverable products include a large number of maps (1:100 000), reports<br />

and important databases. Thirteen regional PACES projects have been completed between<br />

2009 and 2015, with a total funding of 13 M$ from MDDELCC and over 3.5 M$ from a<br />

number of regional partners, including 9 CRÉs and 34 MRCs. These projects cover a total<br />

area of approximately 87 000 km 2 , with a population of over 3 M people. Numerous highly<br />

qualified persons have been trained as part of the PACES projects, conducting research,<br />

including laboratory and field activities, related to data acquisition and to specific regional<br />

groundwater problems. Thematic research projects were also carried out as part of a targeted<br />

research partnership program on groundwater from the Fonds de recherche du Québec<br />

(FRQ). After six years the PACES program has covered approximately 70% of the municipal<br />

territory of Quebec with sound data on groundwater and aquifer systems. Important<br />

outcomes include a significant increase in knowledge and data availability on groundwater,<br />

strengthening of inter-university research activities through the Réseau québecois sur les eaux<br />

souterraines (RQES), development of partnerships with many stakeholders on groundwater,<br />

and impetus for further research projects. A number of related challenges have surfaced<br />

during the PACES projects, particularly on the efficient transfer and the proper use of<br />

hydrogeological data in land use planning, for a better protection and sustainable management<br />

of groundwater.<br />

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Flow and Transport in Fractured Rock<br />

Wednesday, October 28, 15:20 – 17:00<br />

Chair: Kent Novakowski<br />

Room: Schubert<br />

300 - Hydrogeology and sequence stratigraphy correlations<br />

used to inform a regional scale groundwater flow model for<br />

sedimentary rock<br />

J.R. Meyer & B.L. Parker<br />

G360 Centre for Applied Groundwater Research, School of Engineering, University of<br />

Guelph, Guelph, Ontario, Canada<br />

E. Arnaud<br />

School of Environmental Sciences, University of Guelph, Guelph, Ontario, Canada<br />

A.C. Runkel<br />

Minnesota Geological Survey, St. Paul, Minnesota, USA<br />

L. Weaver, S.G. Shikaze & D.G. Abbey<br />

Matrix Solutions Inc., Breslau, Ontario, Canada<br />

Hydrogeologic units (HGUs) represent our understanding of the 3-D distribution of hydraulic<br />

conductivity contrasts; and therefore, accurate delineation of these units is foundational<br />

to conceptual and numerical models of groundwater flow. In standard practice,<br />

existing lithostratigraphic units are often assumed to be HGUs and are used to guide the<br />

length and position of well screens used to collect hydraulic data. This study describes a<br />

unique approach to HGU delineation that relies on depth discrete and detailed (i.e., high<br />

resolution) profiles of vertical gradient to delineate HGUs for a numerical model needed to<br />

support decision making for a contaminated sedimentary rock site in southern Wisconsin.<br />

Seven hydraulic head profiles obtained from high resolution multilevel systems (average of<br />

3.4 monitoring zones per 10 m) monitoring to depths between 90 and 146 m were used to<br />

determine the three-dimensional distribution, magnitude, and direction of vertical gradients.<br />

When examined along 2 cross sections, each spanning 4 km, these vertical gradient<br />

profiles indicated 11 laterally extensive contrasts in the vertical component of hydraulic<br />

conductivity (K v<br />

); the boundaries of which did not coincide with lithostratigraphic units.<br />

Further investigations revealed that the K v<br />

contrasts were strongly associated with regionally<br />

extensive sequence stratigraphic units (maximum flooding intervals and unconformities)<br />

and this relationship was used to delineate 3-D HGUs for the site scale (16 km 2 ).<br />

Development of the 3-D numerical groundwater flow model required expanding the study<br />

area to 300 km 2 in order to incorporate physically based boundary conditions. There were<br />

over 400 additional boreholes in the model domain, but the data sets for most only included<br />

lithostratigraphic picks. Therefore, the association between the high resolution vertical<br />

gradients and sequence stratigraphic units developed on site were used to create guidelines<br />

regarding the position of the HGUs relative to lithostratigraphic units and HGUs<br />

were picked for the additional boreholes. All HGU picks were then examined along > 30<br />

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cross-sections to look for consistency with regional sequence stratigraphy and other bedrock<br />

mapping studies. Continuous surfaces were then generated from the HGU picks and<br />

used as the framework for the numerical model. This study provides an example of how<br />

high resolution site scale characterization provides the data necessary to calibrate hydraulics<br />

to geologic features resulting in a robust HGU framework and confidence in extending<br />

that framework to the full flow system scale.<br />

292 - Parameter Estimation in a Regional Groundwater Flow<br />

Model to Represent Site-Specific High Resolution Head Profiles<br />

Steven G. Shikaze, Beiyan Zhang & Daron G. Abbey<br />

Matrix Solutions Inc., Breslau, Ontario, Canada<br />

Jessi R. Meyer & Beth L. Parker<br />

G360 Centre for Applied Groundwater Research, School of Engineering, University of<br />

Guelph, , Ontario, Canada<br />

In the 1950s and 60s, over 70,000 L of dense non-aqueous phase liquid (DNAPL) was<br />

released into the subsurface at a site in Wisconsin. In the 1980s, contamination (chlorinated<br />

solvents, BTEX, ketones) was discovered in the bedrock. Groundwater flow through<br />

the source zone has resulted in a dissolved-phase plume that has migrated approximately<br />

3 km downgradient. Remediation activities in the 1990s and 2000s included air sparging,<br />

DNAPL pumping, and hydraulic barrier wells. Over the past 11 years, researchers from<br />

the University of Guelph (UG) have been studying the site. This has included extensive<br />

field operations to understand of the groundwater flow system at the site. UG has collected<br />

high-resolution vertical hydraulic head data at various locations across the site, and this<br />

information has been used to inform an evolving site conceptual model.<br />

Groundwater modelling studies began in 2010 to aid in the understanding of the groundwater<br />

flow regime. A regional scale, three-dimensional groundwater flow model was constructed<br />

in FEFLOW. This model covers an area of approximately 300 km 2 and includes<br />

nearby communities that rely on groundwater water. The model is refined in the area of<br />

interest, which encompasses the plume area (approximately 16 km 2 ). Using the detailed<br />

on-site data as well as the sparser off-site data, the FEFLOW model was constructed<br />

from a site conceptual model that includes 21 model layers (6 overburden and 15 bedrock).<br />

Initial estimates for the hydraulic properties of these layers were based on UG’s hydraulic<br />

testing and detailed examination of borehole logs.<br />

Parameter estimation (PEST) software (Doherty, 2010) has been used in conjunction with<br />

the steady-state groundwater flow model in FEFLOW. PEST was used to adjust the<br />

input parameters (i.e., hydraulic conductivity (K), anisotropy (K h<br />

/K v<br />

), recharge) to obtain a<br />

good match with observed hydraulic heads. Emphasis has been placed on matching UG’s<br />

high-resolution vertical head data on site. Preliminary results suggest that the initial estimates<br />

for the range in K for most model layers need to be wider than the initial estimates.<br />

By expanding the K range in PEST, a better match with the vertical head measurements<br />

was attained. The results from this numerical analysis can be used to inform the site conceptual<br />

model.<br />

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286 - Advances in the Application of Thermal Logging Techniques<br />

for Hydro-physical Characterization of Flow through Fractured<br />

Rock<br />

Peter Pehme, Beth Parker, John Cherry & Jessica Meyer<br />

G360 Centre for Applied Groundwater Research, University of Guelph, Ontario, Canada<br />

Detlef Blohm<br />

Instruments for Geophysics, Brampton, Ontario, Canada<br />

The nuances of changes in the thermal field within the subsurface (i.e. magnitude and orientation<br />

of thermal gradients, irregularities in temperature patterns etc.) are primarily controlled<br />

by groundwater flow. The use of thermal hydro-physical techniques for identifying<br />

groundwater flow in fractured rock is experiencing revitalization as a consequence of both<br />

advances in sensors and synergistic developments of other technologies. Flexible impermeable<br />

liners can be used to restore the ambient groundwater flow conditions that would<br />

have existed without the borehole being present eliminating the distortion of temperature<br />

logs caused by cross-connected flow between fractures and hydrologic units in open boreholes.<br />

The active line source (ALS) technique, wherein the entire length of the static water<br />

column in the lined-hole is heated and high resolution, temperature profiles are repeatedly<br />

measured to observe the dissipation of thermal energy, overcomes the depth limitations<br />

created by homothermic conditions while standardizing the basis for comparison of flow<br />

zones thereby improving characterization of both major and subtle flow zones critical to<br />

understanding contaminant migration and attenuation. More recently four sensors with<br />

resolution approaching 0.001C have been incorporated in the magnetically orientated<br />

thermal vector probe (TVP) to measure the vector components (magnitude and direction)<br />

of the temperature field.<br />

Examples of combining these techniques in sandstone and dolostone environments are<br />

presented. The interpretations identify numerous hydraulically active fractures under both<br />

ambient flow conditions and in response to pumping without a depth related bias. The<br />

broad scale changes in the thermal regime are shown to provide an improved basis for<br />

assessing the relative magnitude and direction of groundwater flow and variations akin<br />

to subdivision into hydrogeologic units (HGUs) based on other data sets such as detailed<br />

head profiles from multi-level systems.<br />

210 - Palaeo-hydrogeological evolution of a fractured-rock aquifer<br />

following the Champlain Sea Transgression in the St. Lawrence<br />

Valley (Québec)<br />

Marc Laurencelle 1 , René Lefebvre 1 , Michel Parent 2 , John Molson 3 & Christine<br />

Rivard 2<br />

1<br />

Institut national de la recherche scientifique, Centre Eau Terre Environnement, Québec City,<br />

Québec, Canada<br />

2<br />

Natural Resources Canada, Geological Survey of Canada (GSC), Québec City, Québec, Canada<br />

3<br />

Université Laval, Department of Geology and Geological Engineering, Québec City,<br />

Québec, Canada<br />

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Surface conditions have changed thoroughly over North America during the last glacial-deglacial<br />

cycle and postglacial time (80-5 ka BP). Our study area, Montérégie Est (~9 000 km 2 ),<br />

was covered by the Laurentide Ice Sheet during ~20 ka, until the isostatically depressed St.<br />

Lawrence Valley became ice-free, by about 13 ka BP. These lowlands were briefly occupied by<br />

Glacial Lake Candona, a large freshwater body that preceded the incursion of marine waters<br />

from the Atlantic Ocean. During the early part of this incursion, known as the Champlain<br />

Sea, the deep water body was strongly stratified, with light meltwater-rich surface waters<br />

overlying dense polyhaline seawater. However, the salinity of Champlain Sea water decreased<br />

rapidly, due to the combined effects of sustained meltwater production and isostatic rebound,<br />

which progressively prevented Atlantic seawater from entering the valley upstream of Quebec<br />

City. As the seawater influx had decreased to a minimum, a lacustrine successor basin,<br />

known as Lake Lampsilis, persisted in the central valley. Subsequently, the drainage system<br />

in the lowlands evolved towards its present-day configuration through continued isostatic<br />

adjustment. Along with those spatio-temporal variations in water level and salinity, silts and<br />

clays had deposited during the glaciolacustrine and glaciomarine episodes. These sediments<br />

formed thick low permeability units that retarded the transfer of salt between the marine water<br />

body and the underlying rock aquifer, but also impeded the later flushing of brackish water<br />

from the aquifer, which still contains salty groundwater of marine origin over 2 200 km 2 .<br />

The main objective of this research is to develop a quantitative reconstitution scenario for<br />

the evolution of groundwater salinity within the Montérégie Est regional aquifer system<br />

following deglaciation. To do so, the palaeo-hydrogeological problem was conceptualized<br />

using time-dependent boundary conditions and material properties, while the regional<br />

fractured-rock aquifer system was idealized as a double-porosity equivalent porous medium<br />

with permeability decreasing with depth. A fully coupled 2D density-dependent flow<br />

and mass transport numerical model was set up to simulate the post-marine migration of<br />

salt along a vertical cross-section within the study area. Modeling first assessed the relative<br />

influence of processes and model parameters. Notably, the impacts of transient storage of<br />

salt and fluid in dead-end fractures, on both solute and age mass transport, were investigated.<br />

Overall, results show that salinization of the aquifer below the Champlain Sea was a<br />

density-driven process, with subsequent desalinization being more efficient where silts and<br />

clays had not formed thick confining units.<br />

213 - Nano-scale Colloid Particles Transport in Variable-aperture<br />

Sandstone Rock Fracture<br />

Ertiana Rrokaj, Pulin K. Mondal & Brent E. Sleep<br />

Department of Civil Engineering – University of Toronto, Toronto, Ontario, Canada<br />

In Canada, many communities and over thirty percent of the population rely exclusively on<br />

groundwater for meeting their water demand. These groundwater resources are prone to contamination<br />

by leaking septic tanks, gasoline storage tanks, and municipal landfills. Fractured<br />

rock aquifers are particularly vulnerable to contamination due to the high conductivity pathways<br />

associated with rock fractures. Previous studies have investigated the transport of contaminants<br />

through volcanic rock aquifers, porous shale saprolite, and clay-rich till bedrock, but very<br />

few studies have investigated colloid particles transport through sandstone fractures.<br />

80 IAH-CNC 2015 WATERLOO CONFERENCE


An experimental investigation is currently being carried out to identity the effect of the physical<br />

and chemical characteristics of a sandstone fracture, such as aperture distribution and<br />

mineral composition, on the transport of virus-sized colloid particles. Transport tests are<br />

being conducted in an artificially fractured sandstone block with negatively charged carboxylate-modified<br />

latex particles of three sizes (20 nm, 100 nm, 500 nm diameter), positively<br />

charged amine-modified particles (50 nm diameter), and a conservative solute (bromide).<br />

The tests are also being performed at two specific discharges (0.35 mm.s-1, and 0.95 mm.s-<br />

1), with solutions of two different total ionic strengths (5 mM, 15 mM), and ionic compositions<br />

(sodium and calcium cations). In addition to the laboratory component, this study<br />

will include the application of a one-dimensional advection-dispersion transport model that<br />

incorporates colloid filtration processes to analyze the experimental results.<br />

The outcome of this study will be the identification of the physical and chemical parameters,<br />

characteristic of sandstone fractures that affect the transport of solute and virus-sized colloid<br />

particles in fractured sandstone. In particular, the study will quantify the effects of matrix diffusion,<br />

and determine the importance of the electrostatic interactions between colloid particles<br />

and the rock surface by performing colloid transport tests under favourable and unfavourable<br />

attachment conditions.<br />

Vadose Zone Hydrogeology<br />

Wednesday, October 28, 15:20 – 17:00<br />

Co-chairs: Ed Cey, Mike Callaghan<br />

Room: Heritage<br />

307 - Implications of thick vadose zone infiltration and a falling<br />

water table for recharge estimations beneath an irrigated field<br />

Randy L. Stotler & Britney S. Katz<br />

Department of Geology, University of Kansas, Lawrence, Kansas, USA<br />

Donald O. Whittemore, James J. Butler, Jr., Greg A. Ludvigson & Jon J. Smith<br />

Kansas Geological Survey, Lawrence, Kansas, USA<br />

Daniel R. Hirmas<br />

Department of Geography, University of Kansas, Lawrence, Kansas, USA<br />

The Ogallala-High Plains aquifer (HPA) is one of the largest aquifers in the world and is<br />

critical for agricultural production. Irrigation has large-scale impacts on the water resources<br />

throughout the HPA, causing steep declines in groundwater levels that are expected<br />

to continue due to extensive groundwater mining. Water-level monitoring and analysis<br />

revealed unexpected increases in water levels for some years in the northwestern Kansas<br />

HPA. This indicated a previously unknown source of recharge to the aquifer, in an area<br />

where water level declines from pre-development exceed 30 m.<br />

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The goal of this research was to obtain a better understanding of the sources and rates of<br />

recharge by investigating the storage and transit time of chemicals through the 65 m thick<br />

unsaturated zone. Water fluxes and chemical transit times were estimated using a chloride<br />

mass balance approach. These data provide evidence that flow through the unsaturated<br />

zone to the aquifer is influenced by many factors including lithology, climate, land conversion,<br />

and irrigation. Climate, and the conversion from grassland to cropland and then<br />

to irrigated agriculture changed vadose zone chemical movement. A thick layer of loess<br />

near the surface significantly restricted downward chemical and fluid movement, impeding<br />

irrigation return flow.<br />

The major geochemical signature of fluid in the portion of the vadose zone below the predevelopment<br />

water level (between 35 and 65 m below ground surface) was virtually identical<br />

to groundwater sampled from nearby wells. This indicates incomplete drainage after<br />

substantial groundwater declines since widespread irrigation began in this region in the<br />

1960s. This was not entirely unexpected given estimates for fluid flux through the upper<br />

35 m of the unsaturated zone were on the order of 500 years. Water-level data indicated a<br />

source of recharge to the aquifer; however, it clearly was not through irrigation return flow.<br />

Although assumptions for common chemical-based techniques for recharge estimation,<br />

such as chloride mass balance, are invalid in the partially dewatered zone, there is an opportunity<br />

to learn more about recharge to the aquifer by further investigating fluid in this<br />

zone. This is because the system has clearly not reached steady state, and groundwater age<br />

estimates collected from below the water table today are originally from deeper flow paths.<br />

Finally, other sources of recharge, such as through depressions, ephemeral stream beds, and<br />

playas need to be studied further.<br />

258 - Applicability of the chloride mass balance method for an<br />

evaluation of the depression-focussed recharge in the Canadian<br />

prairies<br />

Igor Pavlovskii & Masaki Hayashi<br />

Department of Geoscience – University of Calgary, Calgary, Alberta, Canada<br />

The chloride mass balance is a well-established tool for an estimation of the local groundwater<br />

recharge rates in the arid and semi-arid settings. However, some hydrological processes associated<br />

with depression-focussed recharge introduce significant bias into recharge estimates<br />

obtained through the application of this method. Such processes as surface runoff and blowing<br />

snow redistribution alter water and chloride inputs in different topographical positions. The<br />

internally drained depressions are on a receiving end of the lateral water fluxes. In contrast,<br />

uplands are losing water through these processes. As a result, the local groundwater recharge<br />

rate starts to deviate from the apparent recharge rate - one calculated using precipitation and<br />

atmospheric deposition rates as an input function in the chloride mass balance method.<br />

Using simple mass balance model, we will show the magnitude of the under- and overestimation<br />

of the local recharge rates within depressions and on the uplands in the idealised<br />

prairie setting. Additionally, the sensitivity of the apparent and real recharge rate to a variation<br />

in the intensity of the lateral water fluxes is investigated.<br />

82 IAH-CNC 2015 WATERLOO CONFERENCE


The chloride mass balance method is then applied to data collected at three sites in southern<br />

Alberta. All three sites are situated in the north-western fringe of the prairie belt<br />

with two sites falling within the boundaries of the parkland ecoregion and third site being<br />

situated in the grassland ecoregion The instruments deployed on the sites permitted to<br />

quantify intensity of the lateral water fluxes. The chloride concentration data were obtained<br />

from the till samples obtained during groundwater well installation in 2014. As<br />

a result, chloride concentrations in the till coupled with information on the lateral water<br />

fluxes allowed us to estimate recharge rate and to compare it with an apparent recharge rate<br />

to demonstrate the magnitude of the bias in a real setting.<br />

283 - Simulated mechanical compression of regenerated<br />

Sphagnum moss potentially accelerates the return of hydrological<br />

functionality in restored bogs<br />

Colin McCarter & Jonathan Price<br />

University of Waterloo, Waterloo, Ontario, Canada<br />

Returning the ecohydrological function to harvested bog peatlands is critical to restoration;<br />

however, after 10 years the current restoration approach does not achieve this milestone, due<br />

to the capillary barrier formed between the regenerated Sphagnum moss and relatively dense<br />

remnant cutover peat. A greater proportion of large pores was observed in the regenerated<br />

Sphagnum that limited capillary draw from the remnant peat. Increasing the density of small<br />

pores in the regenerated Sphagnum would increase its capillarity and allow greater connection<br />

to the water table, which is situated within the remnant cutover peat. This paper aims to assess<br />

the theoretical implications of compression through modelling increases in volumetric soil<br />

moisture content (θ) and unsaturated hydraulic conductivity (K unsat<br />

), representing an increase<br />

in the abundance of smaller pores. Hydrus-1D, utilizing the van Geuchten-Mualem or Durner<br />

dual porosity equation, was used to simulate the current vadose hydrology of regenerated<br />

Sphagnum, along with an undisturbed analogue as reference simulations. Both K unsat<br />

and θ<br />

were increased by 50 % of the difference between the restored and undisturbed Sphagnum<br />

(~1 order of magnitude in K unsat<br />

and 2 – 5 % in θ) and the Sphagnum height decreased by<br />

50 % to 10 cm to simulate compression. Unlike the undisturbed analogue, the regenerated<br />

Sphagnum had highly non-linear soil water pressure distribution, resulting in limited upward<br />

transfer of water to the surface and meeting the evaporative demand ~28 % of the time (~60 %<br />

for undisturbed). Compression achieved linear soil water pressure distributions, similar to undisturbed,<br />

and a large increase in its ability to meet the evaporative demand (57 %). A 2 order<br />

of magnitude increase in average Sphagnum K unsat<br />

(6.2·10 -5 to 1.8·10 -3 cm hr -1 ) was observed<br />

between the regenerated and compressed models, but was still lower than the Sphagnum<br />

K unsat<br />

of the undisturbed (1.5·10 -1 cm hr -1 ). Furthermore, the simulated compression allowed<br />

the water table (minimum -0.82 m bgs) to be influenced by the Sphagnum moss, unlike the<br />

regenerated Sphagnum that had no influence on water table position. These results indicate<br />

that it is possible to have direct connection from the water table to the surface by decreasing<br />

the average pore size and increasing θ and K unsat<br />

, even when the water table resides within the<br />

remnant cutover peat. Mechanical compression of living Sphagnum moss may be a practical<br />

remedial restoration measure to improve hydrological function.<br />

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277 - Assessing soil water content & temperature under<br />

conventional tillage & no-tillage for drought adaptation<br />

G.Y. Suarez 1 , P. von Bertoldi 2 , D. Rudolph 1 & G. Parkin 2<br />

1<br />

Department of Earth and Environmental Sciences – University of Waterloo, Waterloo,<br />

Ontario, Canada<br />

2<br />

School of Environmental Sciences, University of Guelph, Guelph, Ontario, Canada<br />

Pre-growing season weather forecasts are relatively unreliable and farmers must seek an<br />

alternative measure to inform their land management options in order to reduce the potential<br />

impact of drought on crop yield. A potential approach to minimizing drought impacts<br />

is to use measured or modelled soil water storage and temperature in late spring as<br />

a predictor of future dry soil conditions. This information can then be used to modify the<br />

planting date to reduce the impacts of a subsequent dry growing season and to ensure<br />

optimal temperature conditions for crop growth. Both parameters may be influenced by<br />

the tillage methods adopted on the fields. High resolution (hourly) soil water content and<br />

temperature data collected at a research farm for 11 years within the 0–100 cm depth profiles<br />

under no-till (NT) and conventional fall tillage (CT) practices were used to test the<br />

hypothesis that no-tillage reduces the impact of drought on crop yield by conserving soil<br />

water storage while maintaining optimum soil temperature during the growing season in<br />

comparison to conventional tillage. The field data sets were used in a time series analysis<br />

with a forecasting model to understand field data behaviour and predict the ideal planting<br />

date to avoid potential impacts of drought on crop yield. The results indicate that adopting<br />

a no-till management system may be one strategy of reducing the impact of drought by<br />

conserving more soil moisture and temperature than tilled soil. Also the soil temperature<br />

autoregression forecasting model using precipitation and air temperature as correlated data<br />

shows high certainty and accuracy for predicting soil temperature. The forecast model can<br />

be useful for predicting optimum planting date.<br />

205 - Modelling nitrate concentrations in the shallow subsurface<br />

for variable hydrogeological settings in agricultural watersheds<br />

Shoaib Saleem, Jana Levison, Beth Parker, Nishant Mistry & Scott Gardner<br />

School of Engineering – University of Guelph, Guelph, Ontario, Canada<br />

Ralph Martin<br />

Plant Agriculture – University of Guelph, Guelph, Ontario, Canada<br />

Groundwater is the principle source of water for about 30% of population in Ontario<br />

and most families living in rural areas entirely depend on it for their water supply. Advancements<br />

in agricultural technologies have increased farm productivity and profitability.<br />

However, associated intensive nitrogen application in agricultural fields has also resulted in<br />

leaching of excess nitrogen to aquifers in a variety of settings. Elevated nitrate in drinking<br />

water is a concern since it can lead to various health issues such as methemoglobinemia<br />

(blue-baby syndrome). The maximum allowable limit for nitrate in Canadian drinking<br />

water is 10 mg L -1 nitrate-N. Therefore, it is very important to have a comprehensive<br />

understanding of evolving cropping systems and their potential impact on groundwater<br />

84 IAH-CNC 2015 WATERLOO CONFERENCE


quality in various hydrogeological conditions in order to protect water at the source. As<br />

part of a broader nitrate study considering climate change impacts and sensitive aquifers,<br />

the objective of this specific research is to quantify the movement of nitrate through the<br />

root zone to the groundwater under different crop types using process-based modelling<br />

software. Research sites are selected in Ontario overlying different geological settings that<br />

are potentially sensitive to contamination from land-applied substances (fractured sedimentary<br />

bedrock aquifers and sandy aquifers). Nine different sites in Halton Region,<br />

Arkell Research Station (Guelph), and Norfolk County were selected to install twenty<br />

seven suction lysimeters at a depth of 40 cm below soil surface. The selection criteria for<br />

installation of the lysimeters are based on different crop types and proximity to groundwater<br />

wells in the vicinity of the fields. The shallow subsurface samples will be collected<br />

monthly from April to August 2015 and analyzed for nitrate nitrogen and ammonium<br />

nitrogen. DRAINMOD-N, a process-based model that simulates both hydrology (1-D<br />

flow) and nitrogen losses in the shallow subsurface on daily, monthly, yearly bases, is used<br />

to quantify nutrient transport below the root zone from different crop types and variable<br />

weather scenarios. Functional relationships are used in DRAINMOD-N to quantify fertilizer<br />

dissolution, plant uptake, denitrification, net mineralization, runoff and drainage<br />

losses to groundwater. The results of this surface-to-root zone transport study will be used<br />

as the input for groundwater models that will simulate nitrogen transport under a variety<br />

of crop and climate conditions. The research results can be applied specifically to nutrient<br />

management and farm source water protection initiatives.<br />

Groundwater/Surface Water Interaction 3<br />

Thursday October 29, 10:10 – 11:50<br />

Chair: Saskia Noorrduijn<br />

Room: Strauss<br />

223 - Integrated groundwater/surface water modelling to assess<br />

urban development and detailed stormwater design – Babcock<br />

Ranch Community Development, Lee County, Florida<br />

E.J. Wexler 1 , G.F. Rawl 2 , P.J. Thompson 1 , & J.D.C. Kassenaar 1<br />

1<br />

Earthfx Incorporated, Toronto, Ontario, Canada<br />

2<br />

Greg F. Rawl, P.G., Fort Myers, Florida, USA<br />

Integrated groundwater/surface water models are typically thought of as research tools,<br />

yet they can be applied in a practical manner to study impacts of land development and to<br />

assess the effectiveness of engineered mitigation measures. An integrated model was applied<br />

to predict change to shallow groundwater and surface water at the proposed Babcock<br />

Ranch Community (BRC) development in Lee County, FL. The BRC will have 19,500<br />

homes in concentrated “development pods”, with the remaining acreage left as wetland<br />

preserves and natural areas.<br />

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An integrated model was determined to be most appropriate tool for simulating groundwater<br />

and hydrologic response. There is considerable groundwater/surface water interaction<br />

across the site due to the shallow water-table and numerous streams and wetlands.<br />

The system is highly transient due to large rainfall events in the wet season. The area has<br />

been subject to severe drought and extreme wet years during the last decade.<br />

The integrated model was built using the USGS GSFLOW code. The hydrologic model<br />

(PRMS) was fully distributed with the soil water balance solved on the same 300 x 300<br />

foot grid used by the groundwater model. Over 600 wetlands and lakes were represented in<br />

the Current Conditions model along with all mapped streams and agricultural drains. The<br />

model was calibrated for WY2007 to WY2010 to flow at 10 gauges, wetland stage data,<br />

and heads at 165 observation wells.<br />

To represent Natural Conditions, the calibrated model was modified by removing all anthropogenic<br />

features such as roads, ditches, berms and water control structures that affected<br />

drainage and overland flow. Vegetative cover was also converted from agricultural to<br />

pre-settlement cover type and density. For Post-development Conditions, 142 stormwater<br />

ponds and with control structures and connections were added to the model. The ponds<br />

were designed to capture a portion of urban runoff. Leakage from the ponds is intended to<br />

raise groundwater levels and to hydrate nearby wetlands.<br />

Model simulations predicted streamflow, wetland stage, and groundwater heads on a<br />

daily basis for the three scenarios. Hydrographs and maps of net change in groundwater<br />

recharge and wetland hydroperiod were produced. Model comparisons showed that the<br />

stormwater management ponds helped mitigate changes due to increased imperviousness<br />

(up to 58% in the development pods) and confirmed that the changes would moderate<br />

stream flows, increase wetland hydroperiod, and generally restore “natural” conditions for<br />

the groundwater and surface water systems.<br />

209 - The Influence of storm sewers on groundwater-surface<br />

water interaction<br />

Martin Shepley & Nick Schmidt<br />

Amec Foster Wheeler, Hamilton, Ontario, Canada<br />

Ron Scheckenberger & Matt Senior<br />

Amec Foster Wheeler, Burlington, Ontario, Canada<br />

Urbanization of watersheds and increase in impermeable surfaces can strongly affect<br />

groundwater discharge, both in terms of quantity and recession characteristics. Storm sewers<br />

are generally not considered to affect groundwater discharge greatly as they are primarily<br />

seen as conveyances of runoff water. However, storm sewers leak and this leakage may<br />

increase over time as infrastructure ages.<br />

This paper presents results of a long-term monitoring program from an urbanised till plain<br />

setting that has collected detailed water level data from storm sewers, storm sewer trenches<br />

and the shallow groundwater system adjacent to creek. Storm sewer leakage tests have also<br />

been undertaken that allow the assessment of the interaction between the storm sewer<br />

86 IAH-CNC 2015 WATERLOO CONFERENCE


and the groundwater system independent of precipitation events and water level changes<br />

in the creek. These tests show that the water level in the storm sewer can be a dominant<br />

influence on groundwater level rise and recession. When the storm sewers fill, flow into the<br />

groundwater system occurs, which reverses when the storm sewer water level drops generating<br />

baseflow to the creek through the storm sewer trench and storm sewer. It is argued<br />

that under certain conditions, dependent on grading of the storm-sewer system and the<br />

hydraulic conductivity of the soils, the storm sewer system may account for the majority of<br />

groundwater-surface water interaction in urbanized watersheds.<br />

240 - Enhanced Field Methodologies for Quantifying the<br />

Vulnerability of Public Supply Wells to Surface Contamination<br />

C.E. Hillier, D.L. Rudolph & A. Wiebe<br />

Department of Earth and Environmental Sciences, University of Waterloo, Waterloo,<br />

Ontario, Canada<br />

Groundwater vulnerability assessment is crucial to ensuring that a municipal drinking<br />

water supply is safe for consumption. In evaluating the vulnerability of a public supply<br />

well, assessment metrics often rely on generalized or assumed hydrogeologic parameters<br />

combined with various modeling tools to categorize the vulnerability. This approach is<br />

often associated with a significant level of uncertainty, which influences the confidence of<br />

decision makers. This study examines the utility of detailed field site evaluation to enhance<br />

well vulnerability assessment for public supply wells. The value of adopting an integrated<br />

monitoring approach that incorporates hydrogeologic, hydrologic, and climatic data is addressed.<br />

A 60-day pumping test was conducted on a public supply well located within the<br />

Regional Municipality of Waterloo adjacent to a perennial stream. A network of groundwater<br />

monitoring wells was installed and instrumented in the vicinity of the well. Hydraulic<br />

head, temperature, geochemistry, isotopes, electrical conductivity, turbidity, and climatic<br />

data were monitored during the pumping test. Several of the data sets will be presented to<br />

illustrate their relevance to assessing the vulnerability of a supply well. Contrasting water<br />

quality data collected from the deep and shallow environments provided insight into the<br />

groundwater flow system. The dilution of calcium and hardness at the pumping well was<br />

attributed to the shallow groundwater contributions, whereas increasing concentrations of<br />

iron and sulfate indicated deeper groundwater contributions. Shallow groundwater temperature<br />

data indicated the downward movement of warmer, near-surface waters during<br />

the course of the pumping test. The temperature in the pumping well and nearby observation<br />

wells decreased as a result of pumping indicating deep colder groundwater was being<br />

drawn upward into the well over time. The combined geochemistry and temperature data<br />

provide evidence of mixing between the shallow and deep groundwater systems, information<br />

critical to understanding the vulnerability of public supply wells to surface contamination.<br />

The evidence presented here demonstrates that data collected from detailed field<br />

investigations during extended pumping tests provides added insight in the assessment of<br />

well vulnerability. The length of the test required will rely on local conditions.<br />

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198 - Monitoring of event-based, depression focussed recharge<br />

to a shallow unconfined aquifer near a municipal well in the Alder<br />

Creek Subwatershed, SW Ontario<br />

Paul G. Menkveld, Andrew J. Wiebe, & David L. Rudolph<br />

Department of Earth and Environmental Sciences – University of Waterloo, Waterloo,<br />

Ontario, Canada<br />

Groundwater is a critical resource that is dependent on recharge processes. Contrary to<br />

some conventional modelling practices that rely on annual and aerially averaged recharge<br />

rates, the natural recharge process is often discrete in time and space, which may significantly<br />

influence the dynamics of the groundwater flow system. Events such as snow melts<br />

and major rainfall periods may result in large amounts of infiltration over short time spans.<br />

In addition, depression-focused recharge may lead to anomalously large rates of recharge<br />

in small, local areas. To quantify these localized recharge phenomena, a dense monitoring<br />

network was established in a small (200 m 2 ) depression-focused recharge site, located<br />

within the Alder Creek sub-watershed, in the Regional Municipality of Waterloo. The<br />

site is located on the heavily managed Waterloo Moraine, with a shallow screened public<br />

supply well located within 40 m of the study site. Soil moisture (using TDR and a neutron<br />

probe), soil water tension, temperature, hydraulic head, resistivity, isotopes and pore-water<br />

geochemistry were measured in vertical profiles in the unsaturated zone and shallow<br />

saturated zone by electronic and manual instruments beneath an ephemeral pond formed<br />

during a snow melt event. Photo surveys were used to capture the formation, extents, and<br />

evolution of the pond. Continuous and time sparse (manually collected) data sets were<br />

constructed and compared to assess the value and accuracy of the different instruments.<br />

The combined data sets provide insight into the depression-focused recharge process and<br />

support estimates of recharge rates based on analytical and numerical modeling techniques.<br />

The effectiveness of the different data sets in understanding and quantifying the recharge<br />

process will also be discussed. Considering the close proximity of the public supply well<br />

to this recharge site, the study has implications for water supply security (GUDI) as hydrologic<br />

event-based analysis of the well’s capture zone will affect the well’s vulnerability<br />

to surface water.<br />

281 - Cumulative impacts of groundwater extraction on seasonal<br />

flows of a regulated stream, Cowichan River, BC<br />

Sylvia Barroso, Neil Goeller, & Pat Lapcevic<br />

BC Ministry of Forests, Lands and Natural Resource Operations, Nanaimo, BC, Canada<br />

Cowichan River is an important resource for the Vancouver Island region and North<br />

America’s west coast, providing critical spawning and rearing habitat for salmonid species,<br />

in addition to being a key source of industrial and municipal water supply, effluent dilution,<br />

a destination for recreation and tourism, and possessing cultural and economic significance<br />

to the Coast Salish First Nation. River flows in the lower reaches are linked to the underlying<br />

fluvial and glaciofluvial aquifer complex. Groundwater demands on this aquifer are<br />

substantial, including municipal and aquaculture well fields proximal to the river which<br />

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extract an estimated 27 Mm 3 of water annually. During the spring and summer periods,<br />

flows within Cowichan River are moderated by releases from a weir at Cowichan Lake, to<br />

ensure minimum instream flows are maintained and to provide for a major surface water<br />

extraction (50 to 60 Mm 3 /year) in the lower watershed. A three year, multi-disciplinary<br />

study was conducted to evaluate the interaction between groundwater withdrawals and<br />

surface water flows in Cowichan River. River stage above, within and below the primary<br />

well field reach was monitored on a continuous basis, using in-stream data loggers, coincident<br />

with groundwater level monitoring within a network of off-channel piezometers<br />

and observation wells. The median stream-bed conductivity estimated from in-stream<br />

mini-piezometers and seepage meters was in the range of 2x10 -4 m/s, and losing conditions<br />

were observed consistently within the well field reach. During the summer season,<br />

river flow within the well field reach was measurably reduced as a result of cumulative<br />

groundwater extractions and may impact sensitive aquatic habitat. Stable water isotopes<br />

and geochemistry were utilized to evaluate the relative contribution of groundwater and<br />

surface water inputs to production well withdrawals, and to characterize the quality of<br />

water sources throughout the basin. The complex interactions between consumptive and<br />

non-consumptive water use, competing water demands, and changing precipitation inputs<br />

and snowpacks resulting from climate variability present a challenge for long-term management<br />

and sustainability of an integrated water resource for this region.<br />

Sustainability of Groundwater Resources 1<br />

Thursday October 29, 10:10 – 11:50<br />

Chair: Garth van der Kamp<br />

Room: Wagner<br />

163 - Using numerical groundwater models as a land use planning<br />

tool – Town of Torbay, NL<br />

John Kozuskanich<br />

Stantec Consulting Ltd, Dartmouth, Nova Scotia, Canada<br />

Jonathan Keizer<br />

Stantec Consulting Ltd, Fredericton, New Brunswick, Canada<br />

Carolyn Anstey-Moore & Robert MacLeod<br />

Stantec Consulting Ltd, St. John’s, Newfoundland and Labrador, Canada<br />

The Town of Torbay, NL has grown quickly over the last two decades as a bedroom community<br />

for the neighbouring cities of St. John’s and Mount Pearl. Growth has been primarily<br />

focused in three developments around the periphery of the town in the form of halfto<br />

one-acre lots with private servicing. Approximately 30% of the residents in the older<br />

portions of Torbay rely on municipal servicing for their drinking water which is sourced<br />

from one of the many surface water ponds that dominate the landscape. This study is the<br />

first of its kind in NL to go beyond the scale of individual unserviced developments and<br />

evaluate the cumulative effects of development on the community’s groundwater resources.<br />

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A steady-state equivalent porous media groundwater flow model was developed as a tool to<br />

assist in planning the growth and sustainability of their community. Well log information<br />

was utilized in an effort to incorporate some of the attributes of the discretely-fractured<br />

bedrock groundwater system into the definition of adverse condition drawdown targets.<br />

The model was used to assess water availability under different future commercial and<br />

residential development schemes, rank development options, identify areas to be left undeveloped,<br />

define sustainable pumping rates, and evaluate the potential for municipal well<br />

fields. The results highlight the need for larger-scale hydrogeological assessment as part<br />

of the land use planning decision making process for semi-urban greenfield development.<br />

234 - Occurrence of viruses, other pathogens, and organic<br />

wastewater indicators, in seven First Nation Communities in<br />

Southern BC<br />

Marta Green<br />

Summit Environmental<br />

Ted Molyneux<br />

Aboriginal Affairs and Northern Development Canada<br />

Pierre Bérubé<br />

University of British Columbia Civil Engineering, Vancouver, British Columbia, Canada<br />

The BC region of Aboriginal Affairs and Northern Development Canada requires that all<br />

community water supply sources be disinfected at the source. This includes all groundwater<br />

supply wells that supply connections of five homes of more. Many first nation communities<br />

are located in remote areas, with low housing density. Moreover, well systems with<br />

chlorine treatment cause iron and manganese to precipitate, leading to a low aesthetic<br />

value of the water. The overall project goal is to develop screening methods for assessing<br />

groundwater that is at risk of containing waterborne pathogens (GARP) including using<br />

indicators/surrogates or newly available genetic testing methods such as quantitative polychain<br />

reaction (qPCR) testing for viruses. This is part of AANDC’s larger goal to assist<br />

First Nations in providing safe water to their members, and in providing understanding of<br />

the inherent safety of, or risk posed by, their water sources.<br />

The specific objectives of this study were to (1) develop and test a methodology to test for<br />

viruses in groundwater at First Nations’ wells in BC using dead end ultra-filtration techniques;<br />

(2) assess if surrogates or other indicators can be used to assess presence of viruses;<br />

and (3) determine if viruses, other pathogens, and/or organic wastewater compounds are<br />

present in a select number of First Nation communities in Southern BC at one snap shot<br />

in time. Samples were collected from confined and unconfined wells located near surface<br />

water, near septic fields and sanitary lines, and away from potential sources of pathogens.<br />

For pathogen testing, water was pumped through a dead-end ultrafilter, and filters were<br />

submitted to Tetratech laboratory in Vermont, USA. The work at Tetratech determined<br />

the presence and abundance of: (1) adenovirus types A, B, C, D, adenovirus-F, enterovirus,<br />

human polyoma virus, norovirus type GIA, norovirus type GII, and rotavirus using qPCR<br />

and real-time PCR (rtPCR) genetic testing (2) Cryptosporidium oocysts and Giardia<br />

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cysts by a modified Method USEPA 623 procedure; and (3) pathogenic bacteria E. coli<br />

O157:H7 and thermotolerant Campylobacter spp. by qPCR.<br />

UBC Vancouver conducted analysis of several organic wastewater compounds including<br />

ammonia, chloride, bisphenol A (BPA), bromide, caffeine, cholesterol, coprostanol, cotinine,<br />

methylene blue active substances (MBAS), nitrate, optical brighteners, residual<br />

chlorine, tinopal CBS-X , triclosan, and tri (2-chloroethyl)phosphate.<br />

Viruses were present in three of fifteen samples collected. Comparison of the results<br />

showed no link between presence or absence of organic wastewater indicators and presence<br />

or absence of viruses when virus sampling is conducted only once. Viruses were observed<br />

to be present in all types of sources except confined wells, while organic wastewater compounds<br />

were observed in all types of sources, even confined wells, indicating that a pathway<br />

for potential contamination exists even for confined wells. The study was successful in<br />

developing and testing a methodology to test for viruses in groundwater at First Nations’<br />

wells in BC using dead end ultra-filtration techniques. This methodology can be applied<br />

to future groundwater supply projects where communities wish to know their risk to water<br />

borne pathogens including viruses.<br />

238 - Groundwater: A sustainable water source for Waterloo<br />

Region<br />

Emil Frind<br />

University of Waterloo, Waterloo, Ontario, Canada<br />

Sustainable use of water is a challenge in many parts of the world, and extreme climate<br />

events due to climate change may aggravate this challenge in the future. The persistent<br />

drought in the American Southwest is just one example. Water sustainability is also a<br />

serious issue in Waterloo Region. The Region, having been designated as a main growth<br />

centre by the Province of Ontario, is expected to grow by 50% over the next 30 years,<br />

while its main water source, groundwater, remains limited. Can groundwater be a sustainable<br />

source for a rapidly growing Region? The Regional Municipality of Waterloo has<br />

addressed this question by developing a comprehensive water supply strategy balancing<br />

source water management and demand.<br />

The scientific basis and policy approach to the Region’s source water management are<br />

discussed in the Summer 2014 Special Issue “Water, Science and Policy” of the Canadian<br />

Water Resources Journal. The volume shows how collaboration among different disciplines<br />

of science, policy-making, and sociology has provided a comprehensive management<br />

framework. The science starts with a 3D hydrostratigraphic model of the Waterloo<br />

Moraine based on geological and geophysical data. Integration with existing hydrogeological<br />

data then creates a detailed picture of the complex moraine aquifer/aquitard system and<br />

its linkages to recharge areas and sensitive environmental features. Geochemical studies<br />

provide insight into the impact of human activities in urban and rural areas. Mathematical<br />

models play an important role as practical tools for resource management, and water<br />

budget calculations show how long the projected municipal water demand can be met<br />

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with the existing well system without affecting sensitive ecosystems. The broader role of<br />

the Moraine’s groundwater within the Grand River watershed is also examined. Threats<br />

to the quantity and quality of the Region’s groundwater are examined, and a framework<br />

for threats assessment for different types and scales of threats is developed. Finally, the<br />

science is translated into science-based policy satisfying the objectives of both environmental<br />

protection and source water protection. As an alternative for rural areas, collaborative<br />

decision-making integrating expert science, local knowledge, and community beliefs/values<br />

is explored. Finally, the issue of knowledge management, important in the context of<br />

complex problems, is discussed.<br />

This work has provided the Region with a solid basis for managing its groundwater source.<br />

The source is sustainable for at least the next forty years, and external water sources will<br />

not be needed. Beyond that, sustainability will depend on maintaining the balance between<br />

supply and demand.<br />

191 - Assessment of the Long-term Sustainability of Groundwater<br />

Aquifers in the Waterloo Moraine and Surrounding Areas<br />

Patricia Meyer, Paul Martin, & Martinus Brouwers<br />

Matrix Solutions Inc., Waterloo, Ontario, Canada<br />

Richard Wootton & Eric Hodgins<br />

Region of Waterloo, Waterloo, Ontario, Canada<br />

A Tier Three Water Budget and Local Area Risk Assessment (Tier Three Assessment)<br />

was recently completed within the Region of Waterloo. The study evaluated whether the<br />

municipality’s drinking water wells would be able to meet future demand without negatively<br />

impacting other water uses including sensitive coldwater streams, rivers and wetlands.<br />

Two groundwater flow models were used in the Tier Three Assessment; one was used to<br />

evaluate the well fields within the Kitchener-Waterloo area (the Regional Model), and the<br />

second was used to evaluate the well fields within the Cambridge area (the Cambridge<br />

Model). A GAWSER watershed-based flow generation model was also used to evaluate<br />

surface water conditions and partition precipitation into overland flow, evapotranspiration<br />

and groundwater recharge.<br />

Following a detailed calibration at the well field scale (to long-term and time varying conditions),<br />

the two groundwater flow models were used to conduct a series of Risk Assessment<br />

scenarios to evaluate potential changes in groundwater elevations at the municipal<br />

wells and groundwater discharge to sensitive surface water features under various conditions.<br />

The scenarios included evaluation of current and future municipal pumping, current<br />

and future land development (as specified in the Region’s Official Plan), and long-term<br />

drought. Results of these scenarios were used to assign risk levels to the Local Areas, an<br />

area defined as the cone of influence of the municipal wells, as well as land areas where reductions<br />

in recharge had the potential to have a measurable impact on the municipal wells.<br />

All four Local Areas within the Region were assigned a Low Risk Level. Within the<br />

Kitchener-Waterloo area, the integrated system of municipal groundwater supply wells are<br />

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completed in productive overburden aquifers within and beneath the Waterloo Moraine.<br />

The wells are capable of supplying water at rates that meet the Region’s projected 2031<br />

water demands without causing negative impacts on other water uses. Similarly, the wells<br />

in Cambridge are completed in productive overburden and bedrock aquifers that are able<br />

to meet the 2031 demands without negatively impacting other water uses. If the Region<br />

continues to proactively manage the quantity and quality of their groundwater supplies, the<br />

groundwater resources will be available for residents of the Region for generations to come.<br />

172 - Region of Waterloo Tier Three Water Budget - Now What?<br />

Richard Wootton<br />

Region of Waterloo, Kitchener, Ontario, Canada<br />

Paul Martin & Patricia Meyer<br />

Matrix Solutions Inc., Breslau, Ontario, Canada<br />

The Region of Waterloo’s Tier Three Water Budget and Local Area Risk Assessment has<br />

recently been completed. The Risk Levels applied to the four delineated Local Areas were<br />

identified as “Low” suggesting the Region has sufficient water resources to meet current<br />

and future (2031) water demands. Despite the Low Risk Level, a number of knowledge<br />

and data gaps were noted in the Tier Three Assessment. The most significant knowledge<br />

and data gaps, from a water supply and risk management measures perspective, included<br />

interaction between the municipal groundwater aquifers and urban streams/creeks and<br />

wetlands, and interaction between municipal well fields through the deep overburden or<br />

shallow bedrock aquifers within the Local Areas.<br />

Going forward the Region plans to develop an integrated groundwater and surface water<br />

monitoring program. The insights gained from the Tier Three groundwater flow model<br />

will be used to guide program implementation. The program will target collection of<br />

groundwater and surface water data in areas where there is potential for streams, creeks<br />

and wetlands to be influenced by municipal groundwater pumping, but knowledge and<br />

data gaps prevent conclusive analyses.<br />

The program will be designed to augment existing groundwater and surface water monitoring<br />

programs and focus on collecting data to integrate understanding of groundwater<br />

and surface water systems. It specifically will incorporate Tier Three recommendations for<br />

drilling boreholes and constructing new monitoring wells at strategic locations, installing<br />

stream flow gauges and streambed mini-piezometers, expanding and/or collecting more<br />

frequent groundwater level measurements in existing monitoring wells, and utilizing readily<br />

available spatial data (e.g., landsat imagery, historical airphotos).The data collected could<br />

be used to support permit to take water applications and where necessary, help establish<br />

adaptive management plans for water takings within the Region.<br />

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Groundwater Issues From Oil and Gas<br />

Exploration & Production 1<br />

Thursday October 29, 10:10 – 11:50<br />

Chair: Dick Jackson<br />

Room: Schubert<br />

275 - A case study of water well interference by CBM fracking:<br />

Lessons learned<br />

M. Cathryn Ryan & Per Pedersen<br />

Geoescience, University of Calgary, Calgary, Alberta, Canada<br />

Tiago A. Morais<br />

Geology, Federal University of Rio Grande do Sul, City, Porto Alegre, Rio Grande do Sul,<br />

Brazil<br />

A 2004 case study of perceived water well interference by ‘stimulation’ of a coal bed methane<br />

well with ~9 MPa N 2<br />

stimulation about 1200 meters away was reviewed. Although an<br />

official complaint was never filed with the regulator, the energy company contracted an<br />

environmental consultant to review the homeowner’s concerns. These reports, water well<br />

records, baseline water well testing, and energy well activities in the region were reviewed,<br />

and discussions with various individuals involved were held.<br />

The timeline of water well events and details surrounding the CBM well activity during<br />

and after the N 2<br />

stimulation suggest the water well could have been affected by the stimulation.<br />

The energy well perforations were unusually shallow for the region, and similar in<br />

elevation to the domestic water well screen. The shallowest energy well perforations were<br />

cement-¬squeezed on two subsequent occasions to mitigate groundwater flow into the<br />

CBM well, which was abandoned about seven months after the initial stimulation.<br />

Although the evidence suggests that the energy well stimulation may have been related<br />

to the perceived domestic water well interference, subsequent stimulation in energy wells<br />

located even closer to the rural residence (but perforated at greater depth) did not cause<br />

observed interference in a replaced domestic water well on the same property.<br />

This case study highlights water well complaint challenges for both the energy industry<br />

and domestic well owners that are relevant to the ‘social license to operate’. Dedicated<br />

groundwater monitoring systems are seldom used to evaluate impacts in the shallow<br />

groundwater zone. Rather energy and water wells are often the only source of subsurface<br />

data available. The industry deals with a large fraction of apparently invalid water well<br />

complaints, making it difficult to focus on complaints that may be valid. In part in an effort<br />

to minimize invalid water well complaints, the industry i) has not historically disclosed<br />

details about confirmed water well complaints that are appropriately addressed and ii) do<br />

not provide any notification of energy activities in a given region. The latter can prevent the<br />

timely collection of appropriate information, with subsequent the difficulties in conducting<br />

a ‘post--mortem’ analysis and perceived water.<br />

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160 - A study of potential links between the Utica Shale and<br />

shallow aquifers in St-Édouard, southern Québec, Canada<br />

Rivard, C., Bordeleau, G., Lavoie, D., Ladevèze, P., Duchesne, M., Pinet, N., &<br />

Ahad, J.<br />

Geological Survey of Canada, Québec City, Québec, Canada<br />

Lefebvre, R. & Aznar, J.-C.<br />

Institut national de la Recherche scientifique – Centre Eau Terre Environnement (INRS-<br />

ETE), Québec City, Québec, Canada<br />

Pugin, A. & Crow, H.<br />

Geological Survey of Canada, Ottawa, Ontario, Canada<br />

Séjourné, S.<br />

Consulting geologist, Montréal, Québec, Canada<br />

Labrie, D.<br />

CanmetMINING, Ottawa, Ontario, Canada<br />

Potential links between a deep gas shale formation and shallow aquifers are being investigated<br />

in southern Quebec (Canada), near a shale gas well drilled and fracked in 2009-2010.<br />

A large set of data has been collected to detect potential natural fluid migration pathways.<br />

Acquired data include hydrogeological, geophysical, geochemical, as well as geomechanical<br />

data. Hydrogeological work involved drilling, permeability tests and structural surveys<br />

of outcrops. Geophysical surveys comprised shallow high-resolution seismic, borehole logging<br />

in the newly drilled shallow wells, as well as airborne Transient-Electro-Magnetic and<br />

magnetic surveys. Groundwater from 44 wells was sampled and analyzed for a wide range<br />

of compounds, and 6 of these wells were chosen for continued monitoring of dissolved<br />

alkane concentration and isotopes (every 3 months). Soil and core samples were also collected<br />

to determine their hydrocarbon content. Geomechanical properties of deep shale<br />

formations were studied using both acoustic geophysical logs and core samples.<br />

Geochemical data show that methane is present throughout the study area, but in highly<br />

variable concentrations (from nearly 0 to 40 mg/L), while ethane and propane are only<br />

found in a few wells. Preliminary results indicate that alkane concentrations are strongly<br />

correlated to the water type, well depth and groundwater age. They also show that all<br />

samples would contain bacteriogenic methane, and from 20 to 40% would also have a thermogenic<br />

component. Additional analyses on groundwater and core samples are ongoing<br />

to better identify the methane source. The geophysical interpretation, including deep and<br />

shallow data, suggests that possible pathways could be present. However, hydraulic tests<br />

have not indicated different permeabilities close to known faults. Permeabilities in the<br />

shallow and naturally fractured shale rock aquifers vary from moderate where sandstone<br />

beds occur (10 -6 – 10 -7 m/s) to low when mostly black shale is present (10 -9 -10 -8 m/s).<br />

Borehole logging showed that most of the permeable fractures occur in the upper 40 m<br />

and that permeability usually rapidly decreases with depth. Brackish water in one well<br />

was encountered at about 140 m deep, confirming that active groundwater flow is very<br />

shallow. Geomechanical data further indicate that the caprock geological units above the<br />

gas shale act as a good protection against potential contamination from deep fluids. This<br />

study integrates data from multiple sources in order to acquire the necessary knowledge to<br />

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support provincial regulations and water management to insure that aquifers would not be<br />

adversely affected by shale gas development, at least from a geological point of view.<br />

138 - Local study of the environmental risk of hydrocarbon<br />

exploration<br />

Mélanie Raynauld 1 , Morgan Peel 1 , René Lefebvre 1 , Michel Ouellet 2 , John Molson 3 ,<br />

Heather Crow 4 , Jason Ahad 5 , & Luc Aquilina 6<br />

1<br />

INRS, Centre Eau Terre Environnement, Québec City, Québec, Canada<br />

2<br />

Ministère du Développement durable, de l’Environnement et de la Lutte contre les<br />

changements climatiques, Québec City, Québec, Canada<br />

3<br />

Laval University, Geology and Geological Engineering Department, Québec City, Québec,<br />

Canada<br />

4<br />

Natural Resources Canada, Geological Survey of Canada, Ottawa, Ontario, Canada<br />

5<br />

Natural Resources Canada, Geological Survey of Canada, Québec City, Québec, Canada<br />

6<br />

Université de Rennes 1, Géosciences Rennes, Rennes, France<br />

Horizontal drilling is planned to further assess a tight sandstone petroleum reservoir in<br />

the Haldimand sector of Gaspé, Québec, Canada. Petroleum exploration is taking place<br />

in this area within the forested core of a hilly 40 km 2 peninsula by the sea (up to 200<br />

m amsl) and water supply wells are located on its periphery. Our study aimed to assess<br />

the local risk to groundwater related to oil and gas (O&G) industry upstream activities.<br />

Such assessment involves the identification of potential fluid migration paths between<br />

the petroleum reservoir and the shallow fractured rock aquifer system. This study<br />

also served as a test case for a new Quebec regulatory framework for O&G operations,<br />

which requires the hydrogeological characterization of all new drill sites. The study was<br />

based on the compilation of existing hydrogeological, geological and petroleum exploration<br />

data and on field characterization. The field work involved 1) the installation of<br />

17 observation wells and related hydraulic testing, including two fully-cored wells, 2)<br />

groundwater sampling in observation wells and more than 70 residential wells, as well<br />

as surface water sampling, mostly within a 2 km radius of the proposed new drill pad,<br />

and 3) geophysical logging of the open-hole observation wells. Fracturing was found to<br />

be more intense in the upper 20 m of the rock aquifer and it controls groundwater flow.<br />

Recharge occurs on topographic highs where the rock is not covered by a low permeability<br />

glacial till, which is found almost everywhere. Significant variations in groundwater<br />

geochemistry were found, with evolved groundwaters affected by cation exchange or<br />

mixing with a marine water component. Groundwater residence times can thus be quite<br />

long, which may be due to the relatively high porosity (5-10%) of the rock. Methane<br />

is associated with evolved water types and is mostly biogenic, but with a thermogenic<br />

fraction. SALTFLOW, a variable-density flow and mass transport simulator, was used<br />

to represent the peninsula and the adjacent highlands in a 2D vertical section model.<br />

The interaction of the highland and peninsula recharge leads to nested flow systems<br />

with converging-diverging flow conditions, and a relatively shallow active flow zone. Assessment<br />

of the risk for groundwater considered regulatory requirements, contaminant<br />

emission mechanisms and their expected effects. A surface spill is the most probable<br />

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contaminant release mechanism. There are no indications of active natural preferential<br />

fluid migration pathways, but old O&G exploration wells cut through the reservoir and<br />

their integrity should be verified.<br />

182 - Three-dimensional Reactive Transport Simulations of<br />

Methane Gas and Brine Migration from Decommissioned Shale<br />

Gas Wells into Shallow Aquifers<br />

N. Roy 1 , J. Molson 1 , D. van Stempvoort 2 , A. Nowamooz 1 , & J.-M. Lemieux 1<br />

1<br />

Département de géologie et de génie géologique, Université Laval, Québec, Canada<br />

2<br />

National Water Research Institute, Environment Canada, Burlington, Ontario, Canada<br />

Three-dimensional numerical simulations are presented for methane gas and gas-saturated<br />

brine leaking from a decommissioned shale gas well into a shallow aquifer. The<br />

main objective is to assess the efficiency of natural bacterially-driven processes to mitigate<br />

dissolved gas contamination in both confined and unconfined aquifers. The basecase<br />

conceptual model, based on an Alberta field site, includes a shallow sandy confined<br />

aquifer intersected by a vertical well which is leaking gas-phase and dissolved-phase<br />

methane from a faulty cement seal. We couple the DuMux multi-phase simulator with<br />

the BIONAPL/3D flow and reactive transport code to simulate biodegradation of dissolved<br />

methane under oxygen and sulfate-reducing conditions. The methane degradation<br />

rate is calibrated for the field case while a range of literature values are applied in<br />

a sensitivity analysis. Methane behavior in the aquifer is simulated for different leakage<br />

rates, background geochemistry and hydraulic gradients. The confined aquifer simulation<br />

shows that, unlike the buoyant gas phase that migrates upward towards the confining<br />

layer, the gas-saturated brine flows at the base of the aquifer following the hydraulic<br />

gradient. The upper gas-phase pool acts as a longer-term source which dissolves into the<br />

flowing groundwater. Methane concentrations in both confined and unconfined aquifers<br />

are mainly influenced by the gas/brine leakage duration, background oxygen and/or<br />

sulfate concentration and the methane oxidation rate. At the Alberta site, considering<br />

a continuous methane gas phase leakage rate of 0.40 kg/day, a threshold of 7 mg/L (ex.<br />

as stipulated by the Québec Ministry of Environment for identifying wells at possible<br />

risk) is reached 55 m downgradient after 2 years. Moreover, if the leak stops after 2 years,<br />

under natural background SO 4<br />

concentrations of 400 mg/L, it would take between 7 and<br />

8 years for dissolved methane concentrations to decrease to acceptable levels. In confined<br />

aquifers, methane tends to persist longer than in unconfined aquifers from which<br />

the buoyant gas phase will more readily escape and in which oxygen concentrations are<br />

likely higher. Aquifers with a naturally high background sulfate concentration can significantly<br />

attenuate methane migration but sulfide by-products may become a concern.<br />

The modelling approach can be extended to other contaminants emerging from deep<br />

decommissioned or abandoned wells or from natural faults and fractures such as brines,<br />

or fracking fluids.<br />

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319 - Baseline Water Well Testing in Oil and Gas Development<br />

Areas of Alberta<br />

Steve Wallace<br />

Alberta Environment and Parks, Government of Alberta, Alberta, Canada<br />

The Standard for Baseline Water Well Testing (BWWT) for Coalbed Methane Operations<br />

was implemented in 2006 in response to concerns amongst Albertans about the<br />

potential for CBM activities to adversely affect water well supplies. The baseline water<br />

well testing requires operators to test all active water wells within the vicinity of a proposed<br />

CBM well to be completed above the Base of Groundwater Protection. The testing includes<br />

a well capacity test, water quality sampling and testing for dissolved gases. The latter<br />

includes stable carbon isotopic analyses on hydrocarbon gas components. Over 15,000<br />

baseline water well tests have been completed to date. An overview of the BWWT program<br />

and the results gathered is provided.<br />

Expansion of the BWWT program to unconventional oil and gas development areas, including<br />

shale gas and tight oil, is currently being considered. Alberta Environment and<br />

Parks is working closely with the Alberta Energy Regulator on potential revision/expansion<br />

of the BWWT program, using knowledge gained through the CBM experience and<br />

taking into consideration modifications to reflect the unique aspects of unconventional oil<br />

and gas development.<br />

Advanced Techniques for Site<br />

Characterization<br />

Thursday October 29, 10:10 – 11:50<br />

Chair: Walter Illman<br />

Room: Heritage<br />

136 - Definition of granular aquifer heterogeneity for large sites<br />

René Lefebvre 1 , Erwan Gloaguen 1 , Daniel Paradis 2 , Laurie Tremblay 1 , Patrick<br />

Brunet 1 , John Molson 3 , & Gabriel Fabien-Ouellet 1<br />

1<br />

INRS, Centre Eau Terre Environnement, Québec City, Québec, Canada<br />

2<br />

Natural Resources Canada, Geological Survey of Canada, Québec City, Québec, Canada<br />

3<br />

Laval University, Geology and Geological Engineering Department, Québec City, Québec,<br />

Canada<br />

Contaminated site management requires the predictive capabilities of hydrogeological numerical<br />

models. Such models have to encompass source zones and receptors over several<br />

square kilometers. To be representative, these models have to represent the heterogeneous<br />

distribution of hydraulic conductivity (K). Hydrogeophysics has generally been used to image<br />

relatively restricted areas of the subsurface (small fractions of km 2 ), but there remains a<br />

need for approaches defining heterogeneity at larger scales. This communication describes<br />

a workflow defining aquifer heterogeneity that was applied over a 12 km 2 sub-watershed<br />

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surrounding a decommissioned landfill emitting landfill leachate. The aquifer is a shallow,<br />

10 to 20 m thick, highly heterogeneous and anisotropic assemblage of littoral sand and<br />

silt. Field work involved the acquisition of a broad range of data: geological, hydraulic,<br />

geophysical, and geochemical. The emphasis was put on high resolution and continuous<br />

hydrogeophysical data, the use of direct-push fully-screened wells, and the acquisition of<br />

targeted high-resolution hydraulic data covering all aquifer materials. The main methods<br />

used were: 1) surface geophysics (ground-penetrating radar and electrical resistivity); 2)<br />

direct-push operations with a geotechnical drilling rig (cone penetration tests with soil<br />

moisture resistivity CPT/SMR; full-screen well installation); and 3) borehole operations,<br />

including high-resolution hydraulic tests and geochemical sampling. New methods were<br />

developed to acquire high vertical resolution hydraulic data in direct-push wells, including<br />

both vertical and horizontal K (Kv and Kh). Various data integration approaches were used<br />

to represent aquifer properties in 1D, 2D and 3D. Using relevant vector machines (RVM),<br />

the mechanical and geophysical CPT/SMR measurements were used to recognize hydrofacies<br />

(HF) and obtain high-resolution 1D vertical profiles of hydraulic properties. All<br />

1D vertical profiles of K derived from the CPT/SMR soundings were integrated with<br />

available 2D geo-electrical profiles to obtain the 3D distribution of K over the study area.<br />

Numerical models were developed to understand flow and mass transport and assess how<br />

indicators could constrain model results and their K distributions. A 2D vertical section<br />

model was first developed based on a conceptual representation of heterogeneity, which<br />

showed a significant effect of layering on flow and transport. The model demonstrated<br />

that solute and age tracers provide key model constraints. Additional 2D vertical section<br />

models with synthetic representations of low and high K hydrofacies were also developed<br />

on the basis of CPT/SMR soundings. These models showed that high-resolution profiles<br />

of hydraulic head could help constrain geostatistical simulations of the spatial distribution<br />

and continuity of hydrofacies.<br />

204 - Comparison of hydraulic tests used to charaterize aquifer<br />

heterogeneity<br />

Daniel Paradis<br />

Geological Survey of Canada, Québec City, Québec, Canada<br />

René Lefebvre<br />

Institut national de la recherche scientifique – Centre Eau Terre Environnement, Québec<br />

City, Québec, Canada<br />

Hydraulic properties of aquifers, especially hydraulic conductivity (K), have to be known to<br />

understand groundwater flow and solute transport. Indirect characterization methods (hydrogeophysics)<br />

and geostatistical simulations are now accepted approaches to define aquifer<br />

heterogeneity. However, these approaches actually put higher requirements on direct measurements<br />

of hydraulic properties to calibrate indirect methods and constrain geostatistical<br />

simulations. The purpose of this study is to evaluate the ability of diverse hydraulic tests to<br />

define the spatial distribution of hydraulic properties, including commonly used (grain size<br />

analysis, lab permeameter, multilevel slug tests and flowmeter tests) and recently developed<br />

(vertical interference slug tests and tomographic slug tests) methods. This study was carried<br />

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out in heterogeneous and anisotropic littoral silts and sands. A field site was instrumented<br />

with five direct-push wells arranged in a diamond pattern using about 10-m spacing. Direct-push<br />

wells were installed with long screens placed in direct contact with natural sediments,<br />

thus allowing flexibility in the design of high-resolution hydraulic tests using packers.<br />

In these wells, horizontal K (Kh) was estimated at a 15-cm spacing using an electromagnetic<br />

flowmeter and multilevel slug tests, while Kh, K anisotropy (Kv/Kh) and specific storage (Ss)<br />

were characterized at 60-cm vertical intervals using vertical interference slug tests within a<br />

well and tomographic slug tests across wells. Furthermore, sediment samples were collected<br />

near the wells to assess Kh and Kv using grain size analyses and laboratory permeameter tests,<br />

respectively. The hydraulic property fields obtained from the different measurement methods<br />

were then quantitatively evaluated by predicting transient head responses from independent<br />

hydraulic tests using a forward numerical model. Results show that independent hydraulic<br />

tests are fairly well reproduced with vertical interference slug tests. So, even though this approach<br />

requires more complex numerical inverse analysis than conventional hydraulic tests<br />

with analytical solutions, it proves to be relatively time efficient considering that Kh, Kv/Kh<br />

and Ss can be estimated together. Tomographic slug tests are also shown to better represent<br />

transient hydraulic responses between wells, but the additional instrumentation costs and<br />

data burden involved compared to vertical interference slug tests should be carefully considered<br />

for practical field studies. Finally, this study shows that the strong Kv/Kh anisotropy<br />

at the scale of test measurements can make K characterization challenging. The study also<br />

highlights the need for hydraulic methods that can reliably estimate Kv/Kh, since groundwater<br />

flow is strongly influenced by K anisotropy.<br />

262 - Advanced techniques for site characterization: Real-Time<br />

High-Resolution Site Characterization of the Subsurface Using<br />

and MIP, LIF and HPT<br />

Patrick O’Neill<br />

Vertex Environmental Inc, Cambridge, Ontario, Canada<br />

In-situ site characterization can be a key component of site delineation and remediation.<br />

In-situ site characterization allows for large amounts of detailed data to be collected quickly<br />

and cost-effectively compared to traditional techniques. These data, combined with traditional<br />

Phase II Environmental Site Assessment (ESA) methods, greatly enhance the understanding<br />

of the presence, concentration and distribution of contaminants in the subsurface,<br />

which can lead to more efficient and focused monitoring and remediation programs.<br />

Three high-resolution characterization technologies have recently been introduced to<br />

Canada. These include, the Membrane Interface Probe (MIP) for dissolved phase contamination,<br />

the Laser-Induced Fluorescence (LIF) probe for free-phase petroleum hydrocarbon<br />

(PHC) contamination, and the Hydraulic Profiling Tool (HPT) for measuring<br />

the subsurface permeability and ultimately estimating the hydraulic conductivity of the<br />

subsurface. All three probes are advanced to depth by direct push methods (Geoprobe).<br />

The MIP is a heated probe that is used to volatilize dissolved and sorbed contaminants.<br />

The contaminants diffuse through a semi-permeable membrane on the probe and are sub-<br />

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sequently transported to the surface for analysis. The LIF probe consists of a fiber optic<br />

cable that emits an ultraviolet light through a window during probe advancement. The<br />

PAHs in PHCs fluoresce and the response is measured by instrumentation at the surface in<br />

real-time. The HPT probe injects a constant flow of clean water from surface and utilizes<br />

a downhole pressure transducer to measure subsurface permeability above and below the<br />

water table. Hydraulic conductivity can be estimated in the saturated zone at the conclusion<br />

of each push.<br />

Using these technologies and Phase II ESA data, subsurface plumes can be rendered in<br />

3D to visualize the interpreted area of impact requiring remediation. Aerial photographs,<br />

building CAD models or GIS terrain data can also be added to provide a more detailed<br />

visualization of the site for conceptual models and presentation purposes. This visualization<br />

tool can be used to optimize remedial system designs or supplemental data collection<br />

programs and offers superior communication potential to clients and other stakeholders.<br />

The LIF employs a laser light to excite florescent molecules contained in major LNAPLs<br />

including gasoline, diesel fuel, hydraulic oil, jet fuel, kerosene, etc. Major benefits of the<br />

LIF include high data density collection, speed and daily production for logging NAPL<br />

in the subsurface. The LIF is rapidly deployed using direct push technologies to delineate<br />

large areas efficiently. The LIF transmits pulses of laser light down fiber optic cables<br />

located in probe rods (advanced through the soil column steadily at ~2 cm/second). The<br />

light pulses exit a sapphire window, located on the probe, onto the face of the passing soil<br />

without penetrating into the formation. Any resulting fluorescence laser light that comes<br />

back into the window is brought up hole to the surface by a second fiber, where the light is<br />

processed, analyzed and displayed versus depth in real time.<br />

The MIP employs an inert carrier gas, a semi-permeable membrane in conjunction with<br />

a heater block on a down hole probe used to log the relative concentrations of volatile organic<br />

compounds (VOCs) in the subsurface. Major benefits of the MIP include high data<br />

density collection, speed and daily production for logging dissolved phase impacts in the<br />

subsurface. The MIP is rapidly deployed using direct push technologies to delineate large<br />

areas of dissolved phase VOCs on Site. The MIP heats probe up the subsurface, volatilizing<br />

the VOCs in the immediate area before carrying the VOCs up hole to a gas chromatograph<br />

(GC) at the surface. The VOCs are then analyzed in using a photoionization<br />

detector (PID), flame ionization detector (FID) and a halogen specific detector (XSD).<br />

The VOCs are analyzed and displayed versus depth in real time up hole.<br />

The HPT employs a an up hole pump with a down hole pressure transducer to measure<br />

the down hole back pressure from the formation and calculate hydraulic conductivity in<br />

the saturated zone. Major benefits of the HPT include high data density collection, speed<br />

and daily production for logging formation permeability and hydraulic conductivity in the<br />

subsurface. The HPT is rapidly deployed using direct push technologies to delineate large<br />

areas efficiently. The HPT pumps a flow of clean water into the subsurface at a constant<br />

rate and the down hole pressure transducer measures the back pressure on the flow of water<br />

from formation. The HPT can also be used to measure hydrostatic pressure under zero<br />

flow conditions. This allows for down hole prediction of the water table depth. The data<br />

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collected can then be used to calculate hydraulic conductivity in the saturated zone. The<br />

data collected is analyzed and displayed versus depth in real time up hole.<br />

Each technology will be briefly discussed, and a case study will be presented where both<br />

the MIP and the LIF were used prior to and during in situ remediation of PHCs. The<br />

case study demonstrates how the site characterization tools were utilized to intelligently<br />

alter the approach to work at the site. The 3D modeled renderings of the plumes will be<br />

presented to show how the results were used to alter future remedial designs.<br />

266 - Estimating specific storage of an aquifer using borehole<br />

geophysics, barometric efficiency, and laboratory core testing<br />

Polina Abdrakhimova, Laurence R. Bentley & Masaki Hayashi<br />

Department of Geoscience, University of Calgary, Calgary, Alberta, Canada<br />

A crucial parameter for groundwater management is specific storage, which relates changes<br />

in hydraulic head to changes in the volume of water stored in a confined aquifer. In-situ<br />

values of specific storage are conventionally estimated by analysing pumping test data based<br />

on the idealized aquifer theory. However, in case of heterogeneous aquifers, this method<br />

can result in unreliable estimates due to the violation of the ideal aquifer assumptions. An<br />

example of heterogeneous aquifer is the Paskapoo Formation, which is characterized by<br />

sandstone channels embedded in lower permeability mudstone and siltstone. Being the<br />

most significant groundwater supply source in Alberta, its management requires reliable<br />

characterization of hydrogeological properties.<br />

An alternative approach to the estimation of specific storage is to use its relationship with<br />

the formation’s elastic parameters, in particular the aquifer matrix compressibility. Aquifer<br />

compressibility can be evaluated using Young’s modulus and Poisson’s ratio, which can be<br />

derived from laboratory core testing or in-situ geophysical methods. It can also be estimated<br />

by analysing water-level fluctuations due to the barometric effect. In-situ geophysical<br />

methods include borehole vertical seismic profiling (VSP) and sonic logging. Continuous<br />

borehole logs of compressional and shear wave velocity are used to calculate the distribution<br />

of Young’s modulus and Poisson’s ratio along the profile, and estimate specific storage<br />

distribution. The three methods produce estimates of specific storage at a variety of spatial<br />

sampling scales. The comparison of these methods and their performance gives insights<br />

into the characterization of complex fluvial aquifer systems.<br />

301 - Versatile Monitoring Completions for Bedrock Vadose Zone<br />

VOC Gas Sampling<br />

Beth L. Parker & Amanda A. Pierce<br />

G360 Centre for Applied Groundwater Research, University of Guelph, Ontario, Canada<br />

Murray Einarson<br />

Haley & Aldrich, Oakland, California, USA<br />

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Robert Ingleton & Tadeusz Gorecki<br />

Department of Earth and Environmental Sciences, University of Waterloo, Ontario, Canada<br />

Michael O. Bower<br />

The Boeing Company, Canoga Park, California, USA<br />

Eric VanderVelde<br />

MWH Americas, Arcadia, California, USA<br />

The Shaw Portable Core Drill was used to install bedrock vadose zone monitoring probes at<br />

an industrial facility in southern California where in the 1950s-1960s an estimated 2 million<br />

litres of immiscible phase trichloroethene (TCE) was released into the subsurface. The subsurface<br />

is composed of faulted Late Cretaceous age turbidite sandstones with shale interbeds.<br />

TCE, as dense non-aqueous phase liquid, entered the fractures at many locations decades ago<br />

where it was dissolved and subsequently diffused into the rock matrix. Sampling and analysis<br />

of rock core (COREDFN) indicates contaminants present in the vadose zone rock matrix at<br />

contaminant input locations. The Shaw drill was used to drill 51 millimeter diameter holes<br />

to shallow depths (2 to 4.5 metres) in the vadose zone at three locations in the central portion<br />

of the site. Two design types were tested; the first type consisted of a modified ‘grout-liner’<br />

design, where a seal is created in the small diameter hole by injecting grout into a flexible<br />

cylindrical impervious fabric liner and the second type consisted of a modified packer. Both<br />

designs incorporate high integrity seals to allow for the versatility of active vapour sampling,<br />

as well as passive sampling using the Waterloo Membrane Sampler TM . Measurements of volatile<br />

organic contaminant (VOC) vapour concentrations in the vadose zone can be used for<br />

assessing the transport of contaminants in the fractures and the flux of contaminant concentrations<br />

from the vadose zone to ground surface. The efficiency of these small portable drills<br />

has allowed them to become a valuable tool to quickly install monitoring probes in bedrock<br />

for assessing VOC transport in fractured rock vadose zones.<br />

Groundwater/Surface Water Interaction 4<br />

Thursday October 29, 13:00 – 14:40<br />

Chair: Steven Berg<br />

Room: Strauss<br />

239 - Artificial sweeteners track septic system effluent in rural<br />

Ontario groundwater<br />

John Spoelstra<br />

Environment Canada, Burlington, Ontario, Canada & Department of Earth and<br />

Environmental Sciences - University of Waterloo, Ontario, Canada<br />

Natalie D. Senger & Sherry L. Schiff<br />

Department of Earth and Environmental Sciences - University of Waterloo, Ontario,<br />

Canada<br />

Susan J. Brown<br />

Environment Canada, Burlington, Ontario, Canada<br />

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Artificial sweeteners (AS) are commonly used in food, beverage and medicinal products,<br />

largely to reduce sugar consumption. Several of these artificial sweeteners are not completely<br />

broken down during wastewater treatment and are increasingly being found in<br />

lakes, rivers, and groundwater around the world. In urban areas, municipal wastewater<br />

treatment plants and leaky sewer systems can be a source of artificial sweeteners to local<br />

groundwater and surface water. In rural areas, private septic systems treat domestic wastewater<br />

and discharge effluent to the sub-surface, making them a primary source of AS in<br />

rural groundwater. Landfill leachate may also be a source of AS in both settings.<br />

To investigate the prevalence of artificial sweeteners in rural groundwater, we sampled<br />

private domestic wells and groundwater springs in the Nottawasaga River Watershed<br />

(NRW), located about 50 km north of Toronto, Ontario, Canada. Domestic groundwater<br />

in the southern NRW is typically supplied by the Lake Algonquin Sand Aquifer (LASA),<br />

a sandy surficial aquifer known to have nitrate concentrations of up to ten times the drinking<br />

water limit. The LASA is exposed along the incised banks of the southern Nottawasaga<br />

River and groundwater discharge was sampled from these seeps.<br />

Four AS, acesulfame (ACE), cyclamate (CYC), saccharin (SAC), and sucralose (SUC)<br />

were analyzed using ion chromatography coupled with tandem mass spectrometry operated<br />

in negative electrospray ionization mode, with minimum detection limits ranging from<br />

2 to 20 ng/L for the individual AS. ACE was the most frequently detected AS in groundwater<br />

and had the highest measured concentration (>26,400 ng/L). Artificial sweeteners<br />

were detected in 31% and 37% of the domestic wells and groundwater seeps, respectively,<br />

indicating a contribution of water derived from septic system effluents. No clear relationships<br />

were found between the presence of artificial sweeteners and the concentrations of<br />

other groundwater contaminants potentially derived from septic systems, including nitrate,<br />

ammonium, and soluble reactive phosphorus.<br />

The persistence, mobility, and relatively high concentrations of AS in the environment,<br />

particularly ACE, means that these compounds may still be detectable in groundwater<br />

long after other wastewater constituents (e.g. nutrients, pharmaceuticals, pathogens) have<br />

been removed or diluted to levels below detection limits. Artificial sweeteners have the<br />

potential to be a powerful groundwater screening tool for identifying wells or aquifers that<br />

have a septic effluent component to recharge and where testing for additional contaminants<br />

may be warranted, especially where the groundwater is used for potable water supply<br />

or discharges to environmentally sensitive surface waters.<br />

217 - Hydrogeological characterization of a waste site at Chalk<br />

River, Ontario<br />

Colleen Steele, Grant Ferguson & Andrew Ireson<br />

Department of Civil and Geological Engineering – University of Saskatchewan, Saskatoon,<br />

Saskatchewan, Canada<br />

Geological storage of low level radioactive waste presents a substantial challenge. Waste at<br />

these sites can remain radioactive for hundreds of years. These sites frequently contain other<br />

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metals and metalloids that may persist for even longer time periods. In order to protect water<br />

quality and manage contaminated sites effectively, the drivers and controls on groundwater<br />

flow and solute transport need to be understood. The purpose of this research project assess<br />

the risk to the environment posed by storage of low level radioactive waste at the Canadian<br />

National Laboratories’ (CNL) Chalk River, Waste Management Area F (WMAF) site.<br />

The larger project includes an investigation of geochemical, vadose zone and saturated zone<br />

processes. The focus is on the potential for transport once solutes reach the water table. This<br />

has yet to happen in appreciable levels at this site. As a result, this study has concentrated on<br />

hydraulic testing and instrumentation of piezometers at WMAF and adjacent areas. During<br />

August 2014, over 20 slug tests were performed at WMAF. Transducers were installed to<br />

measure hydraulic head. Up until this time, hydraulic head measurements were taken sporadically<br />

by CNL staff. Results of the field program have been used to create a probabilistic<br />

groundwater flow model. Results provide a range of travel times between the water table<br />

beneath the waste and the wetland to the east. These travel times provide a framework to<br />

guide future investigations that will reduce the uncertainty and risk.<br />

187 - Assessing the Impacts of Contaminated Groundwater<br />

Discharges to the Surface Waters of the Canadian Great Lakes<br />

Basin: Science Needs and Data Gaps<br />

Brewster Conant Jr.<br />

Department of Earth and Environmental Sciences - University of Waterloo, Ontario,<br />

Canada<br />

A review was undertaken regarding the current state of knowledge with respect to chemical<br />

contaminants in groundwater discharging to the surface waters of the Canadian Great<br />

Lakes Basin (GLB) as part of Canada’s reporting obligations required by the Great Lakes<br />

Water Quality Agreement (GLWQA) Annex 8 regarding groundwater. The purpose of<br />

the work was to identify groundwater impacts on the integrity and quality of the waters of<br />

the Great Lakes, evaluate the risk posed by different types of groundwater contaminants,<br />

and identify information gaps and science needs. Surprisingly little information was found<br />

in the peer review literature or government databases regarding direct discharges of contaminated<br />

or uncontaminated groundwater to the Great Lakes. Additional information<br />

regarding contaminated groundwater discharges may exist in consultant reports submitted<br />

to governmental agencies but they are not publically available. Even if all sources of<br />

contaminated groundwater flowing to surface waters of the GLB were known, determining<br />

how much of the contaminants actually pass through the groundwater-surface water<br />

transition zone and into surface water is problematic. Understanding the role and ecological<br />

importance of transition zones was identified as being a crucial part of evaluating<br />

the actual impact of contaminated groundwater discharges. Transition zones can modify<br />

the composition and concentration of groundwater plumes prior to discharging to surface<br />

water but they also can be where adverse ecological exposures occur because they provide<br />

valuable habitat for benthic and interstitial organisms, areas for fish spawning, and thermal<br />

refuge for aquatic life. Overall, road salt, nutrients, urban contaminants and petroleum<br />

products were of greatest ecological concern because of the large quantities released into<br />

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the environment and (in the few studies available) concentrations observed in transition<br />

zones were often higher than fresh water quality criteria for the protection of aquatic life.<br />

Approximately 40 science needs and data gaps were identified, which indicates overall<br />

impacts of contaminated groundwater discharges cannot be precisely determined at this<br />

time. Priorities for future work to help support science-based decision making include: 1)<br />

developing rapid inexpensive site characterization tools that can identify contaminated<br />

groundwater discharges and collect data on the scale needed to accurately predict ecological<br />

and human exposures, 2) determining the ecological value and connectivity of the<br />

transition zone to the overall aquatic ecosystem and its sensitivity to contamination for<br />

use in cost benefit analyses, and 3) integrating contaminant hydrogeology, ecological, and<br />

ecotoxicological studies from the beginning of investigations to ensure critical relationships<br />

and problems are identified.<br />

158 - Factors influencing the accumulation and transport of E.<br />

coli near the shoreline at freshwater beaches<br />

Ming Zhi Wu, Denis M. O’Carroll, Laura J. Vogel, & Clare E. Robinson<br />

Department of Civil and Environmental Engineering, Western University, London,<br />

Ontario, Canada<br />

Greater understanding of the fate and transport of microbial pollutants at the sediment-water<br />

interface of lakes is required to inform beach water quality policy and management programs.<br />

Studies have indicated that foreshore sands at beaches can act as a reservoir of fecal<br />

indicator bacteria (FIB) such as Escherichia coli (E. coli) and subsequently be an important<br />

non-point source of FIB to lake water (e.g. Beversdorf et al., 2007; Ge et al., 2010). This<br />

can result in a beach being posted with a water quality advisory. While prior research has<br />

focused on the mechanisms by which FIB is released to surface water (e.g. Halliday et al.,<br />

2014; Phillips et al., 2014), factors controlling the accumulation of E. coli (and also other<br />

bacteria and colloids) in the foreshore sand is not well understood.<br />

This study focuses on developing a mechanistic understanding of the role of groundwater-lake<br />

interactions (i.e., low-energy lapping waves) in the accumulation and transport of<br />

E. coli in the saturated foreshore sand reservoir of freshwater beaches. Numerical modelling<br />

was conducted utilising the finite element solver COMSOL, and incorporated<br />

groundwater transport, attachment of the bacteria to sand grains (using colloid filtration<br />

theory (Yao et al., 1971)), and microbial die-off. The influence of bacterial, beach and wave<br />

parameters (e.g. beach slope, inland groundwater flow, wave height, bacterial attachment<br />

efficiency) on E. coli deposition is assessed. Sensitivity analyses were conducted under both<br />

steady-state and varying wave conditions. The findings from this study are important in<br />

understanding the impact of groundwater and surface water interactions in the transport<br />

of bacteria, using E. coli as an example, at the sediment-water interface of freshwater lakes.<br />

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149 - Using Sea Water/Groundwater Interaction for Calibration of<br />

Variable-Density Groundwater Flow Model<br />

Steven M. Harris<br />

Conestoga-Rovers & Associates, a GHD Company, Waterloo, Ontario, Canada<br />

A variable-density groundwater flow model was developed using SEAWAT_V4 for a confidential<br />

peninsula site in Puget Sound off of the Pacific Northwest Coast. The model will<br />

aid in evaluating remedial design alternatives to address co-mingled chlorinated solvent<br />

and pH plumes. Salt water bodies surround the peninsula. Salt water, being denser than<br />

fresh groundwater, created naturally occurring sea water distributions in the groundwater<br />

flow system beneath the peninsula. Superimposed on this is a high density plume (HDP)<br />

caused by site releases of high density fluids. The HDP was delineated based on where<br />

specific gravity measurements in groundwater samples were greater than that of typical<br />

sea water. The geochemical composition of groundwater was evaluated to determine the<br />

degree of sea water and groundwater interaction beneath the peninsula and estimate the<br />

natural sea water extent present in groundwater excluding the HDP. The sea water density<br />

distribution was used as a model calibration target, in addition to measured groundwater<br />

elevations beneath the peninsula converted freshwater equivalent heads (FEHs). Calibration<br />

proceeded with initially fresh groundwater throughout the model domain and transient<br />

simulation of inland sea water migration from the salt water bodies to a steady-state<br />

condition. Transient coupled flow and transport was simulated using TDS as the density<br />

solute. Boundary condition inflows and aquifer properties were adjusted so the simulated<br />

density distribution reflected the natural sea water distribution in the absence of the HDP.<br />

The simulated sea water density distribution was then merged with the HDP, and further<br />

model adjustments were made to match the observed hydraulic conditions reflected by<br />

FEHs, groundwater flow directions, and horizontal/vertical hydraulic gradients. Model<br />

calibration involved iterating between the natural sea water distribution as one calibration<br />

target set and the observed hydraulic conditions as a second calibration target set. Matching<br />

both sets of targets improved uniqueness and confidence in the calibrated model.<br />

Sustainability of Groundwater Resources 2<br />

Thursday October 29, 13:00 – 14:40<br />

Chair: Garth van der Kamp<br />

Room: Wagner<br />

202 - The global volume, distribution, and lifespan of young and<br />

old groundwater<br />

Tom Gleeson 1,2 , Kevin M. Befus 3 , Scott Jasechko 4 , Elco Luijendijk 2,5 ,<br />

& M. Bayani Cardenas 3<br />

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1<br />

Civil Engineering, University of Victoria, Victoria, British Columbia, Canada<br />

2<br />

Department of Civil Engineering, McGill University, Montreal, Québec, Canada<br />

3<br />

Department of Geological Sciences, The University of Texas at Austin, Austin, Texas, USA<br />

4<br />

Department of Geography, University of Calgary, Calgary, Alberta, Canada<br />

5<br />

Geoscience Centre, Georg-August-Universität Göttingen, Göttingen, Germany<br />

Groundwater is important for energy and food security, human health, and ecosystems.<br />

Unfortunately, groundwater is being depleted globally impacting agriculture and the environment,<br />

and even causing regional crustal deformation. Groundwater is also part of diverse<br />

earth processes from chemical weathering to ocean eutrophication but groundwater<br />

dynamics are not part of most earth system models. The time since groundwater recharge,<br />

or groundwater age, ranges hugely from days to millions of years, which is important for<br />

groundwater management and the role of groundwater in various earth processes. Yet,<br />

the volume, distribution and lifespan of young groundwater remain unknown. Here we<br />

show that only ~6% of global volume of groundwater is less than fifty years old (0.26 - 4.2<br />

million km 3 ) and that current pumping rates can deplete this young groundwater in less<br />

than fifty years in half the areas heavily irrigated with groundwater. We combine extensive<br />

geochemical, geological, hydrologic and geospatial datasets with numerical groundwater<br />

simulations to derive two consistent and independent estimates of the young groundwater<br />

volume as well as provide the first data-driven estimate of total groundwater volume<br />

(~22.6 million km 3 in the upper 2 km of the crust). Most young groundwater is found in<br />

the first 250 meters underground but is very unevenly distributed across the Earth. The<br />

regions with heavy groundwater irrigation and a


al groundwater model has been developed for the Township aquifer system using MOD-<br />

FLOW modelling code based on a rigorous data gathering and review exercise, and the<br />

model is being used by the Township as a groundwater management tool. The model was<br />

initially developed in 2003 and has been recently updated to incorporate changes to groundwater<br />

extraction, and land development as well as additional hydrogeologic information that<br />

have been gathered since the initial model development. The updated model is now being<br />

used by the Township to determine the long-term availability of groundwater to support<br />

future demand and aquatic needs by evaluating the effects of future municipal extraction<br />

and land use development scenarios on water levels in aquifers, and base flows to aquatic<br />

habitats. These results will be incorporated in landuse planning, and to identify groundwater<br />

management options that will ensure the viability of groundwater as a sustainable long term<br />

water-supply source for the Township in the decades to come.<br />

235 - Evaluating the influence of regional stratigraphic<br />

architecture on hydraulic conductivity variability in Early Silurian<br />

carbonate rock aquifers, Guelph Region, southern Ontario<br />

Elizabeth Priebe 1 , Christopher Neville 2 & Frank Brunton 1<br />

1<br />

Earth Resources and Geoscience Mapping Section, Ontario Geological Survey, Sudbury,<br />

Ontario, Canada<br />

2<br />

S.S. Papadopulos & Associates, Inc., Waterloo, Ontario, Canada<br />

The City of Guelph (City) relies on the underlying Early Silurian carbonate bedrock aquifers<br />

for an average water taking of more than 40 million litres per day. Since 2005, the City<br />

and the Ontario Geological Survey (OGS) have collaborated to improve the local understanding<br />

of the bedrock sequence stratigraphy, biostratigraphy and rock/water geochemistry,<br />

with the motivation that such characterization can provide valuable insight into the<br />

distribution and quality of groundwater resources. The collaboration was initiated at a time<br />

when the City was conducting a 50-year water supply master plan, and future projections<br />

of population growth and water demands indicated that additional or alternative water<br />

sources would be needed. The City has recently updated its water supply master plan, and<br />

future projections once again indicate that additional water supply will be needed.<br />

The main objective of this study is the integration of geological and physical hydrogeological<br />

results from the various collaborative studies. This is being accomplished with the<br />

creation of two separate datasets: the stratigraphic logs for the wells in which hydraulic<br />

tests have been conducted and the associated discrete Kh estimates from those tests. For<br />

the creation of the Kh dataset, the raw displacement data for more than 130 hydraulic tests<br />

have been re-analyzed. Analyses have been conducted using a consistent interpretation<br />

approach to enable a reliable comparison between parameter estimates. Three types of single-hole<br />

hydraulic tests have been analyzed, i) single-hole pumping tests; ii) slug tests; and<br />

iii) packer tests. The packer tests comprise either slug tests or short-term pumping tests<br />

conducted within an interval isolated by straddle packers. The spatial density of hydraulic<br />

testing locations is excellent, as is the vertical distribution of test intervals at the formation,<br />

and at many locations, the member scale. The integration of this large set of high quality<br />

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Kh estimates within the context of the stratigraphic architecture will elucidate the geologic<br />

controls on groundwater resource potential, and assist the City in finding new groundwater<br />

resources in a cost effective manner.<br />

153 - Arkell Spring Grounds Adaptive Management Program and<br />

Operational Testing Program in Support of Increased Water Taking<br />

R. Freymond & M. Fraser<br />

Stantec Consulting Ltd., Kitchener, Ontario, Canada<br />

D. Belanger<br />

City of Guelph, Guelph Water Services, Guelph, Ontario, Canada<br />

The Arkell Spring Grounds, located east of the City of Guelph in the Township of<br />

Puslinch, is the largest producing well field for the City. The spring grounds consist of<br />

shallow spring collectors, one overburden and five bedrock production wells. Subject to<br />

the conditions of the Arkell Class Environmental Assessment and the existing Permit<br />

To Take Water, the water taking from the bedrock aquifer was proposed to increase from<br />

19,584 m 3 /day to a maximum of 28,800 m 3 /day. The conditions of approval for increasing<br />

the water taking required the City to complete a detailed hydrogeologic study of the Arkell<br />

Spring Grounds and to develop an Adaptive Management Plan (AMP), both of which<br />

were approved by the Ministry of the Environment in 2009.<br />

The AMP is an iterative decision making process that includes assessing the problem, designing<br />

a management plan, implementing the plan and monitoring, followed by evaluating<br />

and adjusting the plan based on the results. The Arkell AMP focuses on the ecosystem health<br />

of Blue Springs Creek, a coldwater stream situated about 2 km to the northeast of the Arkell<br />

Spring Grounds. The AMP was intended to confirm the conclusion of the initial studies:<br />

Blue Springs Creek will not be impacted by the proposed increase in water taking from the<br />

bedrock aquifer system. The AMP included detailed ecosystem monitoring of Blue Springs<br />

Creek as well as groundwater monitoring conducted over 42 months starting in January<br />

2011. The 42 month monitoring period included 6 months of baseline data collection followed<br />

by 3 years of an Operational Testing Program (OTP) where the bedrock production<br />

wells are pumped at rates as high as 28,800 m 3 /day for extended periods of time.<br />

The use of the AMP allowed continuous re-evaluation of the monitoring program<br />

throughout the regulatory process in an effort to optimize the program by allocating resources<br />

to areas that were most informative. The results of the first two years of the OTP<br />

indicated no impact to the Blue Springs Creek Ecosystem as a result of pumping at the<br />

conditional testing rate of 26,957 m 3 /day. Through the AMP process, the testing program<br />

was re-evaluated resulting in the removal of a pumping rate limiting condition in<br />

the PTTW so that the full permitted pumping rate (28,800 m 3 /day) could be tested, thus<br />

accelerating project implementation.<br />

The talk will focus on the results of the Arkell Spring Grounds AMP and OTP while<br />

highlighting the use of the AMP to accelerate project implementation while avoiding unneeded<br />

study.<br />

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294 - The impact of climate change on the sustainability of<br />

municipal water supplies and groundwater / surface water<br />

interactions<br />

Paul Y.S. Chin<br />

Matrix Solutions Inc., Breslau, Ontario, Canada<br />

Dave Belanger<br />

City of Guelph, Guelph, Ontario, Canada<br />

The City of Guelph is one of the largest municipalities in Canada to rely almost entirely<br />

on groundwater for its potable water supply. The municipal supply system currently includes<br />

21 operational groundwater wells and the Arkell Spring Grounds “Glen Collector”<br />

system, which collects shallow groundwater through a series of underground perforated<br />

pipes. To enhance the supply of water into this collection system, the City operates the<br />

Eramosa River intake and an artificial recharge system at the Spring Grounds. Water is<br />

pumped from the Eramosa River into an infiltration pond and trench where it replenishes<br />

groundwater supplies.<br />

The City has recently completed a Tier Three Water Quantity Risk Assessment that assessed<br />

source water sustainability under future water demand, future land use development,<br />

and drought conditions. A watershed-scale hydrologic model (GAWSER) and a regional-scale<br />

groundwater flow model (FEFLOW) were developed for the study and used to<br />

evaluate water budgets under 45 years of historical climate conditions. The drought assessment<br />

used historical conditions as a surrogate to simulate future drought risk.<br />

The impact of potential climate change on the sustainability of municipal supplies has<br />

been assessed using the Tier Three models. Changing flow conditions in the Eramosa<br />

River, and the subsequent impact on the artificial recharge system’s ability to supply<br />

groundwater to the Glen Collector were examined. Groundwater recharge under changing<br />

climate conditions and the effect on groundwater / surface water interactions were also<br />

evaluated. This study provides insights that will assist in the operation and management<br />

of the municipal supplies.<br />

Innovation in the Remediation of<br />

Contaminated Sites 3<br />

Thursday October 29, 13:00 – 14:40<br />

Chair: Jason Gerhard<br />

Room: Schubert<br />

212 - Full Scale Application of In Situ STAR to Treat Residual Coal Tar<br />

Michaye McMaster, Len DeVlaming, Danielle Thorson & Gary Wealthall<br />

Geosyntec Consultants, Guelph, Ontario, Canada<br />

Grant Scholes, Dave Major, & Gavin Grant<br />

Savron Solutions, Guelph, Ontario, Canada<br />

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This presentation will provide an overview of the on-going full scale application of<br />

Self-Sustaining Treatment for Active Remediation (STAR) to treat soils at a former<br />

cresol manufacturing facility in New Jersey. The remedy objective is to remove residual<br />

free product to the extent practicable. Non aqueous phase liquid (NAPL) smoldering is<br />

different from existing thermal remediation techniques. NAPL smoldering aims to create<br />

a combustion front that (i) initiates at a single location with the NAPL-occupied porous<br />

medium, (ii) is initiated with a one-time, short-duration energy input and not continuous<br />

application of energy, and (iii) destroys the NAPL wherever the front passes. Two successful<br />

pilot tests were previously conducted. These pilot tests were conducted to evaluate<br />

key design parameters such as: contaminant mass destruction rates; treatment radius of<br />

influence (ROI); and, vapor emissions levels. A feasibility and sustainability evaluation<br />

was conducted and STAR was selected as the remedy for on-site soils. A detailed high<br />

resolution site characterization program was completed to confirm the treatment area and<br />

to more accurately delineate the areas for treatment (i.e., NAPL). In 2014 site preparations<br />

were completed and the first treatment train was designed and built. TarGOST®<br />

and confirmatory borings indicate that upwards of 900 tons of residual NAPL exist at the<br />

site. STAR treatment began in late 2014 and is estimated to require 2 years to treat the<br />

free product NAPL. The presentation will provide an overview of the STAR process, the<br />

NAPL estimation methodology and discuss the activities to date in this multiyear remediation<br />

program. Advanced site characterization tools are vital for evaluating and refining<br />

the total treatment area and focusing innovative remediation technologies to where success<br />

can be achieved.<br />

284 - Two-Dimensional Numerical Modelling of STAR to Optimize<br />

Smouldering Combustion for NAPL Remediation<br />

Rebecca L. Solinger, & Jason I. Gerhard<br />

Dept. of Civil and Environmental Engineering – The University of Western Ontario,<br />

London, Ontario, Canada<br />

Gavin Grant<br />

Savron, Guelph, Ontario, Canada<br />

“Self-sustaining Treatment for Active Remediation” (STAR) is an emerging technology<br />

for the remediation of soils impacted with non-aqueous phase liquids (NAPLs). STAR<br />

uses energy generated from an exothermic combustion reaction to propagate a self-sustaining<br />

smouldering front through contaminated soil, leaving soil behind the front effectively<br />

remediated. The approach is being applied in pilot tests and at full scale for both in situ and<br />

ex situ applications. A two-dimensional in situ smouldering model (ISSM) was developed<br />

by MacPhee et. al (2012) to simulate the propagation of the smouldering front during<br />

STAR. Hassan (2013) then calibrated the ISSM to data from bench-scale experiments,<br />

providing confidence that the model predicted both the spreading pattern and ultimate<br />

extinction of the front in two dimensions. The model uniquely combines a multiphase<br />

flow simulator, which predicts the evolving air velocity field as remediation occurs, with<br />

an analytical combustion spread model that tracks the complex smouldering front while<br />

accounting for soil and contaminant heterogeneity. This work is applying the ISSM to<br />

112 IAH-CNC 2015 WATERLOO CONFERENCE


study the sensitivity of large scale, commercial applications of STAR to site conditions<br />

and system design parameters. One study, focused on in situ applications, is calibrating the<br />

model to a field pilot test which will then be used for sensitivity simulations that are exploring<br />

permeability, coal tar saturation, injected air pressure, and location of the air injection<br />

well screen to study the effect on the speed and ultimate extent of remediation. A second<br />

study, focused on ex situ applications, is evaluating the influence of reactor design and soil<br />

mixing heterogeneity on the success of batch treatment of excavated soils by STAR. In<br />

partnering with Savron, the company that is commercializing the STAR technology, the<br />

findings of this work will enhance the optimization of STAR for rapid and cost effective<br />

soil remediation, as well as help identify limits to its application.<br />

164 - Feasibility of Liquid Phase Metallic Catalyzed Reductive<br />

Hydrodechlorination of 1,2-DCA by Sodium Borohydride as<br />

Hydrogen Donor<br />

Omneya El-Sharnouby 1 , Denis M. O’Carroll 1, 2 , Jose Herrera 1 , & Hardiljeet Boparai 1<br />

1<br />

Department of Civil and Environmental Engineering- Western University, London,<br />

Ontario, Canada<br />

2<br />

School of Civil and Environmental Engineering, University of New South Wales, Manly<br />

Vale, New South Wales, Australia<br />

1,2-Dichloroethane (1,2-DCA, C 2<br />

H 4<br />

Cl 2<br />

), a probable human carcinogen, is a chlorinated<br />

organic compound (COC) used for the synthesis of vinyl chloride. Due to improper handling,<br />

storage and/or disposal, it has caused widespread subsurface contamination. Chemical<br />

reduction by nano zero valent iron or bimetallic particles systems has been reported<br />

to be capable of degrading many COCs. However, although thermodynamically feasible,<br />

to date metal based reduction of 1,2-DCA has not been shown. Gas phase catalyzed reductive<br />

hydrodechlorination is reported to effectively dechlorinate a wide variety of COCs<br />

including 1,2-DCA using hydrogen gas as reductant, and catalysts for hydrogen activation<br />

and reaction surface. However, the process is carried out at high temperatures (+200 º C),<br />

making it impractical for contaminated field sites applications. Recently, liquid phase catalyzed<br />

reductive hydrodechlorination has emerged as a field applicable technology showing<br />

promising results in reducing COCs. Nonetheless, bench scale studies lack information on<br />

liquid phase catalyzed hydrodechlorination of 1,2-DCA. Therefore, in this study the feasibility<br />

of liquid phase catalyzed reductive hydrodechlorination of 1,2-DCA using sodium<br />

borohydride as a hydrogen source over different catalysts is investigated. Using the gas<br />

phase hydrodechlorination process as an example, Pd, Cu, Cu/Pd, and Ni, were the chosen<br />

catalysts. For the first time, effective liquid phase hydrodechlorination of 1,2-DCA on Pd<br />

and Ni is achieved. 1,2-DCA degradation profiles, and reaction kinetics are explained.<br />

Mechanisms and products are discussed along with likely degradation pathways. Effect of<br />

the different catalysts on the degradation efficiency as well as the different loadings, and<br />

formulations are also presented.<br />

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296 - In-Situ Subsurface Remediation of Tetrachloroethylene<br />

(PCE) Using Soil Mixing Technology with Zero-Valent Iron (ZVI)<br />

and Clay<br />

Sarah Cicchini<br />

Golder Associates Ltd., Edmonton, Alberta, Canada<br />

David Smyth<br />

Golder Associates Ltd., Mississauga, Ontario, Canada<br />

Michelle Gray<br />

Aboriginal Affairs and Northern Development Canada, Edmonton, Alberta, Canada<br />

This paper describes the use of soil mixing technology with bentonite clay and zero-valent<br />

iron (clay/ZVI) technology for the in situ remediation of tetrachloroethylene (PCE) contamination<br />

in a subsurface setting of fractured silty clay overlying weathered shale bedrock.<br />

The subsurface contamination was present beneath a former municipal wastewater treatment<br />

lagoon at the Whitefish Lake First Nation #128 in northern Alberta. The lagoon,<br />

which was situated in close proximity to a shallow lake, had received much of an accidental<br />

release of PCE from a local dry cleaning operation in the early 1980s. As part of the<br />

decommissioning of the municipal wastewater treatment plant, which was completed in<br />

2010, subsurface investigation was undertaken in the vicinity of the lagoon between 2008<br />

and 2011.<br />

PCE and its related degradation compounds were present at high concentrations in soil<br />

and groundwater beneath and in the vicinity of the lagoon. The maximum concentrations<br />

of PCE were 8,900 mg/kg in soil and 170 mg/L in groundwater. The depths of contamination<br />

ranged from the base of the lagoon to as much as 9 metres below ground surface<br />

(mbgs) beneath the former lagoon, and between depths of approximately 2 and 5 mbgs<br />

beyond the limits of the former lagoon.<br />

The selection of remedial actions was influenced by distance to secure landfill facilities and<br />

the intent to return the site of the lagoon to vacant green space. Bench-scale treatability<br />

tests at the Colorado State University using a 2 % ZVI and 1 % bentonite mixture by mass<br />

in site soil indicated PCE removal of between 87 and 93 % after six months. The full-scale<br />

soil mixing program was implemented in 2012. It consisted of the advancement of 306<br />

overlapping mixed soil columns (~2.4 m diameter) to depths between 5 to 9 mbgs, and the<br />

mixing of approximately 7,450 m 3 of soil. To accommodate the swelling of the mixed soils,<br />

a perimeter containment berm was constructed around the mix zone.<br />

Post-mixing monitoring of the soil in the mix zone since 2013 has indicated the loss of<br />

approximately 97% of the PCE, stable to decreasing concentrations of trichloroethylene,<br />

dichloroethylene and vinyl chloride, some variability in concentrations of cis-1,2-dichloroethylene,<br />

and an initial increase in concentrations of chloride. Shallow groundwater flow<br />

has appeared to by-pass the treatment area, with limited groundwater flow into and out of<br />

the soil mix zone. Capping and surface stabilization of the mix zone are planned for 2014.<br />

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173 - Field trials of subsurface chaotic advection<br />

Michelle S. Cho & Neil R. Thomson<br />

Department of Civil & Environmental Engineering – University of Waterloo, Waterloo,<br />

Ontario, Canada<br />

Chaotic advection refers to the mixing of fluid elements which arise from repeated stretching<br />

and folding of fluid parcels. Chaotic advection can be engineered in porous media<br />

by time-dependent Darcy flows and has the potential to enhance mixing under laminar<br />

conditions. Enhanced mixing has many possible applications in environmental science and<br />

engineering. Remediation of contaminated aquifers is particularly relevant where mixing<br />

between the injected reagent and contaminant is necessary. If chaotic advection can be<br />

stimulated and controlled in situ, remediation efficiencies may be significantly increased<br />

by enhanced mixing between the injected reagents and contaminants. To assess whether<br />

chaotic advection can be invoked at scale in a natural porous medium, a field trial has been<br />

designed in the sandpit area at the University of Waterloo Groundwater Research Facility<br />

at CFB Borden located near Alliston, ON, Canada, where we propose to use a transient<br />

reoriented dipole flow for subsurface stirring. A 3 m x 10 m zone in the aquifer has been<br />

isolated by sheet piling penetrating 2 m below ground surface. A funnel and gate system<br />

is in place to assess remedial technologies. In the initial phase, we propose to study the<br />

behaviour of conservative tracers within the aquifer with undisturbed and chaotic groundwater<br />

flows. Focus will then move to the treatability of a light non-aqueous phase liquid<br />

(LNAPL) source zone by injected reagents under chaotic and non-chaotic conditions.<br />

An LNAPL will be released under controlled conditions and then allowed to redistribute<br />

under gravity, forming a residual LNAPL distribution with the vicinity of the water table.<br />

This presentation will describe the design criteria associated with the various aspects of this<br />

field trial, and present modeling results for determination of key flow system parameters<br />

as well as field data from the tracer test to suggest the presence of chaotic advection in the<br />

experimental aquifer.<br />

Groundwater Issues from Mining<br />

& Aggregates<br />

Thursday October 29, 13:00 – 14:40<br />

Chair: Simon Gautrey<br />

Room: Heritage<br />

134 - Protecting water resources with a groundwater recharge<br />

well system at the Dufferin Aggregates Milton Quarry<br />

J. Richard Murphy, William T. Armes, & P. Nicholas Fitzpatrick<br />

GHD (formerly Conestoga-Rovers & Associates), Waterloo, Ontario, Canada<br />

A sophisticated and extensive Groundwater Recharge Well System (GRWS) has been<br />

successfully implemented for the protection of water resources at the Dufferin Aggregates<br />

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Milton Quarry. This system is a unique application of recharge well technology to achieve<br />

hydrogeologic mitigation of quarry dewatering effects in a sensitive ecological environment.<br />

Dufferin Aggregates owns and operates one of the largest aggregate quarries in Canada, near<br />

Milton, in southwestern Ontario. At the Milton Quarry, aggregate resources are extracted<br />

from the caprock of the Niagara Escarpment (dolostone of the Amabel/Gasport Formation)<br />

and processed to produce a range of high‐quality crushed stone products. The same dolostone<br />

formation comprises a shallow unconfined aquifer that supports nearby water supply<br />

wells, cold water fisheries, and wetlands, including vernal pools used for breeding by the<br />

Jefferson Salamander Complex which is protected under the Endangered Species Act.<br />

In 2007 an Extension of the Quarry was approved by the Province of Ontario including the<br />

requirement to implement the GRWS to maintain groundwater levels surrounding the Extension<br />

Quarry to prevent negative impacts that might otherwise occur as a result of quarry<br />

dewatering effects.<br />

GHD conceived and designed the GRWS to protect water resources and associated ecological<br />

features in the area of the Milton Quarry from the quarry dewatering influence. This was<br />

a new approach to environmental mitigation for the aggregate industry; in fact, no comparable<br />

example could be found anywhere in the world. The GRWS was critical to the success of<br />

the approval of the Extension Quarry.<br />

The GRWS has been fully constructed and has been operational since 2007. The GRWS<br />

forms part of an overall water management system comprised of a reservoir, dedicated pumping<br />

stations, buried watermains, build-out to over 100 recharge wells, 3 diffuse discharges<br />

to wetlands, and an Adaptive Management Plan (AMP) that provides the mitigation and<br />

monitoring framework. The AMP involves extensive monitoring including on-line data reporting<br />

for access by oversight agencies.<br />

The GRWS has proven to be effective in mitigating the quarry dewatering effects on nearby<br />

water resources and maintaining pre-determined seasonally-varying target groundwater<br />

levels. Ecological monitoring has demonstrated that there have been no detrimental effects<br />

to the nearby water resources and associated ecological features from the ongoing expansion<br />

of the quarry.<br />

The combination of the technical approach and the Adaptive Management Plan makes Dufferin’s<br />

Milton Quarry a showpiece of environmental protection for the aggregate industry.<br />

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282 - Evaluating mining impacts on groundwater quality in Lake<br />

Poopó basin, Bolivia using geochemical and isotope tracers<br />

Sylvia Barroso 1 , Ronald Zapata 2 & Ramon Aravena 3<br />

1<br />

BC Ministry of Forests, Lands and Natural Resources, Nanaimo, British Columbia, Canada<br />

2<br />

Department of Engineering – University of San Francisco Xavier, Sucre, Bolivia<br />

3<br />

Department of Earth & Environmental Sciences – University of Waterloo, Waterloo,<br />

Ontario, Canada<br />

Historical and present mining activities have seriously impacted water quality in the Bolivian<br />

Altiplano (High Plain). The environmental effects of mining in the Poopó River<br />

and Antequera River sub-watersheds of the Lake Poopó Basin were considered, along<br />

with physiography, geology, and mine waste management. Stable isotopes, 18 O and 2 H in<br />

water, and 34 S and 18 O in sulfate complemented with chemical data were used to evaluate<br />

the impacts of mine tailings in groundwater. In the Poopó River watershed, tailings leachate,<br />

and slurry from the refinement of zinc and lead ore was held in a ~5 hectare tailings<br />

impoundment situated at the apex of a colluvial fan, and isolated from the adjacent river.<br />

In the Antequera River watershed, a >10 ha tailings reservoir was located within the river<br />

channel, creating a dilute acidic (pH 2) mixture of precipitation and wastewater. As a result<br />

of evaporation, the isotopic composition of water in the tailings impoundments was higher<br />

than in groundwater and surface water. Springs, rivers, and shallow groundwater had an<br />

average isotopic composition of -13‰, and -100‰ for δ 18 O and δ 2 H, respectively. Water<br />

isotopes in groundwater from drilled wells were lower (median δ 18 O=-15‰, and δ 2 H=-<br />

110‰), originating from recharge at higher elevation. Stable isotopes of sulfate combined<br />

with geochemical data were useful indicators of mixing between polluted and ambient<br />

waters. In comparison to other sources, tailings samples had a very negative sulfate isotope<br />

composition with average values of -5‰ and -12‰ for δ 34 S and δ 18 O, respectively. Water<br />

sources impacted by mine waste had lower sulfate isotope composition and higher concentrations<br />

of cadmium and other trace metals. In Poopó impacts were evident in shallow<br />

groundwater adjacent to the tailings pond. In Antequera, impacts of leachate from the<br />

impoundment were noted at distance in down gradient groundwater and surface waters.<br />

Options for provision of fresh water in this region are limited. Groundwater in drilled wells<br />

contained elevated, naturally occurring, boron, aluminum and arsenic; while shallow dug<br />

wells were contaminated by natural and anthropogenic pollutants, including tailings leachate<br />

and evaporite salts. Sources of uncontaminated water were low temperature springs and<br />

creeks at higher elevation, upstream of industrial activities and human settlements.<br />

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171 - Evaluating the Effects of Increased Lithium Brine<br />

Extraction from the Salar de Atacama: Conceptual and Numerical<br />

Groundwater Models<br />

Mark King<br />

Groundwater Insight, Inc., Canada<br />

Steve Shikaze<br />

Matrix Solutions Inc., Canada<br />

Hector Maya<br />

Rockwood Lithium, Chile<br />

Jaime Solari & Laura Vitoria<br />

SGA, Chile<br />

Most of the world’s lithium reserves occur in dry salt lakes (salars) located in a section of<br />

the high Andes near the common borders of Chile, Argentina and Bolivia. Almost all of<br />

the current lithium production from this region originates from two companies operating<br />

in the Salar de Atacama. One of these companies, Rockwood Lithium, is currently seeking<br />

government approval to increase its brine production rate. This paper provides an overview<br />

of conceptual and numerical groundwater models constructed to evaluate the potential<br />

impacts of this proposed increase in brine extraction.<br />

The Salar de Atacama is located in an extreme desert environment, with annual precipitation<br />

of less than 50 mm/yr. The lithium-containing brine is located under the flat surface<br />

of the salar, in a porous evaporite matrix. The nucleus of the salar contains brine with as<br />

much as ten times the dissolved solids content of seawater. Meanwhile, subsurface waters<br />

in the outer border areas of the basin are relatively fresh, and are used as a freshwater<br />

resource. A key environmental feature of the Salar de Atacama are the shallow border lagoons,<br />

which are an important breeding habitat for migratory flamingoes. Consequently, a<br />

key criteria for any increase in brine pumping rates is that the water levels in these shallow<br />

border lagoons remain unaffected.<br />

In this environment of extreme salinity contrasts, the effects of increased brine pumping<br />

were evaluated with the numerical model SEAWAT. This numerical code has the capability<br />

of simulating density-dependent flow, which is a key process in the salar border area,<br />

where there is an interface between subsurface brines and saline to fresh waters. In this<br />

evaluation, local-scale SEAWAT models were coordinated with a regional-scale, flow-only<br />

MODFLOW model. This paper presents an overview of the conceptual and numerical<br />

approaches used to evaluate this unique and complex environment.<br />

131 - A Conceptual Model for Pore Water Release from Coal Waste<br />

Rock Piles in the Elk Valley, British Columbia, Canada<br />

Terryn Kuzyk, S. Lee Barbour, & M. Jim Hendry<br />

Department of Civil and Geological Engineering, University of Saskatchewan, Saskatoon,<br />

Saskatchewan, Canada<br />

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The open pit mining of coal results in the formation of new landforms constructed from<br />

waste rock. Rock drains, either constructed or formed during dumping by natural segregation,<br />

underlie some of these landforms. Constructed rock drains are often designed to convey<br />

surface water from higher in the watershed through the waste rock dumps. Rock drains also<br />

collect water moving through the waste rock and convey it to adjacent surface and ground<br />

water. Long-term monitoring of the chemistry of water conveyed by rock drains provides<br />

an opportunity to characterize the rates of flushing of these constituents through the waste<br />

rock piles. In this study, a conceptual model for the long-term release of nitrate (NO 3<br />

), selenium<br />

(Se), and sulfate (SO 4<br />

) from coal waste rock piles is developed and used to interpret<br />

monitoring data from eleven rock drains of varying ages in the Elk Valley, British Columbia.<br />

The hypothesis of the conceptual model is that the flushing of the first pore volume of water<br />

within the waste rock can be characterized by NO 3<br />

release. The NO 3<br />

is derived from blasting<br />

and is considered to be a conservative species. The first pore volume will also contain SO 4<br />

and<br />

Se generated by oxidation of waste rock during blasting and pile construction. Post-depositional<br />

oxidation and production of SO 4<br />

and Se are identified by the evolution of the effluent<br />

signature from an initial SO 4<br />

/NO 3<br />

ratio, representative of the initial pore fluid at deposition,<br />

to an increasing SO 4<br />

/NO 3<br />

ratio as the initial pore volume is released and Se and SO 4<br />

are<br />

produced by oxidation. This hypothesis is tested by interpreting the patterns of NO 3<br />

, SO 4<br />

,<br />

and Se release as described by SO 4<br />

/ NO 3<br />

and Se/SO 4<br />

ratios. In cases where upstream sources<br />

are contributing to the observed flow and concentrations within the rock drain, an attempt<br />

is made to correct the monitoring data so that it represents only the contribution from the<br />

waste rock overlying the rock drain. The concentrations of NO 3<br />

and SO 4<br />

were found to<br />

correspond to differences in the chronology of waste rock placement, while the Se/SO 4<br />

ratios<br />

were relatively constant and consistent with ratios associated with oxidation. A model of the<br />

evolution of the effluent chemistry was developed using a system dynamics model comprised<br />

of stocks (water storage) and flows (flushing) within blocks of waste rock placed at various<br />

times within a watershed. The model illustrates how stored water volumes, rates of flushing,<br />

production rates, dump chronology, and, where applicable, upstream sources control the<br />

evolution of rock drain chemistry over time. The goal of this work is to develop methods of<br />

evaluating the impact that various dump designs might have on the timing and magnitude<br />

of NO 3<br />

, Se, and SO 4<br />

releases.<br />

110 - Characterisation of physical mass transport through oil<br />

sands fluid fine tailings in an end pit lake: a multi-tracer study<br />

Kathryn Dompierre & Lee Barbour<br />

Department of Civil and Geological Engineering - University of Saskatchewan, Saskatoon,<br />

Saskatchewan, Canada<br />

The first end pit lake in the Athabasca oil sands region has been developed by Syncrude<br />

Canada Ltd. as part of their closure design for the Mildred Lake Mine site, 40 km north of<br />

Fort McMurray. The end pit lake, referred to as Base Mine Lake, was constructed within a<br />

mined-out pit, and incorporates 186 Mm 3 of fluid fine tailings (FFT) below an 8 m water<br />

cap. Fluid fine tailings are a dense fluid with dispersed, suspended solids, residual bitumen<br />

and elevated TDS (Siddique et al., 2007). Chemical constituents of concern may move<br />

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from the FFT into the lake water via two key processes: (1) advective-diffusive mass transport<br />

with upward pore water flow caused by settling of the FFT; and (2) mixing created by<br />

wind events or unstable density profiles through the lake water and upper portion of the<br />

FFT. Assessing the physical movement of constituents of concern across the FFT-water<br />

interface is central to determining the feasibility of isolating FFT from the overlying lake,<br />

and for defining the long-term water chemistry of an end pit lake system.<br />

In September 2013, vertical thermistor strings were installed off of central platforms on<br />

Base Mine Lake to measure seasonal temperatures within the lake water and FFT. In<br />

July 2014, FFT and water samples were taken at 10 cm intervals across the FFT-water<br />

interface. The samples were centrifuged and analysed in the laboratory using the vapour<br />

equilibration technique to determine the stable isotopes of water signatures of the tailings<br />

pore water (Wassenaar et al., 2008). Numerical models were developed in GeoStudio ©<br />

to represent various forms of heat and mass transport through the FFT. The simulation<br />

results were compared to measured temperatures and stable isotopes of water profiles from<br />

Base Mine Lake, to evaluate the dominant form of heat and mass transport in the FFT.<br />

Temperatures within the top 5 m of FFT were affected by seasonal temperature variations in<br />

the lake water, which was measured to range from 0°C to 18°C. Tailings temperatures below<br />

the seasonally-affected zone were consistent throughout the measurement period, with an<br />

average temperature of 10°C. Stable isotopes of water signatures in the FFT pore water were<br />

fairly consistent with average deuterium and oxygen-18 signatures of -112.84 ‰ and -12.66<br />

‰, respectively. The FFT pore water signatures were more enriched than the isotope signatures<br />

measured in the lake, corresponding to findings outlined by Baer (2014).<br />

The heat transport models indicated that mixing occurs within the top portion of FFT in<br />

Base Mine Lake during unstable conditions in the fall. The FFT mixing models suggested<br />

that the dominant form of energy movement through the FFT is a conduction and forced<br />

convection thermal regime with an upward pore water flow of 0.004 m/d or less. Contrary<br />

to the heat transport model results, the isotope profiles created by the mass transport models<br />

without a mixing event provided a reasonable fit to the field data. However, the mass<br />

transport models with a fall mixing event demonstrated that upward pore water flow could<br />

reset the observed isotope profile before the isotope samples were collected in the summer.<br />

Consequently, the isotopic profiles were used to evaluate the mass transport regime required<br />

Workshop on Groundwater Policy 1<br />

Thursday October 29, 13:00 – 14:40<br />

Chair: Steve Wallace<br />

Room: Bloomingdale<br />

144 - Whither Groundwater Policy - Challenges and Opportunities<br />

of a Paradigm Shift?<br />

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Hugh C. Simpson<br />

Ontario Ministry of Agriculture, Food and Rural Affairs, Guelph, Ontario, Canada<br />

School of Environmental Design and Rural Development, University of Guelph, Guelph,<br />

Ontario, Canada<br />

Robert C. de Loë<br />

Department of Environment and Resource Studies, University of Waterloo, Waterloo,<br />

Ontario, Canada<br />

Historically, the development and implementation of groundwater policy has been guided<br />

almost exclusively by expert science and traditional risk analysis. This approach has worked<br />

well for environmental problems that are relatively simple and predictable. Unfortunately,<br />

many of the environmental problems that are being faced by decision makers can be classified<br />

as complex problems.<br />

Examples include the management and protection or groundwater resources. Complex environmental<br />

problems are a particular challenge because they are ‘quasi-scientific’, requiring<br />

more than scientific knowledge needs to be considered during the problem-solving process.<br />

Current research indicates that a broader and more inclusive risk analysis approach is needed<br />

for addressing complex environmental problems. A key part of this broader approach<br />

is involving members of affected communities so that local experiential knowledge, and<br />

societal beliefs and values, can be incorporated with expert science during the discussion<br />

and negotiation of solutions to complex problems. This is a difficult challenge for the<br />

expert science community, and requires a shift from the inwardly-focused traditional approach<br />

to a more open and inclusive process for groundwater policy development and<br />

implementation.<br />

This paper explores elements of the paradigm shift that appears to be taking place in the<br />

development and implementation of groundwater policy. First, the criteria that qualify<br />

groundwater management and protection as a complex environmental problem are presented.<br />

Second, an alternative to the traditional approach – collaborative environmental<br />

problem-solving – is discussed. Finally, some examples of how collaborative environmental<br />

problem-solving is being implemented into groundwater policy are presented.<br />

124 - Implementing Source Protection in York Region<br />

Scott Lister<br />

York Region, Newmarket, Ontario, Canada<br />

This talk will discuss the preparation for implementation of Part IV of the Clean Water<br />

Act’s source water protection requirements in York Region. This will include a discussion<br />

of tools and techniques used to identify, investigate and manage over 1,000 water quality<br />

threats to drinking water sources in York Region, Ontario, focusing on protection of forty-one<br />

municipal drinking water wells. Threats were investigated using several methods<br />

of outreach, including site visits with business owners and farmers to complete surveys.<br />

Generally speaking, under the proposed Source Protection Plans existing threats must be<br />

managed using Risk Management Plans (RMPs), while proposed activities that would be<br />

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significant threats are prohibited. Two existing threat activities conducted by York Region<br />

require a Risk Management Plan, and a few others are governed by an Environmental<br />

Compliance Approval. In such cases, those approvals will be amended to include conditions<br />

to mitigate water quality risks. While waiting for Source Protection Plans to be<br />

approved the Region has negotiated interim Risk Management Plans (iRMPs) with a<br />

number of businesses and farmers, and itself! To facilitate RMP negotiation, a DNAPL<br />

template was developed with the assistance of a DNAPL expert in order to easily list<br />

threats on-site, existing mitigation measures already in place, and potential gaps. The expert<br />

developed a list of risk management measures to ensure threats on-site cease to be significant<br />

threats. York Region also ran a pilot project with an agricultural expert to develop<br />

an iRMP for a farm. The agronomist, who is also a certified crop advisor, was hired by York<br />

Region to assess the farm’s drinking water threats, current risk management measures, and<br />

to propose new risk management measures in the iRMP to ensure the identified activities<br />

cease to be a significant threat. A Council approved incentive funding program has also<br />

been established to subsidize the cost of risk management measures and foster relations<br />

with affected business owners and farmers.<br />

216 - Source Water Policy Implementation and Application of<br />

Source Water Protection Models<br />

Tom Bradley, Don Goodyear, & Mike Fairbanks<br />

York Region, Newmarket, Ontario, Canada<br />

The Province of Ontario introduced the Clean Water Act in 2006 to implement Source<br />

Water Protection (SWP) of municipal drinking water supplies. The program safeguards<br />

the quality and quantity of municipal drinking water to ensure it is viable in the future.<br />

Approval of Source Protection Plans and their associated policies require government<br />

agencies and consultants to apply tools such as numerical models. This talk will focus on<br />

the current and the future applications of the numerical models developed for the York<br />

Region Tier 3 Water Budget.<br />

York Region provides drinking water to a population of over a million, and is growing.<br />

Water demand associated with the large and expanding population triggered a Tier 3 water<br />

quantity risk assessment. The models developed for the Tier 3 benefited from York Region’s<br />

participation in the York, Peel, Durham and Toronto (YPDT) groundwater management<br />

partnership. The YPDT databases and numerical model were built upon for the<br />

Tier 3 project and the resulting model is a USGS, GSFLOW transient model, a coupled<br />

surface water/groundwater model.<br />

Source Protection Plans (SPP) developed policies that are specific to York Region and ensure<br />

the moderate risk assigned to its WHPA-Q1 never become a significant risk. In order to<br />

maintain the moderate risk assignment the policies require planning and approval agencies<br />

to consider model results when making decisions related to water quantity management. To<br />

be pro-active, prior to implementation of the policies, York Region applied the Tier 3 models<br />

to address policies focusing on potential recharge reductions. The Region developed a model<br />

scenario that evaluated potential impacts associated with increases to impervious, urban area.<br />

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York Region has also begun projects that will permit Region use of the Tier 3 model for<br />

updates to York Region capture zones (Well Head Protection Areas). The work includes,<br />

sensitivity assessments, model updates, and assessment of hydrogeologic assumptions used<br />

in earlier capture zone delineation projects. In addition to implementing Source Protection<br />

Plan policies, York Region developed an operational plan to redistribute water taking and<br />

mitigate predicted impacts of extreme drought (climate change).<br />

The Tier 3 models have provided York Region and its partners, insight into the municipal<br />

supply aquifers. They have highlighted potential water management issues and provided<br />

collaboration opportunities between water managers and planning authorities. Continued<br />

application of the York Region Tier 3 models, as a result of SWP policies, will improve the<br />

models and improve the understanding of local groundwater resources.<br />

183 - Development of a Risk Reduction Process to address<br />

Groundwater Safety in Northern Canada<br />

N.S. Sundaram, J. Sauriol & J.P. Gobeil<br />

Stantec Consulting Ltd., Ottawa, Ontario, Canada<br />

A drinking water system that obtains water from a groundwater source may not require<br />

secondary disinfection, particle filtration, removal of dissolved organics, and other water<br />

treatment techniques, as the aquifer supplying the water may be able to provide sufficient<br />

natural filtration. Because of the significant human health issues associated with drinking<br />

water supply potability, development of a risk reduction process to evaluate aquifer safety<br />

is required. The standard risk reduction process involves the installation of test wells in the<br />

supply aquifer and observation wells between the test wells and nearby surface water bodies,<br />

based on published information from the provincial ministries with respect to aquifer geometry,<br />

geology, and hydrology. The application of this standard process to some northern<br />

Canadian environments introduces significant scientific uncertainties, owing to the lack of<br />

published information at a scale suitable for the application of standard practice, and to the<br />

potential presence of discontinuous groundwater flow regimes resulting from northern geology<br />

and/or significant frost/permafrost presence. Therefore, development of an improved<br />

risk reduction process to address groundwater safety in Northern Canada was considered.<br />

Our approach to the development of an improved risk reduction process comprised of<br />

integrating multiple independent lines of evidence to arrive at a defensible conclusion. In<br />

order for our approach to show potential, at least two lines of evidence needed to confirm<br />

each other. A highly defensible approach would require confirmation from all three lines<br />

of evidence. We have applied this altered risk reduction process to a site located within<br />

the vicinity of Val-d’Or, Quebec. For the subject site discussed in this paper, we have<br />

applied a multi-pronged approach that comprised of assessing several independent lines of<br />

evidence simultaneously (i.e., application of environmental tracer chemicals [Chlorofluorocarbons<br />

(CFCs), Sulfur Hexafluoride] to groundwater age, identification of microscopic<br />

surface water-borne organisms to determine surface water intrusion, and hydraulic testing<br />

to determine aquifer properties) to overcome the uncertainties that are unique to Northern<br />

Canadian environment.<br />

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Groundwater Issues From Oil and Gas<br />

Exploration & Production 2<br />

Thursday October 29, 15:00 – 16:40<br />

Chair: Dick Jackson<br />

Room: Strauss<br />

220 - Injection Wells in the Western Canada Sedimentary Basin<br />

Grant Ferguson<br />

Department of Civil and Geological Engineering – University of Saskatchewan, Saskatoon,<br />

Saskatchewan, Canada<br />

Over 23 km 3 of water has been injected into the Western Canada Sedimentary Basin<br />

(WCSB). The amount of injection has increased in recent years with the advent of hydraulic<br />

fracturing, various enhanced oil recovery techniques and the growth in potash production.<br />

Despite this large volume of injection, few negative effects have been definitively<br />

reported. Contamination of shallow groundwater resources has not been documented at<br />

a large-scale. Links between seismicity and injection have been made in only a few cases.<br />

The dearth of consequences may indicate that there are in fact few to document. Alternatively,<br />

existing research and monitoring efforts may not be sufficient to record the effects of<br />

injection. Here, known effects of injection are characterized and research and monitoring<br />

gaps are identified. Understanding the reasons for the apparent success of most injection<br />

wells in the WCSB is important not only to the continued development of that basin but<br />

also to support development of other sedimentary basins where there is little to no experience<br />

with injection wells.<br />

267 - Assessing water quality of shallow groundwater near a<br />

tailings pond in the Athabasca oil sands region<br />

J.W. Roy, G. Bickerton, R.A. Frank, L. Grapentine, & L.M. Hewitt<br />

Water Science and Technology Directorate, Environment Canada, Burlington, Ontario,<br />

Canada<br />

Oil sands process-affected water (OSPW) contains a complex mixture of neutral and polar<br />

organic compounds, including naphthenic acids, as well as elevated levels of many metals<br />

and major ions. Many of these are toxic to aquatic life. Thus, the potential for leakage of<br />

OSPW from tailings ponds to groundwater and subsequent transport of OSPW-affected<br />

groundwater to nearby surface waters is an environmental concern. However, unaffected<br />

groundwaters in this area may contain similar mixtures, with possible inputs from several<br />

geological formations, including one containing natural oil sands. This complicates the<br />

assessment of groundwater quality and potential ecological impacts from tailings ponds.<br />

In this study, we attempted such an assessment for an old tailings pond on the edge of the<br />

Athabasca River using relatively-routine chemical analyses. Over 3 years, >180 shallow<br />

groundwater samples were collected from riparian areas along the Athabasca River and<br />

nearby tributaries proximate to oil sands developments, with analyses for major ions, trace<br />

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metals and fluorescence profiles of aromatic naphthenic acids (ANA). Within this data set,<br />

71 were collected adjacent to our study tailings pond (called “pond-site” samples), while<br />

54 were not near any tailings pond (called “non-pond” samples). Canadian aquatic life<br />

guidelines were exceeded for about half of the 20 assessed compounds for both of these<br />

sets of samples. Indeed, statistical analyses indicate that non-pond samples were indistinguishable<br />

from, or had higher concentrations than, the pond-site samples for all of the<br />

assessed parameters, except for F, Mo, Se, and U. This suggests that at this time shallow<br />

groundwater adjacent to this study tailings pond generally poses no greater risk to aquatic<br />

life than other shallow groundwaters in the area. Multivariate analyses were also applied to<br />

the full groundwater dataset separated spatially into 11 smaller zones, including 4 adjacent<br />

to the study pond, and 2 OSPW samples from nearby tailings ponds. For the majority of<br />

the parameters, there was considerable overlap in the data from different zones, including<br />

those near the study pond and away from the pond. However, consideration of a set of<br />

indicator parameters, including ANA, F, Mo, Se, and Na–Cl ratio, revealed a similarity between<br />

a small subset of samples (


259 - Assessment of Non-saline Water Use in Alberta’s Upstream<br />

Oil and Gas Sector between 2004 and 2013: Implications on<br />

Forecasted Water Use<br />

T.G. Lemay<br />

Alberta Energy Regulator, Edmonton, Alberta, Canada<br />

The extraction of hydrocarbons from Alberta’s subsurface relies heavily upon non-saline<br />

water resources. This water is used in drilling wells, completing wells using techniques<br />

such as hydraulic fracturing, enhancing recovery through water flooding, processing oil<br />

sands ore, and generating steam for in situ oil sands extraction. Over the 2004 to 2013<br />

time period, many changes have occurred in the upstream oil and gas sector in Alberta<br />

that have influenced non-saline water use in the extraction of hydrocarbons. Many of these<br />

changes in non-saline water use are related to the changes in the type of exploration and<br />

production activities being undertaken by upstream oil and gas companies, many of which<br />

are driven by the transition towards a mature basin, changing commodity prices for oil and<br />

natural gas and the fiscal realities of project economics. The shift from drilling predominantly<br />

vertical natural gas wells to drilling horizontal wells targeting liquid hydrocarbons,<br />

and the continued growth in oil sands mining and in-situ oil sands extraction has meant<br />

that non-saline water use has changed over time as well in response to Alberta’s oil and<br />

gas landscape. Our assessment of non-saline water use yielded results that show increases<br />

between 2004 and 2013 by 54% compared to total non-saline water use in 2004. The<br />

largest user of non-saline water in the upstream oil and gas sector is the oil sands mining<br />

sector accounting for 67 to 80% of total non-saline water used. The second largest user<br />

of non-saline water was the enhanced recovery sector, but only during the 2004 to 2008<br />

time period. After 2008, the enhanced recovery sector became the third largest user of<br />

non-saline water. The use of non-saline water for in-situ oil sands extraction represents the<br />

third largest use of non-saline water between 2004 and 2008, and the second largest use of<br />

non-saline water between 2009 and 2013. Non-saline water use for drilling represents the<br />

fourth largest use, and non-saline water in hydraulic fracturing was identified as the smallest<br />

user. The realities of Alberta’s maturing basin, changing commodity prices and project<br />

economics will continue to influence the future of non-saline water use. The relationships<br />

between trends in exploration and development and water use can therefore enable general<br />

estimates of future non-saline water use based on project development scenarios aiding in<br />

the identification of current and future demands for water in Alberta.<br />

303 - Creation of a comprehensive database to characterize<br />

surface and groundwater quality in the Peace River Regional<br />

District, North East BC, Canada<br />

Antonio Barroso & Gilles Wendling<br />

GW Solutions, Nanaimo, British Columbia, Canada<br />

The Peace River Regional District (PRRD) in northeastern British Columbia encompasses<br />

12 million hectares and is well known for the intensive activity of the oil and gas industry.<br />

Currently there are many entities including private consultants, non-governmental<br />

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organizations and government agencies collecting water samples from both surface water<br />

and groundwater sources. However, this information had not been incorporated into a<br />

comprehensive database that could be used to characterize sites and to evaluate the possible<br />

impact of the industry on water quality. A common approach is to collect new data, without<br />

necessarily taking into account historical records, or information collected by other<br />

entities. Additionally, obtaining reliable information on ambient or background conditions<br />

is difficult, because of the decades long history of industrial activities throughout the<br />

region. A database was developed for the PRRD that compiled existing information on<br />

surface water and groundwater quality. Nearly 12,000 samples from 364 monitoring sites<br />

were incorporated to characterize surface water chemistry and over 800 samples from 364<br />

monitoring sites were included to characterize groundwater chemistry of the area. Data included<br />

in the database span a monitoring period of over 40 years, and were retrieved from<br />

various, mainly publically available, sources of information including the BC Environmental<br />

Monitoring System database, the regional health authority, the Site C hydroelectric<br />

project and so on. The database was built into a GIS format which enables the evaluation<br />

of spatial trends, and which can easily be converted to other platforms such as Google<br />

Earth layers, tables, etc. The information was classified into five categories including site<br />

and sampling information, general chemistry, total and dissolved metals, isotopes, and other<br />

parameters. An analysis of metals in surface water and groundwater was completed to<br />

assess the evolution of different parameters over time at varied watershed scales. Surface<br />

water chemical results were also compared with current national and provincial guidelines<br />

for aquatic life. Aluminum, cadmium and mercury exceeded the aquatic life guidelines<br />

within 70%, 60% and 58% of the samples respectively. This is the first comprehensive<br />

database of this kind compiled for the region, which may be used as a baseline for future<br />

water quality assessments, to identify gaps or deficiencies in current monitoring programs,<br />

and to more effectively evaluate the influence of activities on the land and water resources<br />

in the Peace River.<br />

Regional Groundwater Systems 3<br />

Thursday October 29, 15:00 – 16:40<br />

Chair: Tom Gleeson<br />

Room: Wagner<br />

313 - Sequence Stratigraphic and Karstic controls of Regional<br />

Groundwater Flow Zones within the Early Silurian Lockport Group<br />

of the Niagara Escarpment, Southern Ontario and Manitoulin<br />

Island<br />

Frank R. Brunton<br />

Earth Resources and Geoscience Mapping Section, Ontario Geological Survey, Sudbury,<br />

Ontario, Canada<br />

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Regional bedrock potable groundwater flow zone mapping by the Ontario Geological<br />

Survey across the Niagara Escarpment region of Southern Ontario and Manitoulin Island<br />

has revealed the existence of preferred pathways that have and are taking advantage of<br />

predictable and karstic sequence stratigraphic boundaries. Building upon the revisions to<br />

the Early Silurian stratigraphy in SW Ontario (Brunton and Brintnell, 2012), this study<br />

highlights the implications of a new paleogeographic/paleoenvironmental perspective.<br />

The new perspective provides important insights into the controls and predictive nature of<br />

various carbonate bedrock fluid pathways. It also highlights the economic importance of<br />

characterizing forebulge-tectonic zones, and the value of geologic mapping and acquisition<br />

of geologic data to successfully explore, characterize, and name bedrock flow zones in a<br />

cost-effective manner.<br />

The study area straddles what has traditionally been described as the boundary between<br />

the Michigan intracratonic Basin and Appalachian Foreland Basin – a northeast-southwest<br />

trending feature known as the Algonquin Arch. This study has revealed that the<br />

so-called Arch can better be referred to as a flexural fore bulge region that migrated both<br />

spatially and temporally from north to south in southwestern Ontario through the Early<br />

Silurian. Intermittent responses to far-field tectonics along the Appalachian Foreland basin<br />

influenced local carbonate ramp geometries and relative sea level fluctuations and differential<br />

erosion regionally. The more significant the time breaks within the stratigraphic<br />

architecture – the more regional and significant the extent of the flow zones.<br />

The sedimentary rocks that comprise the Niagara Escarpment are Early Silurian in age<br />

and display a complex but predictable stratigraphic architecture that has been revealed<br />

through acquisition and detailed logging/sampling of cores and outcrops both within and<br />

away from the “Arch” or fore bulge region. Due to regional stress fields and differential<br />

erosion of the Paleozoic strata, rock strata presently dip gently in a SW direction away<br />

from the topographic high of the erosional Niagara scarp face. The underlying regionally<br />

extensive Cabot Head Formation shales of Clinton Group form the regional aquitard to<br />

the potable water supplies that reside in the overlying Lockport Group carbonates.<br />

Delineation of preferred bedrock groundwater flow zones required regional outcrop mapping,<br />

combined with examination of > 100 bedrock/overburden cores and/or geophysically-logged<br />

boreholes. The cores were logged and sampled for whole rock, trace element, and<br />

select REEs and isotopes (C, O, Sr), and conodont biostratigraphy over a five year period<br />

(2009 through 2014). Key cored holes across the study area also had video logs, variable<br />

duration packer pumping tests, FLUTe K-profiling, select Heat Pulse and optical-acoustic<br />

televiewer profiling, and select dye tracer tests. Many of the key cores integrated in this<br />

study were collected in collaboration with municipalities and other partners that both rely<br />

on bedrock ground waters and/or are exploring for new resources to meet future population<br />

and industry pressures.<br />

Following examination of the regional updip shallow well and more than 16000 oil/gas<br />

deeper well data, it became apparent that the sequence stratigraphic character of the Early<br />

Silurian strata was more complex than previously reported, but that similarities exist<br />

from updip and more deeply buried 3D-structures referred to as Guelph Pinnacle Reefs<br />

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(up to 100m-thick x kms in width & length). The deeply buried Guelph Pinnacles are<br />

not biogenic reefs, but comprise older and variably paleokarsted Lockport Group strata<br />

(Gasport & Goat Island Fms) – similar to high-flow groundwaters discovered in Cambridge-Guelph.<br />

The up to 100m of paleorelief of Lockport Group strata represents an ancient<br />

(Early Silurian) discontinuous, northwesterly facing set of scarps (mesa/butte topography—tower<br />

karst) enveloped by Salina Group shallow marine microbialites/evaporites<br />

(Sarnia area). Newly acquired biostratigraphy data suggest a significant time break separates<br />

Lockport and Salina Group strata. The Guelph Fm is a karst breccia regionally – reflecting<br />

extensive Silurian karst erosion – terrestrial settings (Sarnia area) that transition to<br />

marginal marine-estuarine (Bruce Peninsula-Mount Forest-Kitchener-Waterloo) through<br />

more open marine settings (i.e. Luther Lakes-Elora to Guelph-Cambridge regions) in an<br />

ESE direction – carbonate ramp dipping toward the Appalachian Foreland Basin.<br />

180 - The Use of Mass Balance Modelling to Assess Production<br />

Well Capture Zones<br />

M. Fraser & C. Johnston<br />

Stantec Consulting Ltd., Kitchener, Ontario, Canada<br />

R. Wootton, R. Vaillancourt, & E. Hodgins<br />

Regional Municipality of Waterloo, Kitchener, Ontario, Canada<br />

Source water protection is the first step in the multi-barrier approach to protecting drinking<br />

water. Capture zones are the basis for source water protection and source protection<br />

plans and are used to assess potential threats to water quality and/or quantity. The capture<br />

zones delineate the extent and boundaries of the land area contributing water to the intake<br />

or well. Therefore the reliable determination of these capture zones is crucial to successful<br />

source water protection planning.<br />

For groundwater supplies, capture zones are typically developed using groundwater flow<br />

modelling, which depending on the assumptions and parameters used (or known at the<br />

time) could provide varying results. Mass balance modeling of surficial contaminants, such<br />

as nitrate and chloride, could be used to assess the accuracy of these capture zones. The<br />

premise being that the mass of a parameter applied at surface should equal the mass of<br />

the parameter removed in the pumped water at the production well once degradation and<br />

attenuation are considered.<br />

Real world examples will be presented to demonstrate how mass balance modeling of<br />

nitrate and chloride was used to further refine the understanding of the production well<br />

capture zone.<br />

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168 - Deep groundwater systems in southern Ontario: Base of<br />

fresh water, water types, and flow directions<br />

Terry Carter 1 , Dejie Wang 2 , Jordan Clark 3 , Arthur Castillo 4 , & Lee Fortner 4<br />

1<br />

Consulting Geologist, London, Ontario, Canada<br />

2<br />

Ministry of Land and Resources, Beijing, People’s Republic of China<br />

3<br />

Ontario Oil, Gas and Salt Resources Library, London, Ontario, Canada<br />

4<br />

Ministry of Natural Resources and Forestry, London, Ontario, Canada<br />

Between 2008 and 2014 the Petroleum Operations Section of the Ministry of Natural<br />

Resources and Forestry (MNRF) completed a project to identify and map the principal<br />

water-bearing intervals in the Paleozoic bedrock of southern Ontario. After extensive and<br />

prolonged quality control edits, GIS queries of water records in the MNRF petroleum<br />

well database were used to create two map groupings: 17 maps of the static level of water<br />

in selected water-bearing geological formations in the Paleozoic bedrock, and 89 maps of<br />

water types and their geologic and geographic distribution in the bedrock.<br />

In all cases the water contained in Paleozoic bedrock formations and the overlying unconsolidated<br />

sediments in southern Ontario exhibits increasing salinity with depth. There is a<br />

down-dip gradation from fresh water at or near the surface in the drift and shallow bedrock<br />

(


the sampling and analysis of over 100 water wells in the area for 18 Oxygen and Deuterium.<br />

The mapping identified the major flow systems in the area, and identified considerable<br />

variations in the δ 18 O values in the individual flow systems, despite recharge under similar<br />

climatic conditions.<br />

In 1974, the groundwater demand in the Winnipeg area was considerably different than<br />

today. Two major meat packing industries in St. Boniface were each drawing over 4,000<br />

m 3 /day from the carbonate aquifer, while a cold storage facility in the downtown core was<br />

drawing from several deep wells that were partially completed into the underlying sandstone<br />

aquifer. The meat packing industries progressively shut down operations from the<br />

mid 1970’s to the 1980’s. The cold storage plant wells were sealed when the plant was shut<br />

down in the late 1990’s. Thus the recent period is the first time since the 1880’s that the<br />

aquifer has not been extensively developed in Winnipeg.<br />

The author has collected over 100 samples of 18 O and Deuterium across a wide area in and<br />

around the City of Winnipeg. Additional samples have been collected in the south westerly<br />

areas of Winnipeg, where previous analytical data was sparse. In addition, many samples<br />

have been collected from the capital region outside of the City of Winnipeg, within the<br />

individual flow systems presented through the previous research.<br />

The mapping effort has drawn some interesting conclusions about the changing conditions<br />

in Winnipeg since 1974. For example, the main flow systems are still present, although<br />

the values have changed around the eastern areas of the city. Further, the effects of<br />

the saline discharge from the Winnipeg Formation are also seen in the current mapping.<br />

The expansion of quarrying in the Birds Hill area also appears to have had a slight effect<br />

on flow from this recharge area.<br />

This paper presents an interesting update to the isotopic signature of an aquifer area that<br />

has been in a recovery from over 100 years of large consumption. Further, it is interesting<br />

to compare the changes in the isotopic signature that have occurred in the area during the<br />

recovery of the carbonate aquifer.<br />

256 - Geostatistical Characterization of Hydrofacies in a<br />

Heterogeneous Aquifer Considering Uncertainty in Hard Data<br />

Amir Niazi, Laurence R. Bentley, & Masaki Hayashi<br />

University of Calgary, Calgary, Alberta, Canada<br />

Characterizing heterogeneity of aquifers and quantifying the uncertainty associated with<br />

the characterization is an essential part of flow and solute transport modeling. The Paskapoo<br />

Formation is a highly heterogeneous bedrock aquifer located in southern Alberta,<br />

which consists of the remnants of a fluvial depositional system. The large number of wells<br />

completed in the Paskapoo makes this formation the most significant source of groundwater<br />

in the Canadian Prairies. This formation is comprised of relatively permeable sandstone<br />

channels embedded in generally less permeable siltstone and mudstone.<br />

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Lithological logs from the Alberta water well database have been used to build statistical<br />

models of the subsurface and to condition stochastic aquifer simulations. One of the<br />

inherent drawbacks in this database is that all wells within a quarter section (i.e. 800 m<br />

by 800m square) are assigned the coordinate of the center of the quarter section. In order<br />

to quantify the uncertainty associated with the coordinates of the wells, a Monte Carlo<br />

approach was used to generate a suite of 100 randomly distributed sets of coordinates for<br />

collocated wells. The coordinates were randomly selected within the quarter section within<br />

which the collocated wells are enclosed. Subsequently, Markov chain (transition probability<br />

geostatistics) and sequential indicator simulation (SISIM) were used to generate<br />

geologic simulations for each set of random coordinates.<br />

These sets of simulations were then converted to groundwater models and sorted based<br />

on their consistency with the archived data of single-well pumping tests on selected wells<br />

across the study area. A subset of the most consistent simulations was upscaled and the<br />

uncertainty is mapped based on the differences between simulations in the distribution<br />

of high conductivity hydrofacies materials and low permeability materials. The results of<br />

this study will constrain the plausible geometries of high and low permeability regions<br />

and provide a measure of the uncertainty associated with the heterogeneity in a regional<br />

groundwater model.<br />

Agricultural Impacts on Groundwater 2<br />

Thursday October 29, 15:00 – 16:40<br />

Chair: Cathy Ryan<br />

Room: Schubert<br />

221 - Matrix diffusion effects on nitrate transport and fate in a<br />

sedimentary bedrock aquifer<br />

Steven Chapman, Beth Parker, John Cherry, & Amanda Malenica<br />

G360 Centre for Applied Groundwater Research, University of Guelph, Ontario, Canada<br />

Yefang Jiang<br />

Science and Technology Branch, Agriculture and Agri-Food Canada, Charlottetown,<br />

Prince Edward Island, Canada<br />

Qing Li<br />

PEI Department Environment, Labour and Justice, Charlottetown,<br />

Prince Edward Island, Canada<br />

Cathy Ryan<br />

Department of Geoscience, University of Calgary, Calgary, Alberta, Canada<br />

Many agricultural areas are underlain by fractured sedimentary rock with thin overburden<br />

deposits, such that nitrate and other contaminants migrate within these bedrock units, which<br />

may also be relied on as water supply aquifers. The interconnected fracture network has very<br />

low bulk fracture porosity (~10 -3 to 10 -5 ) within which nearly all groundwater flow occurs<br />

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and provide the primary contaminant transport pathways, with flow velocities of a few to<br />

several meters per day possible. However, the rock matrix blocks between fractures have high<br />

porosity (~5-20%) and matrix diffusion causes transfer of nitrate from groundwater flowing<br />

in fractures to the matrix. This can be viewed as a positive effect in that rates of transport<br />

in fractures and downgradient nitrate flux is attenuated, which may be reducing short-term<br />

impacts to water supply wells and groundwater discharge areas since the front of the contaminated<br />

zone is expected to move much more slowly. However a negative consequence of the<br />

large nitrate storage in the matrix is potential for slow release via back diffusion, which can<br />

cause long-term nitrate persistence following declines in nitrate inputs due to changes in agricultural<br />

practices. In this study, a portion of an agricultural field was taken out of production<br />

for a five year period to examine downgradient effects. Field activities included instrumentation<br />

of the field from upgradient to downgradient along the flow system using multilevel<br />

monitoring systems for temporal groundwater sampling, continuous coring to assess the nitrate<br />

distribution in detail in overburden and in the bedrock matrix, and an array of core and<br />

borehole measurements to provide matrix and fracture parameters for modeling. Numerical<br />

modeling was conducted to examine matrix diffusion effects using a coupled Equivalent Porous<br />

Media (EPM) – Discrete Fracture Network (DFN) approach. First a 3-D watershed<br />

scale EPM flow model was developed and calibrated using the HydroGeoSphere code. This<br />

flow model provides information on the bulk groundwater flow system (Darcy flux, hydraulic<br />

gradients) needed to inform 2-D DFN transport simulations using the FRACTRAN<br />

code, which incorporates key processes controlling contaminant transport in fractured porous<br />

media. The DFN model was then used to examine matrix diffusion effects for scenarios<br />

with estimated historical nitrate source inputs followed by removal of the source input. Both<br />

the field datasets and numerical modeling show strong matrix diffusion effects, acting as an<br />

impediment to aquifer restoration. Such effects must be considered when assessing efficacy<br />

of implementation of best management practices (BMPs). Sensitivity to fracture network<br />

characteristics is evaluated with the DFN modeling informed from field data.<br />

194 - Decadal scale groundwater nitrate concentrations in<br />

Western Prince Edward Island<br />

Jessica A. Guselle & M.C. Ryan<br />

Department of Geoscience - University of Calgary, Calgary, Alberta, Canada<br />

G. Somers<br />

Department of Environment, Labour, and Justice, Charlottetown, Prince Edward Island,<br />

Canada<br />

Y. Jiang<br />

Crops and Livestock Research Centre, Agriculture and Agri-Food Canada, Prince Edward<br />

Island, Canada<br />

Prince Edward Island (PEI) relies wholly on groundwater for its potable water supply, and<br />

has a large percentage of land under agricultural cultivation (approximately 50%). In addition<br />

to drinking water concerns, elevated groundwater nitrate in PEI is linked with estuarine eutrophication,<br />

as groundwater discharge accounts for 60-70% of the baseflow to rivers. Decadal<br />

scale increases in river nitrate concentrations have been observed in most of PEI’s watersheds.<br />

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The change in well water nitrate concentrations in western PEI are assessed by comparing<br />

three well water sampling programs: i) a continuation of a domestic well water survey that<br />

was completed by the Geological Survey of Canada (GSC) from 1950-1953; ii) a continuation<br />

of a provincial well water survey of public domains (ie. schools, hospitals, provincial<br />

parks, etc.); and iii) a weekly sampling program of both surface and groundwater at seven<br />

locations along the Mill River into the estuary. Decadal scale changes in land use (including<br />

soil and crop management and the potential increase of the population who relies on<br />

septic systems) are evaluated to reconcile observed nitrate concentration increases in the<br />

majority of water wells.<br />

The overall goal of this project is to link the observed decadal scale changes in groundwater<br />

and the river nitrate concentrations at a watershed scale model to facilitate an understanding<br />

of how future land changes will affect groundwater, river, and estuarine nitrate<br />

concentrations.<br />

304 - Simulating Integrated Water Management for Irrigation in<br />

the Lower Republican River Basin, Kansas<br />

A. Brookfield<br />

Kansas Geological Survey, Lawrence, Kansas, USA<br />

C. Gnau<br />

Kansas Water Office, Topeka, Kansas, USA<br />

In many parts of the world a primary concern for the agricultural industry is the availability<br />

of water for irrigation. Careful management of both surface water and groundwater<br />

resources is needed to ensure sustainable use now and into the future. Engineered water<br />

management systems, including reservoirs and irrigation canals, are often employed to ensure<br />

the optimal use of water available. Traditionally these systems have been designed and<br />

operated with little to no consideration of the unaltered hydrologic system they overlay.<br />

Recent research has highlighted the importance of groundwater/surface water interactions<br />

to the distribution of water in both surface and subsurface regimes and the importance of<br />

simulating the hydrologic system holistically. The significance of these interactions is not<br />

limited to unaltered hydrologic systems, but can extend to the engineered water management<br />

systems as well. To account for these interactions, the integrated hydrologic model<br />

HydroGeoSphere (HGS) was linked to the surface water operations model OASIS to<br />

evaluate the impacts of current water management strategies and potential infrastructure<br />

improvements on the surface water and groundwater resources of the Lower Republican<br />

River Basin (LRRB) located in Kansas and Nebraska, USA.<br />

The LRRB covers approximately 10,300 km 2 and contains two reservoirs and several irrigation<br />

districts (and their associated canal systems). Surface water and groundwater of<br />

the LRRB are heavily utilized for agriculture and the region has historically experienced<br />

severe droughts and floods. Water in this basin is distributed in accordance to an interstate<br />

compact that was ratified in 1942 and has been subject to litigation before Supreme Court<br />

several times in more recent years. The compact and associated Supreme Court final stipulation<br />

settlements require efficient management of both the surface water and groundwater<br />

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in this basin. The HGS/OASIS model framework was used to evaluate the interactions<br />

and dependencies between the engineered and natural hydrologic systems under historic<br />

and projected future climatic conditions and potential structural water management alternatives<br />

in this basin. Results emphasize the need to include groundwater, surface water and<br />

their interactions in water management strategies and planning.<br />

130 - Evaluating innovative techniques for in situ, real-time<br />

remote monitoring of nitrate in groundwater<br />

Graeme MacDonald & Jana Levison<br />

School of Engineering - University of Guelph, Guelph, Ontario, Canada<br />

Certain hydrogeological settings in southern Ontario are particularly vulnerable to nitrate<br />

contamination of groundwater. Nitrate can leach into aquifers during recharge events,<br />

where it is subject to complex fate and transport processes under spatially and temporally<br />

variable flow conditions. Advancements in monitoring and data collection capabilities can<br />

improve our understanding of these transport processes. Groundwater quality measurements<br />

are traditionally obtained by purging wells and analyzing the collected samples ex<br />

situ. This “snapshot” data can disrupt the natural subsurface flow system and is not always<br />

detailed enough to determine critical water quality conditions. This research involved the<br />

application of two innovative sensors, the YSI EXO and Satlantic SUNA V2, to develop<br />

novel groundwater quality sampling techniques. Three unique methods were developed:<br />

flow cell spot sampling, depth-discrete downhole geochemical profiling, and real<br />

time remote groundwater quality monitoring (RTRM). While nitrate was the contaminant<br />

of focus, field parameters including temperature, DO, ORP, EC, and turbidity were<br />

also monitored. Research sites ranged from supply wells located in shallow overburden<br />

aquifers to deep fractured bedrock boreholes. Flow cell spot sampling results were compared<br />

to traditional laboratory sampling methods and were very strongly correlated (R 2 =<br />

0.99), suggesting that the sensors can provide highly accurate field nitrate measurements.<br />

Depth-discrete profiling techniques were used to identify groundwater quality zones corresponding<br />

to different formations. Stratified nitrate concentrations were observed in an<br />

open bedrock borehole (20 m depth) and an overburden well having a long (8 m) screened<br />

interval. RTRM methods were conducted by installing sensor equipment directly downhole.<br />

Groundwater quality parameters were obtained every 15 minutes for several months,<br />

starting in November 2014, greatly improving the temporal resolution of measurements<br />

compared to traditional sampling. Data was transmitted over the HSPA network and observed<br />

in real time, allowing for remote monitoring and effectively reducing labour and<br />

field visits compared to traditional techniques. The detailed datasets obtained will support<br />

future nitrate transport modelling initiatives and complement field projects in which in<br />

situ, detailed nitrate measurements are desired.<br />

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114 - Validating effects of spring plowing forages on nitrate<br />

leaching reduction<br />

Yefang Jiang, Judith Nyiraneza, Mohammad Khakbazan, Brian Murray, & Mark<br />

Grimmett<br />

Agriculture and Agri-Food Canada, Charlottetown, Prince Edward Island, Canada<br />

Prince Edward Island (PEI) is the smallest province in Canada, yet it contributes about onefourth<br />

of the Canadian potato production. The potato industry plays a critical role in the local<br />

economy. Intensive potato production is conducted on sandy soils underlain by a semi-confined<br />

or unconfined sandstone aquifer, which provides all the drinking water in PEI. High<br />

nitrate leaching losses from the production systems have been linked to the contamination of<br />

groundwater (i.e., the source of drinking water) and estuarine eutrophication as indicated by<br />

reoccurring anoxic events in many estuaries. Potatoes are commonly grown in rotation with<br />

grain underseeded with forages, with the latter being plowed down in the fall of the third<br />

season as green manure. Previous work has shown that a high proportion of nitrate leached<br />

from these systems occurs upon potato harvest and fall forage plow down. The rotation forages<br />

usually include N-rich leguminous crops with low C/N ratio intended for maintaining<br />

soil organic matter for optimal production. When being plowed down in the fall, a portion<br />

of these forages release nitrate via mineralization, which leaches from the soil profile with the<br />

excessive moisture during the wet offseason in PEI. Via paired-field tests during 2010-2012,<br />

we found that postponing plowing of forages from fall to spring reduces forage-phase nitrate<br />

leaching by 20-60% and as a result, more soil N is retained for subsequent crops. During<br />

2013-2014, we asked the growers to implement similar delayed forage plowing in the former<br />

study sites with sampling facilities we instrumented. We continued on monitoring the tiledrain<br />

and well water quality, sampling the soil and crop tissues and conducting biophysical<br />

and modeling analysis. We found that spring plowing forages reduces nitrate leaching but to<br />

a lesser extent compared to the previous data possibly because the forages did not grow well<br />

due to the cold spring weather in 2013. We also found that implementing spring plowing did<br />

not compromise potato yield and quality. This new dataset provides a validation on the effects<br />

of spring plowing forages on nitrate leaching reduction and potato production and additional<br />

confidence by industry in the value of implementing spring plowing.<br />

Workshop on Groundwater Policy 2<br />

Thursday October 29, 15:00 – 16:40<br />

Chair: Steve Wallace<br />

Room: Bloomingdale<br />

147 - Groundwater and Aboriginal People: Should the Winters<br />

Doctrine apply in Canada and, if so, what would it look like?<br />

Anderson, Kristina<br />

Toronto and Region Conservation Authority, Toronto, Ontario, Canada<br />

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The Winters doctrine comes out of a United States supreme court case of 1908 which<br />

set forth the idea that, in the early United States, certain rights were reserved for Native<br />

Americans with the purpose of allowing them to become self-sufficient communities.<br />

Where a reserve was created for agricultural purposes, the approach of the American judiciary<br />

has been to base their calculations on the reservation’s practicably irrigable acreage.<br />

Several Canadian academics have argued that the Winters doctrine should be applied to<br />

reservations here but as of yet Canadian courts have not confirmed its application. Assuming<br />

the Winters doctrine should be adopted in Canada, the next question is whether<br />

aboriginal water rights were extinguished by a legislative body with the authority to do so.<br />

The key piece of legislation which might have had this effect at least within the Prairie<br />

Provinces is the federal Northwest Irrigation Act of 1894. If aboriginal water rights were<br />

not extinguished by the Northwest Irrigation Act, and at least one prominent academic<br />

argues they were not, a new issue arises with respect to the priority of aboriginal water<br />

rights over non-aboriginal water rights under all three major Canadian water allocation<br />

schemes - Prior allocation, Riparian rights, and Civil code - although quantification and<br />

priority dates may be less useful outside of the Prior allocation scheme.<br />

Although Canadian courts have not yet confirmed the application of the Winters doctrine,<br />

it is clear the Canadian judiciary is influenced by it. Three questions the four western provinces<br />

will need to grapple with as they determine priority of aboriginal water rights include:<br />

(1) are aboriginal water rights subject to forfeiture and abandonment for non-use? (2) what<br />

was the date the reservation in question was created? and (3) how will the amount of water<br />

necessary to satisfy the objective of the reservation be quantified? In an attempt to answer<br />

these questions, historical context and modern law will be explored. Examples of historical<br />

context include the Metis uprising and the creation of the Province of Manitoba in 1870<br />

exempting lands within the former postage stamp province from the Northwest Irrigation<br />

Act. Examples of modern law include treaties such as Nisga’a Final Agreement Act 1999,<br />

in addition to recent court cases such as Piikani First Nation v. Alberta 2002, Tsuu T’ina<br />

Nation v. Alberta 2010 and Helalt First Nation v British Columbia 2011. The Helalt First<br />

Nation case is of particular interest as it claimed the reserve’s rights extended to groundwater<br />

and baseflow of the Chemainus River to maintain a healthy fishery.<br />

242 - Water Sustainability Act: Factors, principles and reasoning<br />

governing legislative policy development related to the diversion<br />

and use of groundwater in British Columbia, Canada<br />

Mike Wei<br />

B.C. Ministry of Environment, Victoria, British Columbia, Canada<br />

The new Water Sustainability Act (WSA), which received Royal Assent in May of 2014,<br />

was developed to replace the more than 100 year-old Water Act and to address major water<br />

management policy gaps in British Columbia (BC). One such gap is the current lack of<br />

government control over the diversion and use of groundwater, a provincial resource. In developing<br />

the WSA, four major strategic policy questions needed to be answered in relation<br />

to how BC would regulate the diversion and use of groundwater:<br />

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1. Should the diversion and use of groundwater follow a first-in-time, first-in-right priority<br />

framework as currently exists for surface water in BC or is it appropriate to develop a<br />

different (and possibly improved) governing framework for groundwater?<br />

2. How should existing groundwater users be regulated?<br />

3. How should small groundwater users be regulated?<br />

4. How should diversion and use of saline groundwater found at depth in the Interior<br />

Plains Region of northeast BC be regulated?<br />

The limited state of knowledge of the groundwater resource in BC imposed variable degrees<br />

of uncertainty to answering these important groundwater policy questions. This<br />

paper presents the historical regulatory context and examines the factors, principles, and<br />

reasoning that helped shape the policy outcomes in the WSA. This paper also presents<br />

some practical insights gained in the process of developing the WSA, which may be of<br />

useful consideration by other jurisdictions embarking on developing policies to enhance<br />

sustainable management of their groundwater resource.<br />

320 - Development of Groundwater Policy for Alberta’s Oil Sands<br />

Region<br />

Margaret Klebek<br />

Alberta Environment and Parks, Government of Alberta, Alberta, Canada<br />

One of the main concerns in Alberta’s Oil Sands Region (AOSR) is the potential effect<br />

to groundwater from oils sands projects. To address this, Alberta Environment and Parks<br />

has developed a number of policies to guide stewardship of groundwater during current<br />

and future growth. The policies align with the overall principles and goals of Water for<br />

Life: Alberta’s Strategy for Sustainability and Land Use Framework to manage cumulative<br />

effects to groundwater on a regional basis.<br />

The Groundwater Management Framework (GMF) for the Lower Athabasca Region,<br />

Water Conservation Policy for Upstream Oil and Gas Operations and policies for the<br />

management of non-saline groundwater in direct contact with bitumen and thermally mobilized<br />

constituents around in-situ operations have been completed or are nearing completion.<br />

Further policy development is being considered for protection and management of<br />

groundwater in the Shallow Thermal Area (STA).<br />

The GMF introduces several new mechanisms to achieve the goals of preserving and improving<br />

groundwater quality in the AOSR. It establishes the basis for determining when<br />

levels of specific chemical parameters have been reached (“trigger values”) that could have<br />

an effect on groundwater quality. On the basis of trigger values, the GMF establishes<br />

groundwater quality protection limits that prescribe specific management actions when<br />

limits are exceeded.<br />

The Water Conservation Policy for Upstream Oil and Gas Operations expands upon its<br />

2006 predecessor to include oil sands mining operations in addition to thermal in-situ<br />

operations. The policy strives to minimize the amount of non-saline (fresh) water used<br />

for upstream oil and gas projects by requiring operators to critically evaluate all potential<br />

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water sources while taking into account the overall environmental net effects of each water<br />

sourcing option.<br />

Requirements for assessing thermally mobilized constituents are being put into place to<br />

improve understanding of the fate and transport of these constituents in groundwater<br />

around in-situ operations and to ensure that appropriate monitoring and management<br />

occurs through the development and implementation of site-specific Groundwater Management<br />

Plans (GMPs). Further requirements are being developed for the assessment<br />

and management of non-saline groundwater in direct contact with bitumen for in-situ<br />

operations, such that that appropriate monitoring and management occurs through the<br />

implementation of GMPs.<br />

Most bitumen that is recoverable by in situ methods using steam requires a caprock with<br />

low permeability, adequate thickness, sufficient integrity, and lateral continuity to contain<br />

the steam and reservoir fluid. The STA is considered a high risk area for steam-assisted<br />

drainage schemes (SAGD) since the process is undertaken in the area with relatively<br />

thin caprock, presence of faults, incising channels, the Devonian and Cretaceous strata<br />

impacted by dissolution and karsting, which could impact integrity of caprock. Alberta<br />

Environment and Parks intends to address the environmental risks of the SAGD development<br />

in the STA, and is considering developing policy based on risk identification and<br />

performance monitoring.<br />

250 - Groundwater Monitoring for policy support and development<br />

under Alberta Environmental Monitoring, Evaluation and<br />

Reporting Agency (AEMERA)<br />

Guy Bayegnak & Steve Wallace<br />

AEMERA, Edmonton, Alberta, Canada<br />

The province of Alberta is currently in a unique situation where confluence of circumstances<br />

requires us to be very strategic as we continue the responsible development of our resources.<br />

Today’s rapid growth in population and economic activity is placing unprecedented pressure<br />

on Alberta’s environment (air, land, groundwater, surface water and biodiversity). Oil and gas,<br />

forestry and mining, agriculture and recreation, housing and infrastructure are all in competition,<br />

and often on the same parcel of land. This growth has led to basin closure for surface<br />

water allocation in some parts of the province, while drawing an increasing local, national and<br />

international attention of environmental management issues. A key initiative by the province<br />

to ensure responsible development and sustainable growth is the development of an Integrated<br />

Resource Management System (IRMS) and the creation of the Alberta Environmental<br />

Monitoring, Evaluation and Reporting Agency (AEMERA).<br />

AEMERA, as part of the Integrated Resource Management System, is responsible for<br />

monitoring, evaluating and reporting on air, groundwater, surface water, land and biodiversity.<br />

Using the principles of cumulative effects management, aemera’s monitoring work will<br />

support the improvement of thresholds, identify potential needs for future management<br />

responses, and support updating to existing policies as well as the development of new<br />

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policies. In this paper we present a brief overview of AEMRA’s mandate. We then focus on<br />

groundwater and present some of the innovative approaches AEMERA is implementing<br />

to ensure groundwater cumulative effects are detected, measured, evaluated and reported<br />

upon, using the example of the groundwater monitoring optimization project, aimed at<br />

designing a stratified monitoring network.<br />

127 - BC Oil and Gas Commission Regulatory Framework,<br />

Groundwater Initiatives, and Key Groundwater Research Topics<br />

Laurie Welch & Allan Chapman<br />

BC Oil and Gas Commission, British Columbia, Canada<br />

The BC Oil and Gas Commission (Commission) is the regulatory authority for oil and<br />

gas activities in British Columbia. This presentation will outline the current regulatory<br />

framework for groundwater in B.C. as it pertains to oil and gas activities, and discuss<br />

the role of the Commission in regulating aspects of groundwater use and protection. In<br />

response to increasing oil and gas activity in northeast B.C. related to shale gas extraction,<br />

and to support science-based regulation of groundwater aspects, the Commission has implemented<br />

or supported a number of recent initiatives. These include enhancements to the<br />

Commission’s regulatory and permitting procedures for industry water source wells, providing<br />

support for the Northeast B.C. Water Strategy, collaboration on the Northeast B.C.<br />

Aquifer Characterization Study, and support of academic research in British Columbia.<br />

Future focussed research will continue to inform the regulatory regime. Key future research<br />

topics for northeast B.C. will be reviewed.<br />

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POSTER SESSION: Advanced Techniques for<br />

Site Characterization<br />

Thursday October 29, 16:40<br />

Room: Regent<br />

141 - Developing a lithostratigraphic and geomechanical<br />

framework using a discrete fracture network approach across a<br />

dense borehole cluster within a shallow Paleozoic dolostone<br />

Andrey Fomenko 1 , Colby M. Steelman 1 , Pete Pehme 1 , & Beth L. Parker 1, 2<br />

1<br />

School of Engineering – University of Guelph, Guelph, Ontario, Canada<br />

2<br />

School of Environmental Sciences – University of Guelph, Guelph, Ontario, Canada<br />

To improve our understanding of complex bedrock flow systems, test fundamental hydrogeological<br />

assumptions, as well as to facilitate the development of new techniques and technologies,<br />

the G360 group has constructing a field bedrock groundwater research laboratory<br />

on the University of Guelph campus. Nine boreholes (six vertical and three inclined) have<br />

been drilled within a quarter hectare area on the university campus to an approximate depth<br />

of 74 m below ground surface, primarily through the Silurian dolostone and limestone regional<br />

aquifer into the upper portion of the Cabot Head shale aquitard. The boreholes have<br />

been carefully configured to capture the three dimensional complexity of the discrete fracture<br />

network inherent in sedimentary rock. We present the initial phase of the site characterization<br />

which focuses on the results of high-resolution (cm scale) core logging and downhole<br />

geophysical logging to investigate the relationship between the lithological and mechanical<br />

properties of the rock mass and their implications on fracturing. A discrete fracture network<br />

model was developed and evaluated with respect to major and minor lithostratigraphic units<br />

as defined by physical core log descriptions supported by data including natural gamma,<br />

induced conductivity, full-waveform sonic, acoustic televiewer, optical televiewer, borehole<br />

video camera information collected from all nine coreholes. Fracture network characteristics<br />

were evaluated in terms of their relationship / dependency to major lithostratigraphic units<br />

spanning two important bedrock aquifers in the Guelph region. We evaluated the spatial<br />

variability in lithostratigraphy and discrete fracture properties (i.e., geometry, aperture, frequency),<br />

and assessed the relationship between lithstratigraphic and geomechanical layers<br />

at an unprecedentedly small spatial (vertical and lateral) scale. These interdependent data<br />

sets and fracture model will form the foundation of the second phase of the project which<br />

will involve a thorough hydraulic characterization of the site using a broad range of innovative<br />

single and cross-hole hydraulic and hydro-physical tests. Combining these fundamental<br />

characterizations of the field laboratory will not only develop new insights into both the<br />

nature fracturing as well as flow and transport in sedimentary rock, but it will also create the<br />

foundation for future experiments and technology development.<br />

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254 - Microbial community characterization at bioremediation<br />

sites using next generation sequencing<br />

Philip Dennis, Ximena Druar, & Peter Dollar<br />

SiREM, Guelph, Ontario, Canada<br />

Kirill Krivushin, Line Lomheim, & Elizabeth Edwards<br />

Department of Chemical Engineering – University of Toronto, Toronto, Ontario, Canada<br />

Next generation sequencing (NGS) is increasingly used to provide detailed microbial<br />

community characterization in public health, medical, wastewater treatment, industrial<br />

fermentation and resource extraction scenarios. The growing affordability of NGS now<br />

makes this technology practical for bioremediation monitoring and performance assessment.<br />

While NGS protocols are robust, the ability to analyze and interpret results in a<br />

meaningful way requires ongoing use and observations at a variety of remediation sites to<br />

better understand the benefits, and limitations, of NGS approaches.<br />

In this study, NGS using a 454 pyrotag platform and primers targeting 16S rRNA genes,<br />

were employed to characterize eubacteria and archaea from five geographically distinct<br />

chlorinated solvent bioremediation sites in Ontario (ON), Oregon (OR), Alaska (AK)<br />

Kansas (KS) and Florida (FL). All sites were bioaugmented and at various stages of remediation<br />

and had varying geochemistry and contaminant profiles. Archived genomic<br />

DNA samples spanning several years were used for the analyses. The resulting sequences<br />

were analyzed using cluster analysis, to compare the microbial communities over time and<br />

between sites and non-metric multidimensional scaling (NMDS) to provide correlations<br />

with geochemical parameters.<br />

NGS returned an average of 8,000 reads per sample, providing detailed microbial community<br />

profiles. Cluster analysis indicated that samples generally grouped together by site<br />

suggesting geographic uniqueness of microbial community structure across these diverse<br />

sites. Based on the number of operational taxonomic units (OTUs) the AK site had the<br />

lowest apparent microbial diversity and the FL site had the highest. Furthermore, cluster<br />

analysis indicated that microbial community at the FL site evolved to become the most<br />

similar to the bioaugmentation culture injected at the site (KB-1) and may indicate that<br />

the FL site was most compatible with bioremediation in general. Observations of OTU<br />

frequency indicated that changes in the abundance of individual microorganisms were significant,<br />

and could be correlated to specific changes in site geochemistry such as oxidation<br />

reduction potential, and metabolic processes such as toxicity, methanogenesis, sulfate reduction<br />

and methanotrophy. It would appear that NGS has great potential to increase our<br />

understanding of microbial communities in bioremediation systems and may find uses in<br />

site monitoring, diagnosis of problematic sites, remediation optimization and monitoring<br />

ecological recovery of aquifers. The technology’s usefulness will undoubtedly increase in<br />

tandem with our ability to meaningfully interpret NGS results.<br />

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295 - Bedrock Groundwater Monitoring Design Created Using<br />

Portable Drills for Remote and Ecosensitve Areas<br />

Amanda A. Pierce, Beth L. Parker, John A. Cherry, Steven Chapman, & Celia<br />

Kennedy<br />

G360 Centre for Applied Groundwater Research, University of Guelph, Ontario, Canada<br />

Robert Ingleton<br />

Department of Earth and Environmental Sciences, University of Waterloo, Ontario, Canada<br />

Portable drilling machines, the Shaw Portable Core Drill and the Winkie Drill, originally<br />

produced for the mineral exploration industry have been used in remote and eco-sensitive<br />

areas to install bedrock monitoring probes for groundwater investigations at distinct hydrogeologic<br />

settings. The methodology was developed at a large industrial site in southern<br />

California. The California site is located on a mountain ridge 490 to 670 metres (m) above<br />

mean sea level. The site is underlain by faulted Late Cretaceous age turbidite sandstones<br />

with shale interbeds. The mountain groundwater system is a large mound maintained by<br />

recharge from rainfall with flow primarily in fractures directed downward and outward toward<br />

the slopes and the urban lowlands below. Groundwater is found discharging at seeps<br />

along the mountain bedrock slopes. To provide insight into the groundwater flow system<br />

and contaminant transport and fate the portable rock core drills were hiked into remote<br />

seep locations and used to core small diameter holes (41 to 50 millimeters) to a maximum<br />

depth of 12 m. A cluster of wells were completed at multiple depths at 17 locations surrounding<br />

the site. A monitoring well was designed to accommodate the small diameter<br />

size of the coreholes by using a seal created by injecting grout into a flexible cylindrical<br />

impervious fabric liner of diameter slightly larger than the hole. The ‘grout liner’ method<br />

ensures that the entire annulus above the top of the short well screen is sealed, which allows<br />

the monitoring well to perform as a piezometer both for measuring hydraulic head and<br />

groundwater sampling. The seal created using this method avoids loss of the sealant into<br />

fractures and therefore avoids influence of grout on groundwater chemistry. The methods<br />

developed at this study area have been implemented in Prince Edward Island sandstone<br />

to investigate nitrate discharging at streams due to agricultural practices and in dolostone<br />

near Guelph, Ontario for hydrologic studies regarding surface water/groundwater interaction<br />

along a bedrock river. These methods applied in these studies overcomes the portability<br />

limitations of conventional drilling methods that prevent installation of monitoring<br />

wells in rugged mountainous terrain and has proven transferable to ecologically sensitive<br />

areas along rivers, lakes and wetlands.<br />

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POSTER SESSION: Agricultural Impacts on<br />

Groundwater<br />

Thursday October 29, 16:40<br />

Room: Regent<br />

243 - Fate and transport behavior of waste Greenhouse nutrient<br />

feed water during controlled land application experiments at<br />

selected field trial sites<br />

Jiangyue Ju 1 , David L. Rudolph 1 , Don King 2 , & Ann Huber 2<br />

1<br />

Department of Earth and Environment Science, University of Waterloo, Waterloo, Ontario,<br />

Canada<br />

2<br />

Soil Resource Group, Guelph, Ontario, Canada<br />

Because of the high concentration of greenhouses in Essex County, greenhouse discharges<br />

are considered as a potential contributor to nuisance and harmful algal blooms (HABs)<br />

and hypoxia in Lake Erie. Nutrient feed waters from greenhouses are comparable to other<br />

nutrient sources used in agriculture. Land application of greenhouse nutrient feed water to<br />

adjacent crop land is regarded as a potentially suitable alternative to in-house wastewater<br />

treatment systems both in cost and ease of adoption. Therefore, the land application of<br />

the feed water can be an appropriate management response to the nutrient load issues<br />

in such water courses. In an effort to assess the potential environmental impacts of this<br />

land application option, a collaborative monitoring program was established at partner<br />

greenhouse operations near Leamington, ON. We hypothesized that the nutrients in feed<br />

water applied to active crop lands would be absorbed and attenuated to an acceptable level<br />

within the soil profile before reaching the local water table. Four field trial sites were established<br />

and characterized for controlled plot size experiments. Field installations included<br />

porous cup lysimeters at 30cm, 60cm and 90cm for the collection of soil water samples,<br />

groundwater wells above and below water table to monitor groundwater quality and water<br />

table fluctuations and composite soil cores at random locations for soil analysis. At two<br />

of the field sites, feed water from the greenhouses was applied to the monitored plots in<br />

the spring at the maximum allowed rate and at the other two sites; the feed water was applied<br />

both in the fall and spring. Composite soil samples and water samples including soil<br />

water from lysimeters, shallow groundwater from monitor wells and surface water from<br />

tile outlets were collected both before and after the land application events. Laboratory<br />

analysis was focused on nutrients and heavy metals. The field data sets will be compared<br />

in this presentation to illustrate the performance of the land application process relative<br />

to environmental impacts and initial observations regarding the utility of this approach to<br />

managing the waste greenhouse feed waters will be discussed.<br />

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208 - Impacts of alkaline stabilized biosolids application on<br />

emerging substances of concern (ESOC) in groundwater<br />

Carolina Klabunde & Jana Levison<br />

University of Guelph, Guelph, Ontario, Canada<br />

Gordon W. Price & Rob Jamieson<br />

Dalhousie University, Truro, Nova Scotia, Canada<br />

Anthony Tong & John Murimboh<br />

Acadia University, Wolfville, Nova Scotia, Canada<br />

Mehdi Sharifi<br />

Trent University, Peterborough, Ontario, Canada<br />

Shiv Prasher<br />

McGill University, Montréal, Québec, Canada<br />

Cathryn Ryan<br />

University of Calgary, Calgary, Alberta, Canada<br />

Beth Parker<br />

University of Guelph, Guelph, Ontario, Canada<br />

This multidisciplinary study, part of a broader investigation about the environmental fate<br />

of biosolids application to agricultural fields, aims to better understand the transport of<br />

ESOC to a shallow sedimentary fractured bedrock aquifer. Application of biosolids on<br />

agricultural land is a growing practice and disposal alternative, and can replace the use of<br />

chemical fertilizers. The biosolids applied for this study are produced using an advanced<br />

alkaline stabilization process. There is a desire to understand potential environmental implications<br />

from the application of these soil amendments to ensure that they can be applied<br />

without negative impacts on the underlying aquifer. The relationship between biosolid<br />

application rates and resulting concentrations of ESOC in aquifers requires further investigation.<br />

The research objectives are to identify potential impacts of biosolids application<br />

on groundwater quality in a shallow bedrock aquifer, looking at both temporal and spatial<br />

variability, and to determine whether tile drainage systems affect the leaching of ESOC<br />

to the aquifer. The research site is located at the Bio Environmental Engineering Centre<br />

(BEEC) in Bible Hill, Nova Scotia. Local soils are usually acidic, allowing the utilization<br />

of the amendments applied in this study. Previously, the field had received yearly applications<br />

of manure and herbicides for 11 years, meeting needs of the alternating barley,<br />

soybean and spring wheat crops. The saturated zone is a red sandstone bedrock aquifer<br />

(Wolfville formation). The field site is instrumented with a modern and efficient high<br />

resolution design, using a newly installed CMT multilevel system (25 m deep), tile drain<br />

sampling and 5 shallow piezometers (1 m to 5 m deep). Two loads of 14Mg/ha each of<br />

biosolids were incorporated into the soil (November 2014 and May 2015) in a field which<br />

has not previously received biosolids. The monitoring approach facilitates obtaining distinct<br />

insights on water quality and contaminant behaviour, capturing a detailed picture<br />

of contaminant leaching into the subsurface. In addition, a bromide tracer experiment is<br />

used to further characterize the groundwater flow and travel times from the surface to the<br />

aquifer. A site conceptual model is developed to characterize the surface-to-aquifer transport<br />

of relevant ESOC tailored to the local overburden and sedimentary bedrock aquifer<br />

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setting. Preliminary results from analysis of major ions and nitrate-nitrogen (e.g. ranging<br />

from 1 mg/L to 11 mg/L) show that the system is sensitive to surface-applied compounds.<br />

The results are relevant for the implementation of local water protection policies, can aid in<br />

the development of standards or guidelines to avoid harm from biosolids application, and<br />

should be considered by specialists when recommending ideal agronomic loading rates of<br />

biosolids for agricultural soil amendments.<br />

299 - Non-point or multi-point? Capturing spatial and temporal<br />

variation of groundwater nitrate contamination to inform soil and<br />

crop management<br />

Shawn E. Loo, Edwin Cey, & M. Cathryn Ryan<br />

Department of Geoscience – University of Calgary, Calgary, Alberta, Canada<br />

Bernie J. Zebarth<br />

Potato Research Centre – Agriculture and Agri-Food Canada, Fredericton, New Brunswick,<br />

Canada<br />

Elevated nitrate concentrations in the highly vulnerable, unconfined Abbotsford-Sumas<br />

Aquifer has been recognized for decades and has been attributed to agricultural practices<br />

on the land surface. The Abbotsford-Sumas Aquifer represents a case study where small<br />

fields (~5 ha), with different managers, and large variations in inter-annual and inter-field<br />

nutrient inputs create a multi-point, rather than non-point, nitrate source. Consequently,<br />

relating groundwater nitrate concentrations to specific management practices is a key<br />

challenge for addressing groundwater nitrate from a crop management perspective. Environment<br />

Canada has monitored Abbotsford-Sumas Aquifer nitrate concentrations since<br />

early 1990s using a widespread piezometer network with 0.9 – 2.4 m long screens. This<br />

approach captures long-term regional trends, but the confounding effects of predominantly<br />

horizontal flow, complex multi-point nitrate sources, and the unknown time between<br />

leaching and arrival at the piezometer make it difficult to relate spatial and temporal variations<br />

in nitrate concentrations to field scale crop management. This study models the fate<br />

of groundwater nitrate from multiple field sources with time and depth in the Abbotsford-Sumas<br />

Aquifer, and compares the effects of varying down-gradient distance, depth of<br />

sampling, and piezometer screen length. The detailed transport modelling results are compared<br />

with measured concentrations from high-resolution sampling of an individual field<br />

over several years, as well as the results of Environment Canada’s long-term nitrate time<br />

series. This work aims to strengthen our conceptual understanding of such multi-point<br />

agricultural cases to aid interpretation of the long-term nitrate concentration data and<br />

plan future groundwater monitoring that would better link soil and crop management to<br />

groundwater nitrate loading on timescales that are meaningful (i.e. ideally within a year).<br />

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271 - Field evaluation of nitrate transport and matrix storage<br />

processes in Prince Edward Island’s fractured sandstone aquifer<br />

Amanda Malenica, Steven Chapman, Beth Parker, & John Cherry<br />

G360 Centre for Applied Groundwater Research, University of Guelph, Ontario, Canada<br />

Mark Grimmett & Yefang Jiang<br />

Science and Technology Branch, Agriculture and Agri-Food Canada, Charlottetown, Prince<br />

Edward Island, Canada<br />

Cathy Ryan<br />

Department of Geoscience, University of Calgary, Calgary, Alberta, Canada<br />

The province of Prince Edward Island (PEI) is unique in Canada because 100% of the<br />

population is reliant on groundwater for drinking water supply. Of PEI’s total land area,<br />

42% is cleared for agricultural use, 15% of which was planted with potatoes in 2014 (PEI<br />

DAF, 2014). Nitrate concentrations have increased steadily in municipal and domestic<br />

wells and in surface water since the mid-1980s, as have the production of potatoes. Ecological<br />

impacts are detrimental to estuarine biota and evidenced by visible eutrophication<br />

and anoxic events. Although beneficial management practices (BMPs) have been identified<br />

and implemented, groundwater and surface water nitrate concentrations have not decreased<br />

substantially. The accumulation of nitrate mass diffusing into the porous rock matrix<br />

over time from fractures that dominate groundwater flow could be impeding the rate<br />

of nitrate concentration decrease. The relatively low-K rock matrix between the fractures<br />

constitutes the storage capacity of a dual-domain flow and transport system. Improvements<br />

in groundwater quality resulting from reduced nitrate loading are likely tempered<br />

by back-diffusion of the nitrate stored in the matrix where diffusion back to the fractures<br />

could delay down-gradient improvements in water quality.<br />

The objective of this study was to characterize the nitrate distribution at two different<br />

study sites within a discrete fractured network (DFN) context, including quantitation of<br />

nitrate concentrations in the rock matrix. Continuous cores, up to 45 m deep, were logged<br />

for lithology, discrete fractures and advective pathways. Discrete depth samples were collected<br />

adjacent to fractures and at varying distances into the matrix between fractures to<br />

quantify the immobile nitrate porewater concentrations and evaluate the magnitude of<br />

attenuation by diffusion and redox controlled reactions. Results showed local peaks in<br />

matrix nitrate concentrations, as high as 36 mg/L-N, primarily in the partially saturated<br />

overburden and upper saturated fractured bedrock. Nitrate concentrations did not completely<br />

attenuate with depth. This suggests the denitrification process is not strong, likely<br />

due to lack of electron donors and oxygenated conditions. Multi-level monitoring systems<br />

(MLS) were designed to facilitate high–resolution spatial and temporal measurements of<br />

mobile groundwater in fractures (hydraulic head, nitrate and other major ions and isotopes).<br />

Results demonstrate the influence of various mechanisms, including matrix diffusion<br />

and redox conditions, on the movement and attenuation of nitrate. Understanding<br />

these controlling processes is critical to informing conceptual models of flow and transport<br />

in sedimentary bedrock aquifers and understanding efficacy of BMP implementation and<br />

for development of sustainable agricultural practices.<br />

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279 - Groundwater nitrate leaching under various land uses on<br />

the Abbotsford Sumas Aquifer<br />

Alison Schincariol, Shawn E. Loo & M. Cathryn Ryan,<br />

Geoscience, University of Calgary, Calgary, Alberta, Canada<br />

Martin Suchy<br />

Environment Canada, Vancouver, BC, Canada<br />

Bernie Zebarth<br />

Agriculture and Agri-Food Canada, Fredericton, NB<br />

Groundwater nitrate contamination in the Abbotsford Sumas Aquifer has been recognized<br />

as early as the 1970s, and widespread aquifer contamination since the 1990s. Although<br />

other sources are present on the aquifer, standard agricultural practices have been<br />

identified as the main nitrate source. Understanding the direct influence of soil and crop<br />

management on groundwater nitrate leaching is important to support beneficial management<br />

practices. Evolving agricultural land use over the past decades reflects a variety of socio-economic<br />

conditions, however. Since nitrate leaching is different under different land<br />

uses, additional research is required to understand the timing and extent of groundwater<br />

nitrate leaching in each new type of land use.<br />

While recent research has worked with cooperators on to evaluate the timing a rate of nitrate<br />

leaching under raspberries, significant blueberry planting have occurred over the past<br />

decade. This field research uses high-resolution passive diffusion sampling wells installed<br />

immediately downgradient of varying land uses of interest, including blueberries. A time<br />

series of high-resolution nitrate profiles are interpreted to evaluate nitrate leaching with<br />

respect to land use upgradient of each of the three wells.<br />

In addition to providing insight into nitrate leaching under different land uses, the vertical<br />

profiles are interpreted holistically in the context of aquifer wide groundwater flow, land<br />

use, and vertical nitrate distribution.<br />

POSTER SESSION: Flow and Transport in<br />

Fractured Rock<br />

Thursday October 29, 16:40<br />

Room: Regent<br />

148 - Towards effective First Nations’ source water protection: A<br />

groundwater-focused study for decision-making and long-term<br />

planning<br />

Rachael Marshall, Jana Levison, & Edward McBean<br />

School of Engineering, University of Guelph, Guelph, Ontario, Canada<br />

First Nations in Ontario are facing many complex water management issues that put them<br />

at higher risk than other communities for source water contamination. While source water<br />

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protection (SWP) has been an important priority for municipalities in Ontario under the<br />

Clean Water Act since 2006, there has been little First Nations’ participation in these processes<br />

for a variety of reasons. First Nations are often constantly in a state of crisis management,<br />

with little time or resources to attend SWP Committee meetings, for example. First<br />

Nations have also voiced concern over their lack of input and the general lack of cultural<br />

recognition in these processes . The Chiefs of Ontario have highlighted that although it is<br />

well known that increased First Nations involvement in SWP would reduce rising expenditures<br />

on drinking water infrastructure, governments continue to regard on-reserve SWP<br />

as a low priority. Current Canadian federal guidelines for First Nations’ on-reserve SWP<br />

planning discard hydrogeological studies as too expensive to carry out, and recommend using<br />

‘rules of thumb’ to determine wellhead protection zones. However, particularly for First<br />

Nations situated above sensitive aquifer settings such as shallow fractured sedimentary<br />

bedrock, this lack of hydrogeological data leaves communities unprepared and vulnerable<br />

to a host of potential drinking water threats. To this extent, the University of Guelph has<br />

partnered with the Chippewas of Nawash Unceded First Nation – a community situated<br />

above fractured sedimentary bedrock – to develop an effective SWP process for the<br />

community. This research aims to develop an improved understanding of groundwater<br />

processes in fractured bedrock through the use of anthropogenic tracers and 7-channel<br />

CMT multilevel monitoring systems installed in three retrofitted five- and six-inch drinking<br />

water wells. Field activities completed to provide aquifer characterization data include<br />

conducting pumping tests on existing wells in the study area to investigate aquifer yield;<br />

collecting downhole geophysical data (conductivity and resistivity, gamma ray, temperature,<br />

and acoustic televiewer) to characterize the subsurface and design the multilevel systems;<br />

collecting field parameters such as temperature, pH, EC, DO, ORP and turbidity;<br />

and installing new multilevel monitoring systems in unused five- and six-inch diameter<br />

wells. The project also aims to determine what implications this fractured rock aquifer<br />

data may have on SWP processes, particularly for Indigenous communities with limited<br />

resources located in these vulnerable hydrogeological systems. These findings will be used<br />

to inform several participatory processes (e.g., focus groups, community events) to develop<br />

a functioning SWP plan for the community.<br />

287 - Temporary Sensor Deployments: a Method for Improved<br />

Insight into Hydraulic Variations and Design of Permanent<br />

Multilevel Installations<br />

Peeter Pehme, Beth Parker, Ryan Kroeker, Steven Chapman, & John Cherry.<br />

G360 Centre for Applied Groundwater Research, University of Guelph, Ontario, Canada<br />

Detailed investigations of groundwater flow through fractured rock are consistently progressing<br />

towards an increased focus on hydraulic characterization of both large and small<br />

aperture fractures, the latter having an important role on matrix diffusion processes influencing<br />

plume transport and fate. With increased frequency, the field investigations progress<br />

to the installation of one of several available detailed multilevel monitoring systems<br />

(MLS) to monitor pressure and/or variations in groundwater chemistry. Inevitably the<br />

choice of which MLS to use and its design (i.e. details of port and seal intervals) is a<br />

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compromise between: the number of available ports, borehole condition and potential for<br />

blending hydro-stratigraphic units or missing key flow zones. The importance of these<br />

compromises is heightened when the MLS is to be used for monitoring a tracer test without<br />

adequate data to prioritize critical flow zones.<br />

Temporary sensor deployments (TSDs) were originally designed in response to the challenge<br />

of developing a method for continuously monitoring an injection of heated water as<br />

a tracer in a series of down-gradient monitoring wells. The primary goal was to measure<br />

subtle changes in both the temperature of the groundwater and pressure as near to continuously<br />

in space and time as possible within the five down-gradient monitoring wells. The<br />

system consists of the temporary installation of both pressure and high sensitivity (0.0001<br />

C°) temperature sensors at numerous (10 or more) discrete depth intervals hydraulically<br />

isolate by a blank polyurethane borehole liner and thermal logging. The depth and length<br />

of the TSD intervals is designed considering both rock core and geophysical data.<br />

Subsequently, the deployment of a TSD has proven a valuable pre-screening tool for planning<br />

permanent multi-level system (MLS) installations. The TSD has also provided insight<br />

into other types of hydraulic testing such as lining boreholes and thermal logging.<br />

The system is entirely reusable and reconfigurable as appropriate for another location. Data<br />

from sites in California and in Prince Edward Island are presented to demonstrate the<br />

process, the detailed resolution of the system, and the utility of the approach.<br />

302 - New insights from field deployments of fibre optic<br />

distributed acoustic sensors to characterize a bedrock aquifer<br />

Jonathan Munn & Beth Parker<br />

G360 Centre for Applied Groundwater Research, University of Guelph, Ontario, Canada<br />

Thomas Coleman, Michael Mondanos, & Athena Chalari<br />

Silixa Ltd, Elstree, Hertfordshire, United Kingdom<br />

Distributed fibre optic sensing is a relatively new technology that allows continuous measurements<br />

to be made along the entire length of a fibre optic cable. Borehole applications<br />

of distributed fiber optic sensing have been traditionally applied in deep oil and gas wells;<br />

however, recent technological advances have brought the sensitivity and spatial resolution<br />

to the point where shallow (


with a fibre optic cable. A new cable coupling technique using a flexible borehole liner was<br />

tested and was shown to be highly effective for enhancing the seismic signal recorded with<br />

the DAS. A comparison between two different cable structures, tight buffer and loose tube,<br />

were also examined and it was determined that the different structures can strongly influence<br />

the amplitude of the seismic signal. With good cable coupling, the DAS can provide<br />

high-resolution VSPs to provide information on the bedrock aquifer matrix and optimal<br />

cable structures can help maximize the signal to noise ratio of the profile.<br />

297 - Depth-discrete contaminant mass composition and<br />

concentration distribution emanating from an aged DNAPL source<br />

zone in sedimentary rock<br />

A. Buckley, J.R. Meyer, & B.L. Parker<br />

G360 Centre for Applied Groundwater Research, School of Engineering, University of<br />

Guelph, Guelph, Ontario, Canada<br />

Prior to 1970 an estimated 72,700 L of dense non-aqueous phase liquids (DNAPLs)<br />

were released into the subsurface at a site in south central Wisconsin. Investigations at<br />

the site found that the DNAPL accumulated about 56 m bgs in a fractured sandstone<br />

unit. Groundwater flow through the DNAPL source zone over three decades resulted in<br />

a dissolved phase mixed organic contaminant plume extending about 3 km downgradient.<br />

Evaluation of potential remedial options requires quantification of the mass and phase<br />

distribution in and near the DNAPL source zone. In 2014, five holes were continuously<br />

cored to between 55 and 63 m bgs in a transect downgradient of the source zone. The core<br />

lithology and fractures were logged in detail and over 630 rock samples were taken (at least<br />

1 per 30 cm) from the continuous cores for extraction and analysis of the contaminants<br />

of concern. A comprehensive suite of geophysical and hydro-physical logs were collected<br />

from each of the boreholes and all of the data was utilized to design high resolution multilevel<br />

systems (MLSs) for each borehole. Hydraulic heads were measured and groundwater<br />

samples for contaminant analyses were collected from the MLSs. The rock core contaminant<br />

profiles provide a quantitative and high resolution view of the contaminant mass<br />

and phase distribution in the rock matrix; commonly showing over an order of magnitude<br />

change in concentration across less than 1 m of depth. The groundwater contaminant<br />

profiles collected from the multilevel systems represent the contaminant distribution in the<br />

fractures. Integration of the data sets provides a robust understanding of the two-dimensional<br />

contaminant mass and phase distribution along a transect orthogonal to groundwater<br />

flow to show the concentration distribution and mass composition relative to the<br />

high permeability fractures and mass stored in the lower permeability matrix immediately<br />

downgradient of the DNAPL source zone. Ultimately the variability in the contaminant<br />

composition and concentration at different spatial scales across this transect will be compared<br />

to geologic and hydrogeologic properties to provide additional insights into controls<br />

on contaminant transport and fate in sedimentary rock.<br />

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298 - Fracture network and groundwater flux characterization<br />

using a suite of high resolution methods in a sedimentary<br />

bedrock aquifer<br />

Lucas A.F.S. Ribeiro, Jessica R. Meyer, & Beth L. Parker<br />

G360 Centre for Applied Groundwater Research, School of Engineering, University of<br />

Guelph, Guelph, Ontario, Canada<br />

In fractured rocks, contaminant distribution and flux are strongly influenced by the characteristics<br />

and connectivity of fracture networks. This study focuses on characterizing the<br />

fracture network and hydraulics along a 2-D transect down-gradient of a DNAPL source<br />

zone in sedimentary rock. Five boreholes were continuously cored along the transect to<br />

depths between 55 and 63 mbgs. The lithology, sedimentary structures, and fractures observed<br />

in core were described in detail and were complemented by a comprehensive suite of<br />

borehole geophysics collected in the open boreholes. Active line source (ALS) temperature<br />

logging was collected in FLUTe lined holes to identify hydraulically active fractures under<br />

ambient conditions and hydraulic conductivity data were collected from FLUTe transmissivity<br />

profiling and straddle packer testing. Additionally, transient hydraulic heads were<br />

collected using transducer arrays installed behind FLUTe liners. The data collected from<br />

the core and open and lined boreholes were used to design Westbay MLSs to provide high<br />

resolution head profiles. 3-D fracture network characterization is achieved by combining<br />

the 5 transect borehole datasets with 11 boreholes containing similar datasets. Fracture<br />

scan-line surveys were also done in analogous formations in outcrops to provide regional<br />

structural trends and to inform fracture lengths, especially for vertical joint sets that inform<br />

the mechanical unit boundaries. The application of numerous high resolution borehole<br />

methods and the combined use of surface and borehole fracture datasets contribute to the<br />

definition of the site specific fracture network. The fracture network information is then<br />

integrated with the hydraulic data to provide robust estimates of groundwater flux across<br />

the 2-D transect enhancing the understanding of the present contaminant distribution and<br />

providing key information for discrete fracture network numerical models for groundwater<br />

flow and contaminant transport.<br />

POSTER SESSION:<br />

Groundwater Issues from Mining &<br />

Aggregates<br />

Thursday October 29, 16:40<br />

Room: Regent<br />

169 - Numerical Groundwater Modeling of the Lithium Brine<br />

Extraction at the Salar de Atacama<br />

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Steven G. Shikaze & Benjamin L. Bolger<br />

Matrix Solutions Inc., Breslau, Ontario, Canada<br />

Mark King<br />

Groundwater Insight Inc., Halifax, Nova Scotia, Canada<br />

Hector Maya<br />

Rockwood Lithium Ltd., Santiago, Chile<br />

Catalina Orb, Jorge Garcia Tascon, & Jaime Solari<br />

SGA, Santiago, Chile<br />

The Salar de Atacama contains one of the world’s largest lithium brine deposits. The<br />

salar (dry salt lake) is located in the Andes in northern Chile, approximately 1,500 km<br />

north of Santiago, near the Chile/Argentina/Bolivia border. Lithium is mined from the<br />

salar by extracting (via pumping) the high salinity brine (over 300,000 mg/L total dissolved<br />

solids) from the geologic materials in the nucleus of the salar. Around the border<br />

of the nucleus, shallow lagoons are a nesting habitat for migratory flamingos, and therefore,<br />

pumping of the brines in the nucleus must consider the potential impact on water<br />

levels at these lagoons.<br />

To examine this impact in the nucleus, a numerical model study has been carried out.<br />

Because the lithium-rich brines in the salar have a fluid density much higher than the<br />

surrounding fresher water, the program SEAWAT was used to simulate brine pumping<br />

in the nucleus, and its effect on (1) the groundwater levels around the lagoons, and (2)<br />

the location of the brine-freshwater interface. The SEAWAT model, which was developed<br />

in parallel with a three-dimensional MODFLOW model for groundwater flow,<br />

was used to examine the sensitivity of model parameters such as hydraulic conductivity<br />

(K), recharge (which is very low over the nucleus), and evaporation (which is very high).<br />

285 - A review of key groundwater issues, eight years after<br />

the start of dewatering at the Victor Diamond Mine, James Bay<br />

Lowlands, Ontario<br />

Simon Gautrey<br />

Amec Foster Wheeler, Hamilton, Ontario, Canada<br />

The Victor Diamond Mine is an open pit mine located in the James Bay Lowlands, approximately<br />

90 km west of the community of Attawapiskat and 120 km east of the Ring of<br />

Fire. The mine is surrounded by contiguous wetlands that extend for thousands of square<br />

kilometers. The limestone bedrock at the site is prone to karst development and the mine is<br />

located within a few kilometers of two rivers, one of which, the Attawapiskat River, is more<br />

than 500 m wide. This submission will review two key issues related to impacts of dewatering<br />

to the wetlands and rivers that were raised as concerns prior to the start of mining and<br />

compare them to observed conditions after eight years of dewatering.<br />

From the beginning, it was known that mining would require large scale dewatering. Both<br />

the mine investors and the Attawapiskat First Nation, on whose traditional lands the mine<br />

is located, needed to know how much dewatering was going to be required and what<br />

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effects dewatering would have on the local environment. For these reasons, the hydrogeological<br />

assessment of the mine was a priority to all parties.<br />

The assessment of the mine was supported by a multi-year hydrogeological investigation<br />

including drilling, pumping tests, groundwater sampling and modelling. This investigation<br />

concluded that construction of a 300 m deep open pit mine in the limestone was feasible,<br />

but would require large scale dewatering with a drawdown cone that would extend<br />

kilometers. There would however, be no long term groundwater related impacts to the<br />

surrounding wetlands or the nearby rivers.<br />

The hydrogeological assessment of the mine underwent several rounds of peer review,<br />

including internal reviews, external reviews, government reviews, and third party reviews.<br />

A number of groundwater issues were identified by reviewers, with several reviewers indicating<br />

that the prospect of wide spread drainage of the muskeg and sudden, uncontrollable<br />

inflows from the rivers as possible reasons to restrict mine development.<br />

Eight years into dewatering at rates of up to 90,000 m 3 /day, neither of these scenarios has<br />

materialized. The purpose of this presentation is not to review the original hydrogeological<br />

investigations, but review the conceptual model more than two thirds of the way through<br />

the project. This will be supported by a review of select monitoring data from the more<br />

than 160 monitoring wells. The presentation will illustrate the local hydrogeology by explaining<br />

why neither widespread wetland drying nor uncontrollable inflows has occurred.<br />

POSTER SESSION: Groundwater Issues from<br />

Oil and Gas Exploration & Production<br />

Thursday October 29, 16:40<br />

Room: Regent<br />

125 - Baseline Groundwater Quality Monitoring and<br />

Unconventional Gas Development<br />

Richard E. Jackson<br />

Geofirma Engineering Ltd, Heidelberg, Ontario, Canada<br />

Dru Heagle<br />

Geofirma Engineering Ltd, Ottawa, Ontario, Canada<br />

It has become standard practice to monitor domestic (i.e., ‘landowner’, ‘farm’ or ‘residential’)<br />

wells to establish the baseline groundwater quality (GWQ) in areas of oil and gas<br />

development. This is because of both regulatory requirements and the proximity of such<br />

water wells to areas of drilling operations that can lead to complaints of perceived GWQ<br />

deterioration from landowners.<br />

However domestic and farm water wells are not scientific instruments designed for sampling<br />

GWQ and they present numerous constraints that need to be understood and accounted<br />

for in such reporting. Given (i) the spatial and temporal variability of GWQ in<br />

154 IAH-CNC 2015 WATERLOO CONFERENCE


aquifers and (ii) the uncertain integrity of domestic and farm wells, there is clearly a burden<br />

of proof on those sampling such wells to demonstrate that the ‘pre-drill’ data collected are<br />

robust and provide reliable information for use in dispute resolution and resource management.<br />

If the only purpose of such ‘baseline’ sampling is the collection of natural gas samples,<br />

then (i) the transient nature of natural gas emissions from oil and gas wells needs to be<br />

considered in terms of monitoring and (ii) sample collection must be optimized to reduce<br />

degassing at the well. Neither constraint is easily overcome with domestic wells.<br />

An exemplary protocol for testing of domestic and farm wells is that developed by Alberta<br />

Environment (Standard for Baseline Water Well Testing for Coalbed Methane/Natural<br />

Gas in Coal Operations, April 2006) that encourages (but does not require) the removal<br />

of the sanitary seal of a landowner’s well in order to conduct both a water-supply ‘yield<br />

test’ and GWQ sampling downhole. The additional expense (~$3,000 per well) of such a<br />

precaution may be considered as part of the cost of acquiring better scientific data from a<br />

water well not designed to yield scientifically reliable GWQ data.<br />

145 - Case Study Source Discrimination of a Benzene Release<br />

Using a Two-Dimensional (2D) Compound Specific Isotopic<br />

Analysis (CSIA) Approach<br />

Natalie Szponar, Brad J. MacLean, Tom H. Grimminck, Heather Stuart, & Rob F. Kell<br />

Dillon Consulting Limited, Oakville, Ontario, Canada<br />

In recent years, Compound Specific Isotope Analysis (CSIA) has emerged as an important<br />

tool in environmental forensics in assessing source(s) at contaminated sites, understanding<br />

comingled plumes and evaluating contaminant attenuation. This case study presents<br />

a Two-Dimensional (2D) CSIA approach that was used to gain a better understanding<br />

of the potential source(s) and age of benzene impacts to groundwater where no definitive<br />

source or release date had been identified.<br />

Extensive groundwater and soil characterization at the site of the case study identified benzene<br />

impacts in soil from 1 to greater than 4 meter below ground surface, with a maximum<br />

identified benzene concentration of 1,500 ug/g in soil; and 939,000 ug/L in groundwater.<br />

Although the characterization has provided a good understanding of the distribution of<br />

the benzene impacts, the source of the identified impacts and the time of release(s) were<br />

unknown. These unknowns were further complicated by the presence of numerous potential<br />

sources and a complex array of underground services and pipelines.<br />

Stable isotope techniques provide a powerful tool for source discrimination. In particular, stable<br />

carbon (δ 13 C) and hydrogen (δ 2 H) isotopes when plotted against each other for a specific<br />

compound (i.e., benzene) [referred to 2D-CSIA] can provide a “fingerprint” plot. This plot<br />

can be used to distinguish between different physical and biological processes affecting the<br />

compound, and may also provide further differentiation between different sources of refined/<br />

manufactured benzene product (based on source material and manufacturing process).<br />

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For this study, impacted groundwater was collected from selected monitoring wells representing<br />

different areas of the site and concentrations of benzene impacts. In addition, a<br />

raw benzene product sample was also collected as a representative example potential source<br />

material from one of the underground pipelines. The 2D-CSIA approach was used on<br />

these samples to provide information on the source and state of the benzene impacts (i.e.,<br />

historic vs. ongoing) and the degree of weathering (i.e., biological, physical, chemical) as<br />

interpreted from the isotope signatures. The results of 2D-CSIA will be discussed within<br />

the limitations of the stable isotope interpretation.<br />

POSTER SESSION: Groundwater/Surface<br />

Water Interaction<br />

Thursday October 29, 16:40<br />

Room: Regent<br />

120 - Moisture loading – the hidden information in observation<br />

well records<br />

Garth van der Kamp<br />

Environment Canada, Saskatoon, Saskatchewan, Canada<br />

It has long been recognized in soil mechanics and hydrogeology that changes of mechanical<br />

load acting on the ground surface lead to changes of fluid pressure in underlying formations.<br />

Barometric pressure changes are a changing surface load and their effects on groundwater<br />

levels are familiar to every hydrogeologist dealing with the “barometric efficiency” of observation<br />

wells. Changes of total moisture (e.g. snow accumulation, surface water, soil moisture,<br />

water table storage) also represent changes of mechanical load and therefore are reflected in<br />

groundwater pressure records for all confined formations. However, moisture loading effects<br />

are obscured by groundwater pressure fluctuations due to other causes, primarily atmospheric<br />

pressure changes, and are therefore generally not recognized. Analysis and removal of the<br />

barometric effects allows identification and analysis of moisture loading effects and can provide<br />

valuable information on the hydrogeology and hydrology of the well site.<br />

Observation wells thus act as large-scale weighing lysimeters. Such “geolysimeters” may<br />

be normal observation wells in confined aquifers and can also be in the form of shut-in<br />

pressure sensors positioned in the interior of thick aquitards, in which case the sensing<br />

area is well defined. Geolysimeters can provide a unique measure of total water storage<br />

changes on a scale commensurate with that of the “pixels” of regional hydrogeological and<br />

hydrological models. Such storage changes are increasingly recognized as a critical link<br />

between precipitation and streamflow in watershed hydrology. Incorporation of moisture<br />

loading theory in numerical models of groundwater-soil moisture-vegetation interactions<br />

can open the way for use of detailed records of groundwater levels to verify and improve<br />

model performance.<br />

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186 - A Determination of the Lower Limit of Vertical Fluxes that<br />

can be Quantified Using Temperature Profiles in Low Permeability<br />

Streambeds<br />

Michael O. McBride 1 & Brewster Conant Jr. 2<br />

1<br />

WorleyParsons Canada, Calgary, Alberta, Canada<br />

2<br />

Department of Earth and Environmental Sciences - University of Waterloo, Waterloo,<br />

Ontario, Canada<br />

Vertical profiles of temperature in streambeds can be modeled to quantify exchanges of<br />

water between groundwater and surface water, but in low permeability and low flux environments<br />

the modeling can yield unreliable or non-unique results. This study was undertaken<br />

to determine the threshold flux below which the influence of advection water (and<br />

heat) can no longer be reliably quantified, because it is so small relative to heat conduction<br />

processes. Thermographs from 1-D vertical arrays of temperature dataloggers deployed in<br />

the top 1.5 m of low permeability streambeds at three different field sites were simulated<br />

using the USGS numerical heat transport model VS2DH and 1DTempPro graphical user<br />

interface. A vertical upward flux of 3.4 x 10 -7 m/s (above the threshold value) was determined<br />

for silty clay till in Logan Drain (Kintore, Ontario). Modeled best fit fluxes of 5 x<br />

10 -8 m/s (marginally above the threshold) and ≤1 x 10 -8 m/s (at or below the threshold),<br />

were determined for the clay streambed deposits of the South and Middle branches of the<br />

Raisin River (near Cornwall, Ontario), respectively. Sensitivity analyses using the South<br />

Branch of the Raisin River data indicated simulated streambed temperature profiles were<br />

practically identical (i.e., non-unique) for specific discharges below 1 x 10 -8 m/s. Although<br />

threshold flux values were site specific and found to be a function of specific discharge,<br />

depth of streambed temperature measurement, and sediment thermal properties, the value<br />

of 1 x 10 -8 m/s was about the minimum reliable flux estimate achievable when using<br />

dataloggers with accuracies of 0.1°C. The threshold flux values had thermal Péclet numbers<br />

(tPe) less than 1 (tPe=1 when contributions to energy transport from advection and<br />

conduction are equal) indicating the Raisin River streambed sites were indeed conduction<br />

dominated. Additional simulations showed that the threshold flux occurs at a flux corresponding<br />

to about tPe=0.1 and so between values of 0.1 and 1.0, advection can still be<br />

quantified. To ensure one can obtain the lowest possible threshold value at a site, high<br />

resolution and accuracy temperature dataloggers should be deployed as deep as feasibly<br />

possible (within the active thermal zone, or at least 1 m deep), both within the zone of<br />

diurnal fluctuations and below to provide optimal transient temperature data to calibrate<br />

the model to. It appears that shallow streambed temperature profiles (≤ 1.5 m) cannot be<br />

used to reliably determine flow directions or magnitudes of fluxes below about 1 x 10 -8 m/s.<br />

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257 - Hydrogeological and geochemical evaluation of the eastern<br />

Minesing Wetland in support of the Hine’s Emerald Dragonfly<br />

(Somatochlora hineana)<br />

Ryan Post<br />

Nottawasaga Valley Conservation Authority<br />

John Spoelstra<br />

Environment Canada, Burlington, Ontario, Canada & Department of Earth and<br />

Environmental Sciences - University of Waterloo, Waterloo, Ontario, Canada<br />

The globally rare Hine’s Emerald dragonfly (Somatochlora hineana) is restricted throughout<br />

its range to calcareous wetlands (marshes, sedge meadows and fens) dominated by<br />

graminoid vegetation and fed primarily by groundwater seeps. To date, the only known<br />

location of the Hine’s Emerald dragonfly in Ontario is the Minesing Wetlands, Simcoe<br />

County.<br />

Characterization of both the eastern Minesing Wetlands groundwater regime and potential<br />

Hine’s Emerald dragonfly habitat was carried out through field campaigns in 2013 and<br />

2014 which consisted of monitoring groundwater levels and annual geochemical sampling<br />

along two transects in addition to updating the ecological lands classification.<br />

The groundwater-dominated regime of the Minesing Wetlands comprises 3 progressive<br />

ecohydrological zones: discharge wetlands systems, flow through wetland system, and the<br />

graminiod fen with the corresponding recharge area situated in the Snow Valley Uplands.<br />

The Minesing Wetlands groundwater is geochemically characterized as calcium-bicarbonate/alkaline.<br />

The source of the groundwater is from the upgradient discharge wetland<br />

systems situated at the base of the bluffs. Groundwater flow direction is locally to the west<br />

towards the Nottawasaga River. The groundwater regime of the generalized uniform 3m<br />

think peat unit overlying the clay wetland bottom within the gramoniod fen is atmospherically<br />

influenced through temperature and precipitation events however levels and temperature<br />

are strongly correlatable. The Minesing Hine’s Emerald habitat is characterized<br />

by very slowly moving water, saturated organic soils (e.g. peat), predominance of ground<br />

level vegetation, and calcium-bicarbonate/alkaline dominated water regime; similar to other<br />

known locations in the USA.<br />

Funding for this project was through the Ministry of Natural Resources and Forestry<br />

Species at Risk Stewardship Fund and by the Environment Canada’s Lake Simcoe/<br />

South-Eastern Georgian Bay Clean-up Fund for the geochemical analysis.<br />

113 - The influence of water table fluctuation on nutrient<br />

dynamics in sand from a freshwater beach environment<br />

Danny Hyumin Oh, Avid Banihashemi, Radmila Kovac, Fereidoun Rezanezhad, &<br />

Philippe Van Cappellen<br />

Ecohydrology Research Group, Waterloo, Ontario, Canada & Department of Earth &<br />

Environmental Science – University of Waterloo, Waterloo, Ontario, Canada<br />

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Water table fluctuations between groundwater and surface water significantly affect the biological<br />

and geochemical functioning of soils. The pulse of oxygen introduced or removed<br />

by cyclic draining and rewetting results in significant oxidation and reduction of redox sensitive<br />

chemical species. Our approach to unravel the biogeochemical implications of water<br />

table fluctuations is to conduct laboratory experiments with soil columns in which the<br />

position of the water table can be manipulated. In this project, we used a novel automated<br />

soil column system where the time course of the water level is imposed via a programmable<br />

multichannel pump. Four undisturbed sand cores (10, 20, 30 and 40 cm length) were<br />

collected from the Burlington beach site and were introduced into four columns in the lab.<br />

The soil columns have ports that are used to install ceramic pore water samplers to characterize<br />

the evolution of pore water chemistry (pH, major anions/cations, nutrients, DOC<br />

and DIC) in soil columns during water table fluctuations. At the end of experiment, the<br />

soil was extruded via the top of the column using a lifting jack and will be sliced every 2 cm<br />

for further solid phase geochemical characterizations. The goal of this study was to better<br />

delineate the role of water table oscillations on nutrient fate and distribution in sand from<br />

a freshwater beach environment.<br />

129 - Effect of freeze-thaw cycles on soil oxygen dynamics<br />

T. Milojevic, F. Rezanezhad, & P. Van Cappellen<br />

Ecohydrology Research Group, University of Waterloo, Waterloo, Ontario, Canada<br />

Freeze-thaw cycles represent a major climate forcing acting on soils at middle and high<br />

latitudes. Freezing and thawing of soils affect their physical properties, biogeochemical<br />

processes, microbial community, and carbon and nutrient budgets, and modulate gas exchanges<br />

between the soil and atmosphere, which, in turn, exerts a strong influence on oxygen<br />

(O 2<br />

) availability within soil environments. To investigate the role of freeze-thaw cycles<br />

on soil oxygen dynamics, a highly instrumented soil column experiment was designed<br />

to realistically simulate freeze-thaw dynamics under controlled conditions. The ability to<br />

monitor changes in O 2<br />

levels in both the gas and aqueous phase is key to understanding<br />

how changes in frequency and amplitude of freeze-thaw cycles affect a soil’s geochemical<br />

conditions and microbial activity. In this study, we perform soil column experiments in a<br />

temperature-controlled environmental chamber. The air temperature of the chamber determines<br />

the soil’s surface temperature, while a band-heater keeps the lower part of the column<br />

at a constant groundwater temperature. This design allows us to reproduce realistic,<br />

time- and depth-dependent temperature gradients in the soil column. High-resolution,<br />

luminescence-based, Multi Fiber Optode (MuFO) microsensors are used to enable continuous<br />

O 2<br />

detection at a high degree of spatial flexibility in the column. High-resolution digital<br />

images of the sensor-emitted light are recorded and light intensity is converted to O 2<br />

concentration via signal image-processing techniques. In this presentation, we will present<br />

preliminary results to assess the hypothesis that freeze-thaw cycles regulate the fluxes of<br />

the greenhouse gases (GHG) not only by acting on the physical transport of gases, but also<br />

on soil microbial respiration via the variations in O 2<br />

availability.<br />

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151 - Prevalence of Arsenic Enrichment Near the Sediment-Water<br />

Interface Along Shorelines of the Great Lakes<br />

Sabina Rakhimbekova, Clare Robinson, & Denis O’Carroll<br />

Department of Civil and Environmental Engineering – University of Western Ontario,<br />

London, Ontario, Canada<br />

The mobility of arsenic in groundwater is controlled by interacting biogeochemical and<br />

hydrological processes – these processes are complicated near surface water-groundwater<br />

interfaces due to the mixing of two distinct water entities. The mixing of anoxic groundwater<br />

with toxic lake water recirculating across the sediment-water interface sets up a reaction<br />

zone characterized by sharp pH and redox gradients where a range of chemicals (e.g.,<br />

arsenic) undergo important transformations. While prior research has revealed arsenic<br />

enrichment near the sediment-water interface along the shores of the Great Lakes (up<br />

to 56 µg/L), there is limited understanding of the ultimate source of arsenic, the physical<br />

and geochemical processes governing the arsenic behaviour and if arsenic enrichment in<br />

beach aquifers is a naturally occurring widespread phenomenon. This paper presents pore<br />

water and sediment chemistry data obtained near the sediment-water interface at a wide<br />

range of permeable Great Lake shorelines. Elevated As concentrations at a number of field<br />

sites indicates the process may be naturally occurring and suggests that lake water with<br />

trace concentrations of arsenic may deliver arsenic to the beach aquifer as it recirculates<br />

across the sediment-water interface. Arsenic may then be sequestered by metal oxides that<br />

precipitate below the beach face in distinct redox zones. The accumulation of arsenic in<br />

the beach aquifer creates a potential risk of elevated arsenic concentrations being rapidly<br />

released back to the surface water under favorable hydrologic and geochemical conditions<br />

(e.g., high organic loading from algae washup). The paper also explores potential scenarios<br />

that may cause mobilization of arsenic from the aquifer and subsequent release to adjacent<br />

surface waters.<br />

152 - Quantification of groundwater discharge along shorelines of<br />

the Great Lakes using Radon-222<br />

Tao Ji & Clare Robinson<br />

Department of Civil and Environmental Engineering – Western University, London,<br />

Ontario, Canada<br />

Groundwater discharge can be a significant pathway for transporting pollutants, including<br />

nutrients, organic contaminants and trace metals, into nearshore waters of the Great<br />

Lakes. Groundwater as a contributor of nutrients to the Great Lakes has received increased<br />

attention in recent years, particularly with respect to the potential for onsite sewage<br />

systems to be a source of elevated nutrient levels in nearshore waters. There is, however,<br />

limited understanding and methods available to quantify the groundwater discharge to the<br />

Great Lakes, including regional-scale methods to identify hotspot areas of discharge. Radon<br />

( 222 Rn, t 1/2<br />

= 3.8 days) is a suitable natural tracer for estimating groundwater discharge<br />

because it is a conservative gas and its activity is typically 3-4 orders of magnitude higher<br />

in groundwater than in surface water. Regional-scale 222 Rn surveys were conducted along<br />

160 IAH-CNC 2015 WATERLOO CONFERENCE


20 km stretches of shoreline in three areas along Lake Huron (Blue Water Beach, Balmy<br />

Beach and La Fontainne Beach) to identify potential hotspot zones with elevated groundwater<br />

discharge. Measurements were conducted with portable instrumentation (RAD 7<br />

and RAD AQUA, Durridge Inc.). Shoreline areas to conduct these regional-scale surveys<br />

were selected based on topography, hydrogeological information and prior published results.<br />

222 Rn activities in groundwater, benthic flux, losses to air and mixing were measured<br />

in specific hotspot area. A steady-state mass balance model which considers the various<br />

sources and sinks of 222 Rn was then applied to estimate groundwater discharge rates. The<br />

challenge of this method is minimizing uncertainties in the 222 Rn mass balance including<br />

quantifying 222 Rn loss through air evasion and mixing, as well as adequately characterizing<br />

222<br />

Rn in the groundwater end-member. Intensive sampling and analysis was conducted to<br />

minimize these uncertainties. The results indicate that high groundwater discharge occurs<br />

primarily in the nearshore, with decreasing discharge rates offshore. Detailed temperature<br />

and hydraulic gradient profiles were also collected at discrete locations within the survey<br />

areas to validate the groundwater discharge rates estimated from the 222 Rn surveys. This<br />

development of methods to evaluate regional-scale groundwater discharge to nearshore<br />

waters is critical for developing more effective and targeted management plans to mitigate<br />

the contribution of groundwater pollutants to nearshore waters.<br />

162 - Effect of groundwater-lake interactions on the transport of<br />

nutrients from groundwater to the Great Lakes along permeable<br />

shorelines<br />

Monica A. McVicar, Alex Hockin, Denis M. O’Carroll, & Clare Robinson<br />

Department of Civil & Environmental Engineering, University of Western Ontario,<br />

London, Ontario, Canada<br />

Groundwater discharge represents a potentially important source of nutrients (NO 3-<br />

, NH 4+<br />

, PO 4<br />

3-<br />

) to nearshore waters of the Great Lakes. While studies have linked anthropogenic<br />

activities (i.e., septic systems, leaky sewers, agriculture) to elevated nutrient<br />

concentrations in shallow permeable coastal aquifers, the ultimate discharge of nutrients<br />

from groundwater to the lakes is not well understood. Prediction of nutrient loading from<br />

groundwater to the lake is complex as it is controlled not only by inland groundwater<br />

nutrient sources but also by transformations occurring as nutrients are transported along<br />

their discharge pathway. In particular, important nutrient transformations may occur close<br />

to the groundwater-lake interface where discharging groundwater mixes with lake water<br />

recirculating across this interface (similar to hyporheic zone processes). Transformations<br />

occurring here may play a disproportionate role in regulating the ultimate flux of groundwater<br />

nutrients to the lake including the ratios and chemical forms of the nutrients. The<br />

objective of this study was to evaluate the way in which the interacting hydrological and<br />

biogeochemical processes occurring near the groundwater-lake interface along permeable<br />

Great Lakes shorelines regulates the loading of nutrients to the lakes from groundwater.<br />

Detailed field investigations were conducted on a fine sand homogeneous beach aquifer on<br />

Lake Huron to characterize the geochemical conditions close to the groundwater-lake interface<br />

and their effect on the discharge of groundwater-derived nutrients. To quantify the<br />

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nearshore groundwater chemistry including nutrient concentrations, multi-level samplers<br />

up to a depth of 3 m were installed along transects perpendicular to the shoreline. Vertical<br />

arrays of pressure transducers were also installed to infer the groundwater flow gradients<br />

and water exchange across the groundwater-lake interface. At this site NO 3-<br />

and PO 4<br />

3-<br />

concentrations up to 110 mg/L and 450 µg/L, respectively, were observed in the nearshore<br />

aquifer with concentrations decreasing towards the groundwater-lake interface. Nutrient<br />

distributions in the nearshore aquifer were also monitored to capture seasonal variability as<br />

well as to examine the extent to which lake forcing such as waves influence the geochemical<br />

conditions close to the groundwater-lake interface.<br />

167 - Influence of oceanic processes on groundwater flow and<br />

contaminant transport on Sable Island, Nova Scotia<br />

Victoria Trglavcnik, Clare Robinson, & Denis O’Carroll<br />

Department of Civil and Environmental Engineering – University of Western Ontario,<br />

London, Ontario, Canada<br />

Dean Morrow, Darren White, Viviane Paquin, & Kela Weber<br />

Department of Chemistry and Chemical Engineering, Environmental Sciences Group –<br />

Royal Military College of Canada, Kingston, Ontario, Canada<br />

Many coastal aquifers worldwide are impacted by human activities. Groundwater flows<br />

in unconfined coastal aquifers can be extremely complex because the aquifer is exposed to<br />

dynamic ocean fluctuations such as tides and waves (Robinson, 2006, 2007, 2009; Licata,<br />

2011; Heiss, 2014). While the influence of oceanic fluctuations on groundwater levels,<br />

groundwater flow patterns and salinity distribution in coastal aquifers has been well studied,<br />

the subsequent impact on the fate and transport of groundwater contaminants is not<br />

well understood. Due to the complexity of coastal aquifers most previous studies have<br />

used only numerical modelling of idealized systems to examine groundwater contaminant<br />

behaviour. No prior studies have combined field and numerical modelling to rigorously<br />

evaluate the fate and transport of groundwater contaminants in dynamic coastal aquifers.<br />

This paper presents field observations combined with numerical groundwater modelling to<br />

evaluate the influence of oceanic fluctuations and environmental factors (e.g. tides, waves, storm<br />

events, rainfall) on the groundwater dynamics and subsequent fate of groundwater contaminants<br />

on Sable Island, Nova Scotia. Sable Island is a narrow sandy barrier island (maximum<br />

width of 1.5km) located 175km southeast of Nova Scotia, Canada. Zones of elevated soil and<br />

groundwater contamination by various PHCs, PAHs and metals are present on the island from<br />

historical operations. A better understanding of fate and transport of these contaminants will<br />

assist in developing sustainable management practices to ensure the integrity of the island’s<br />

ecosystem. Long-term continuous water level data from twenty wells installed across the island,<br />

and in the contamination around the areas of concern, were first analyzed to determine the external<br />

forces driving the coastal groundwater dynamics. Following this, a numerical groundwater<br />

flow and transport model of the aquifer contamination zone was developed to evaluate the<br />

effects of the transient flow conditions on the fate and transport of the observed contaminant<br />

plumes. The findings provide valuable insights transferable to other coastal environments where<br />

oceanic fluctuations control groundwater flow and contaminant transport processes.<br />

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310 - Assessing the Impact of a Mine Tailings Rehabilitation<br />

Strategy on Nearby Stream and Groundwater Flows<br />

S.D. Donald, R.G. McLaren, M. Gunsinger, F. Junqueira & B. Reiha<br />

Golder Associates Ltd., Cambridge, Ontario, Canada<br />

An alternatives assessment was completed to evaluate feasible rehabilitation strategies to<br />

manage the potential risk posed by gas emissions from a historic tailings facility at a decommissioned<br />

mine site. The preferred solution that was selected involves the construction<br />

of a cover over the surface of the tailings, which provides a barrier of saturated material<br />

that would significantly reduce gas migration to the surface. While the cover provides the<br />

benefit of mitigating gas emissions, a potential concern with this strategy was that the cover<br />

will be constructed with low-permeable soil materials that may promote surface runoff<br />

and reduce groundwater recharge. Potential effects in turn could be a lowering of the water<br />

table, desaturation of peat layers that underlie the tailings, and the possible oxidation and<br />

re-mobilization of currently adsorbed waste products within the peat layer. There were<br />

also concerns with respect to the influence of this reduced recharge on the groundwater /<br />

surface water interactions of a stream channel immediately adjacent to the tailings facility.<br />

In order to assess the impacts that the cover system may have on the local flow system, a<br />

3-dimensional, integrated, fully-coupled, surface/subsurface numerical modelling approach<br />

was utilized. An existing calibrated subsurface flow model was used as a starting point. A preliminary<br />

base case steady-state simulation with average annual surplus water was developed<br />

for the existing site conditions (no cover). Subsequent simulations with average monthly<br />

surplus water were then carried out for the base case and two cover system scenarios with<br />

reduced infiltration. Time-varying infiltration rates for the tailings facility (covered and uncovered)<br />

where derived from a separate 1D numerical flow model and applied as a specified<br />

flux boundary condition in the tailings on the top surface of the 3D model.<br />

Modelling results indicate that the placement of the cover would have minimal impact on<br />

the elevation of the water table and the saturation of the peat layer underlying the tailings,<br />

and the surface water flow magnitude in an adjacent stream. However, the model results<br />

did suggest that there could be significant impacts on the spatial location and temporal<br />

variation of zones where the adjacent stream was ‘gaining’ or ‘losing’ water to and from the<br />

subsurface. While not the case for this particular site, this could have a negative impact on<br />

watercourses where the aquatic systems rely on these relationships. In this particular application,<br />

the advantages of the integrated modelling approach, over traditional uncoupled or<br />

loosely-coupled approaches, becomes evident. With the fully integrated approach, subtle<br />

changes in the surface/subsurface flow relationships are directly visible.<br />

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POSTER SESSION: Innovation in the<br />

Remediation of Contaminated Sites<br />

Thursday October 29, 16:40<br />

Room: Regent<br />

321 - Application of Push-Pull Tests to Define Biogeochemical<br />

Controls on Selenium and Nitrate Attenuation in Saturated Coal<br />

Waste Rock<br />

Marcie Schabert, M. Jim Hendry, & S. Lee Barbour<br />

Department of Geological Sciences – University of Saskatchewan, Saskatoon, Saskatchewan,<br />

Canada<br />

Surface mining of steelmaking coal in the Elk Valley, British Columbia, Canada, has resulted<br />

in the release of constituents of interest such as selenium (Se) and nitrate (NO 3-<br />

) into<br />

the Elk River. Oxidation of sulfide minerals in the unsaturated coal waste rock generates<br />

water-soluble forms of Se (selenite (SeO 3<br />

2–<br />

) and selenate (SeO 4<br />

2-<br />

) that are mobile in the<br />

aqueous phase. Nitrate, introduced to the waste rock through the blasting process, is also<br />

water soluble and mobile in the aqueous phase. Limited data suggests that the attenuation<br />

of Se and NO 3<br />

via reduction can occur in saturated waste rock, therefore the placement of<br />

waste rock in topographic low areas, such as backfilled pits, could create saturated conditions<br />

in which Se and NO 3-<br />

attenuation would be enhanced. A push-pull test is an in situ<br />

method that can be used to examine physical, chemical, and biological characteristics of an<br />

aquifer. Testing involves injecting water spiked with conservative and reactive tracers into<br />

the formation, allowing the spiked water to react within the formation for a period of time,<br />

and then extracting it. Dilution of the injected water can be quantified by monitoring the<br />

concentration of the conservative tracers during extraction. Any loss of reactive tracer beyond<br />

that due to dilution can be attributed to physical-chemical reactions in the formation.<br />

In this study, push-pull tests were used to determine if SeO 4<br />

2–<br />

and/or NO 3-<br />

can be attenuated<br />

within saturated waste rock. Chloride (Cl - ) and deuterium in the water molecules<br />

(δ 2 H) were used as conservative tracers, and either dissolved oxygen (O 2<br />

), SeO 4<br />

2–<br />

, NO 3-<br />

,<br />

or both SeO 4<br />

2–<br />

and NO 3-<br />

were used as reactive tracers. The injection volume for these<br />

tests was between 910 to 1005 L of spiked water, and the reaction time ranged between<br />

19 and 67 hours (h). Extraction was conducted for 8 h, with samples for geochemical<br />

analysis being collected on either 15 or 30 min intervals. In addition to geochemical samples,<br />

pH, temperature, and reduction potential were monitored during both the injection<br />

and extraction phases. Concentrations of tracers were normalized relative to the injection<br />

concentration of each tracer. Normalized plots of reactive tracers were compared to those<br />

of conservative tracers for each test to determine if O 2<br />

, SeO 4<br />

2–<br />

, and NO 3<br />

reduction is occurring<br />

in the saturated waste rock at the scale of the testing.<br />

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268 - Smouldering Combustion of NAPLs in Soil: Advancing<br />

Process Understanding in the Context of STAR Remediation<br />

Marco A.B. Zanoni & Jason I. Gerhard<br />

Department of Civil and Environmental Engineering, University of Western Ontario,<br />

London, Ontario, Canada<br />

Jose L. Torero<br />

School of Civil Engineering, The University of Queensland, Brisbane, Queensland, Australia<br />

Smouldering combustion is defined as an oxygen-limited, flameless form of combustion.<br />

Glowing red charcoal in a barbeque is a typical example. Smouldering is the governing<br />

process of an innovative soil remediation technology called Self-sustaining Treatment for<br />

Active Remediation (STAR), which has been proved an effective approach to successfully<br />

destroy nonaqueous phase liquids (NAPLs) in soil with minimal energy input. A<br />

key feature of STAR is that the reaction is self-sustaining, meaning that once ignited,<br />

the reaction will continue using the energy released from the exothermic oxidation of the<br />

contaminant (i.e., fuel) as long as sufficient contaminant and oxygen is available. Smouldering<br />

has long been studied in a fire safety context, focused almost exclusively on porous<br />

solids, such as foam cushions and insulation; very little is known about smouldering of<br />

liquid fuels (i.e., NAPLs) in an inert solid porous matrix (i.e., soil). Moreover, smouldering<br />

is a complex thermodynamic process, involving kinetic pyrolysis and oxidation reactions,<br />

multiple heat transfer mechanisms and ultimately a balance between energy recirculated<br />

ahead of the front and heat losses. The objective of this work was to develop a better fundamental<br />

understanding of STAR thermodynamics, and the chosen methodology was to<br />

build a numerical model to simulate smouldering behaviour in a one-dimensional system.<br />

A set of partial differential equations representing the conservation of mass, momentum,<br />

and energy were combined with appropriate chemical reactions solved using COMSOL<br />

Multiphysics. Several kinetic reaction frameworks were developed for the pyrolysis and<br />

oxidation of coal tar and the kinetic parameters (pre-exponential factor, activation energy,<br />

reaction order, and stoichiometric coefficients) were estimated through applying a genetic<br />

algorithm to thermogravimetric analysis data. Furthermore, local thermal non-equilibrium<br />

between the injected air and the soil/NAPL was used in the energy conservation. The heat<br />

transfer process was better simulated by the development of a new empirical correlation to<br />

calculate the convective heat transfer coefficient (hsf) between the soil and injected air over<br />

a wide range of in situ parameters. Ongoing work includes further developing the model,<br />

calibrating it to 1D experiments, and simulating a wide range of smouldering scenarios.<br />

Overall, this work is revealing that thermodynamic modelling is an essential tool for better<br />

understanding the complex interactions of mass and heat transfer underlying STAR propagation,<br />

and providing insights into process optimization and application limits.<br />

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278 - Microbial Subsurface Repopulation Following In Situ STAR<br />

Remediation<br />

Gavin Overbeeke & Jason Gerhard<br />

Department of Civil and Environmental Engineering – University of Western Ontario,<br />

London, Ontario, Canada<br />

Elizabeth Edwards<br />

Department of Chemical Engineering and Applied Chemistry – University of Toronto,<br />

Toronto, Ontario, Canada<br />

Gavin Grant<br />

Savron, Guelph, Ontario, Canada<br />

STAR (Self-sustaining Treatment for Active Remediation) is an emerging remediation<br />

technology that employs a self-sustaining smouldering reaction to destroy nonaqueous<br />

phase liquids (NAPLs) in the subsurface. The reaction is a slow, controlled, flameless exothermic<br />

oxidation reaction that proceeds strictly through NAPL-contaminated soil. The<br />

reaction front travels at rates of 0.5 to 5 m per day and subjects the soil to temperatures<br />

between 400°C and 1000°C. As a result, not only does STAR cause in situ destruction of<br />

NAPL, but it thoroughly dries and likely sterilizes the soil through which it passes. The<br />

objective of this work is to monitor the re-saturation of the soil over time and quantify<br />

the microbial repopulation of the treated source zone. STAR is currently being applied as<br />

a full scale, in situ remedy for coal tar beneath a former creosol manufacturing facility in<br />

New Jersey, USA. STAR is being applied at two depths where significant coal tar contamination<br />

is observed: a shallow fill unit and a deeper fine sand alluvial aquifer, both beneath<br />

the water table. This project includes analysis of soil cores and groundwater samples taken<br />

from both depths immediately after STAR treatment and at regular intervals afterwards,<br />

allowing time for groundwater to reinfiltrate and for microbial populations to reestablish.<br />

Samples were also taken from outside the treatment zones to provide background data.<br />

Both soil and groundwater samples were analyzed for total number of microorganisms<br />

and microbial diversity using Pyrotag analysis. Pyrotag analysis subjects DNA within a soil<br />

sample to quantitative Polymerase Chain Reaction (qPCR), which is used to estimate the<br />

abundance of microorganisms, as well as Amplicon sequencing of 16srRNA genes, which<br />

provides an estimation of microbial composition and diversity. To inform the field research<br />

program, an initial bench top laboratory study using site soil and natural groundwater<br />

is exploring the rate at which STAR-treated soil is repopulated with naturally occurring<br />

microorganisms. The expectation of this research program is to provide insight into the<br />

changes in microbial abundance and diversity as the subsurface transitions from contaminated<br />

to remediated and then repopulated soil. The rate at which the microbial abundance<br />

changes, as well as the variations seen in microbial diversity will be a key factor in determining<br />

the rate at which the subsurface improves towards its natural soil function.<br />

196 - Importance of Groundwater Flow Direction Match in<br />

Groundwater Flow Model Calibration<br />

Hongze Gao & Steve Harris<br />

Conestoga Rovers & Associates, a GHD Company, Waterloo, Ontario, Canada<br />

166 IAH-CNC 2015 WATERLOO CONFERENCE


In groundwater flow model calibration, it is a tradition and standard to look at the calibration<br />

error statistics. As a rule of thumb when the statistic errors are minimized, the<br />

simulated groundwater elevations are supposed to match the observed elevations at the<br />

available/selected calibration targets. Thus the groundwater flow directions are theoretically<br />

considered to match as well. However, quite often it is the case that groundwater flow<br />

directions do not match to the best for a long term average flow condition even when the<br />

minimized calibration errors are found. Reasons may include: 1) the observation event (as<br />

calibration targets) does not necessarily represent the long term average conditions due to<br />

groundwater elevation fluctuations (and hence groundwater flow direction variations); 2)<br />

groundwater elevation measurement errors; 3) over simplification of the site conditions<br />

such as lumping different hydrogeological units to a single model layer where a vertical<br />

hydraulic gradient may exist, etc. For a contaminated site where a plume in groundwater<br />

is fully delineated, a long term groundwater flow direction is obtained that should be a<br />

primary calibration target to focus on. Focusing on groundwater flow direction match in<br />

groundwater flow model calibration is extremely important when using a calibrated model<br />

to optimize the design of the groundwater remediation system.<br />

289 - Self-Sustaining Treatment for Active Remediation (STAR) –<br />

Vapour Emissions Characterization and Mitigation<br />

Cody Murray & Jason I. Gerhard<br />

Department of Civil & Environmental Engineering - Western University, London, Ontario,<br />

Canada<br />

Gavin P. Grant, Grant Scholes, & Dave Major<br />

Savron Solutions, Guelph, Ontario, Canada<br />

Self-sustaining Treatment for Active Remediation (STAR) is a novel technology based on<br />

the principles of smouldering combustion where the contaminants, primarily Non-Aqueous<br />

Phase Liquids (NAPLs), are the fuel for the reaction. STAR is self-sustaining in that,<br />

following a short duration, localized ignition event, the combustion front propagates<br />

through the contaminated material without any externally added energy. The reaction is<br />

supported and accelerated by air injection. This technology is capable of destroying greater<br />

than 99.9% of contaminant / waste mass and has many potential applications to the oil and<br />

gas, manufacturing, and utility industries. The STAR process is well suited for the in situ<br />

treatment of NAPL source zones as well as the ex situ treatment (STARx) of excavated<br />

soils, drilling muds, or other contaminated soils. In addition, STARx can be used for the<br />

treatment of organic wastes such as waste oils and lagoon sludges when the waste material<br />

is mixed with a porous media to establish the conditions required for smouldering combustion<br />

reactions to take place.<br />

The objective of this work is to study the gaseous emissions from STAR and STARx. In<br />

particular, this work seeks to characterize the emissions and determine the factors affecting<br />

the volatile emissions rate and its relationship to treatment efficiency / remediation<br />

performance. Specific attention is being given to characterize (i) combustion gases, such<br />

as carbon dioxide (CO 2<br />

), carbon monoxide (CO), and oxygen (O 2<br />

), (ii) volatile organic<br />

compounds (VOCs), and (iii) aerosols/oil mists. These are being quantified for both the<br />

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in situ treatment of coal tar at a field site as well as for the ex situ destruction of crude oil<br />

tank bottoms and hydrocarbon impacted soils. The work is exploring the sensitivity of the<br />

emissions to key system parameters (e.g., air flow rate, water content) and testing ways to<br />

mitigate the emissions. This work is expected to demonstrate the very high rate of mass<br />

destruction occurring during STAR/STARx application and also demonstrate how to understand,<br />

minimize, and manage the emissions that may occur.<br />

POSTER SESSION: Regional Groundwater<br />

Systems<br />

Thursday October 29, 16:40<br />

Room: Regent<br />

133 - Isotope and hydrogeochemical characterisation of<br />

groundwater in a degrading permafrost environment in northern<br />

Quebec, Canada.<br />

Marion Cochand 1 , John Molson 1 , Jean-Michel Lemieux 1 , Johannes A.C. Barth 2 ,<br />

Robert Van Geldern 2 , Richard Fortier 1 , & René Therrien 1<br />

1<br />

Centre d’études nordiques, Université Laval, Québec, Québec, Canada,<br />

2<br />

Friedrich-Alexander-Universität, Erlangen-Nürnberg, Germany<br />

One consequence of global warming already being felt in northern Quebec is permafrost<br />

thaw. Although its influence on groundwater resources is still largely unknown, it will<br />

probably lead to increased groundwater recharge and changing flow dynamics.<br />

A two square kilometer watershed in a discontinuous permafrost zone close to the Inuit<br />

village of Umiujaq (northern Quebec, Canada) has been instrumented to assess the influence<br />

of permafrost degradation on groundwater resources. The catchment is located<br />

in the Tasiapik valley, which is mainly filled with glacial-fluvial and Quaternary marine<br />

sediments. The area became deglaciated about 7500 years ago, and permafrost mounds<br />

have formed within marine silts. The valley has two aquifers: an unconfined shallow sandy<br />

aquifer located in the upper part of the valley, and a deeper confined aquifer in fractured<br />

bedrock below the permafrost mounds.<br />

Nine observation wells are being used to monitor both aquifers in a longitudinal transect<br />

along the valley with measurements of groundwater levels and temperature profiles. In<br />

addition, ground- and surface water, as well as precipitation and permafrost samples were<br />

collected during three field campaigns in the summers of 2013 and 2014, and in November<br />

2014 for hydrogeochemistry (dissolved metals and major anions), stable isotope<br />

analysis (δ 18 O and δ 2 H) and dating ( 14 C and 3 H/ 3 He). The aim was to identify the origin<br />

of groundwater (i.e. proportions from rain, snow and permafrost), to characterize groundwater<br />

evolution along the flow path, and to understand seasonal dynamics together with<br />

determination of residence time.<br />

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First results from stable isotope analyses show groundwater depletion in δ 18 O and δ 2 H<br />

that may result from permafrost thawing which recharges the aquifer with water depleted<br />

in heavy isotopes. In contrast, shallow thermokarst lakes show enriched signals in δ 18 O<br />

and δ 2 H resulting from evaporation. Groundwater hydrogeochemical data revealed mainly<br />

HCO 3<br />

– Ca water types. As expected, the shallow aquifer had lower concentrations in<br />

dissolved ions compared with the deeper aquifer.<br />

These results, combined with further field campaigns including additional site characterization<br />

and water sampling as well as thermal and hydrogeochemical modelling, will<br />

provide better understanding of the flow dynamics in the catchment to evaluate influences<br />

of thawing permafrost on groundwater.<br />

174 - Hydrostratigraphic and Groundwater Flow Models of a<br />

Complex Unconsolidated Aquifer System, Nanaimo Lowlands,<br />

British Columbia, Canada<br />

N. Benoit, D. Paradis, J. Bednarski, & H. Russell<br />

Geological Survey of Canada, Québec City, Québec, Canada<br />

To support sustainable groundwater management, tridimensional (3D) hydrostratigraphic<br />

and groundwater flow models were developed for an unconsolidated aquifer system in<br />

the Nanaimo Lowlands, British Columbia (Canada). The study area is a coastal strip on<br />

eastern Vancouver Island (~580 km 2 ). A 3D hydrostratigraphic model was developed using<br />

existing well logs and published cross sections as well as new data from rotosonic coring,<br />

borehole geophysics, seismic reflection surveys and surficial geology mapping. The detailed<br />

surficial geology consists of 31 different units that are grouped into 8 major hydrostratigraphic<br />

units, of which 5 correspond to aquifers and 3 to aquitards. These are (from the<br />

surface down): Capilano-Salish (sand), Capilano glaciomarine (silty clay), Vashon-Capilano<br />

(sand and gravel), Vashon (till), Quadra (sand), Dashwood-Cowichan (compact silt),<br />

Mapleguard (sand), and siltstone to sandstone bedrock. This succession of Late Pleistocene<br />

to Holocene sediments is up to 140 m thick and is present over most of the study area,<br />

thinning to the southwest with rising topography and bedrock outcrops. Capilano-Salish<br />

and Vashon-Capilano units are shallow aquifers with relatively high vulnerability to surface<br />

contamination and low groundwater potential due to their limited thickness. The<br />

Quadra sand is the most exploited aquifer unit. It underlies the ubiquitous low permeability<br />

Vashon till and overlies Dashwood-Cowichan aquitard or the bedrock. The Quadra<br />

has a thickness of up to 50 m in place and it is predominantly above sea level, which<br />

minimizes issues of seawater intrusion. However, only about one-third of its thickness is<br />

saturated likely due to: (1) the covering by the Vashon aquitard that limits groundwater<br />

replenishment and (2) its deep incision by modern rivers that substantially drain its flanks.<br />

The relatively low permeability sedimentary rock aquifer is also extensively exploited, but<br />

only in areas where the Quadra aquifer is not present. Results of 3D groundwater flow<br />

modelling based on the hydrostratigraphic model show that baseflow to major rivers is<br />

provided mostly by groundwater seepage from heavily incised Quadra sand. Different regional<br />

groundwater flow patterns are also observed reflecting stratigraphic controls: flow<br />

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within the Quadra aquifer generally follows surface water drainage basin with discharge<br />

to rivers, whereas flow in underlying Mapleguard and bedrock aquifers is directed towards<br />

the Strait of Georgia without significant hydraulic connection with rivers. Hydrogeological<br />

insights gained through this study shows that the complexity of this aquifer system can<br />

make groundwater management challenging and that each system component should be<br />

carefully understood to ensure sustainable management.<br />

312 - Hydrogeochemical Assessment of a Regional Geochemical<br />

Anomaly, Niagara Peninsula<br />

Caitlin McEwan & Greg Slater<br />

School of Geography and Earth Sciences, McMaster University, Hamilton, Ontario, Canada<br />

Stewart Hamilton<br />

Ontario Geological Survey, Ministry of Northern Development and Mines, Sudbury,<br />

Ontario, Canada<br />

A geochemical anomaly in the Niagara Peninsula affecting water quality to the point of<br />

non-potability was first identified by the Ontario Geological Survey in 2010 by the Ambient<br />

Groundwater Geochemistry study. Interpretation of data collected during that field season<br />

shows two anomalous geochemical zones that are distinct with respect to the groundwater<br />

chemistry of the same geologic units elsewhere in Southern Ontario. Elsewhere, bedrock<br />

groundwater geochemistry in these Paleozoic strata is reasonably consistent within formations<br />

and reflects the lithological and mineralogical composition of the host rock. The first<br />

zone exists in the western Niagara Peninsula, and is characterized by Ca-Mg-SO 4<br />

2-<br />

-HCO 3<br />

rich waters and has high pCO 2<br />

and bacterial counts. This geochemical zone spans several<br />

geological formations including Devonian carbonates, Silurian evaporates and Silurian carbonates<br />

along a north-south trend, and in some cases cross-formational flow is indicated.<br />

The potentiometric surface was plotted to assess groundwater flow using the static water levels<br />

of wells, GPS elevations and locations, well stick-up and well depth following the protocol<br />

of the Ambient Groundwater Geochemistry Program. The assessment of hydraulic heads<br />

along a north-south transect crossing the Niagara Escarpment and the buried Onondaga Escarpment<br />

in both shows groundwater to flow northward and southward from each bedrock<br />

topographic high. Several new monitoring wells installed in the local Silurian carbonate/<br />

evaporite contact aquifer through collaborative efforts of the Ontario Geological Survey and<br />

the Niagara Peninsula Conservation Authority will provide hydrogeological ‘golden spikes’<br />

for the determination of regional flow direction. Ongoing work seeks to identify sources<br />

of these geochemical anomalies with additional sampling to increase the density of sample<br />

points. The collection of ∂ 34 S, ∂ 13 C, ∂ 18 O, and ∂D isotopic samples at each site during ongoing<br />

sampling will aid interpretation of the geochemical processes occurring in this anomalous<br />

geochemical zone. Previous work has suggested several possibilities for the source of<br />

the anomalous geochemical zones including the presence of corroded abandoned gas well<br />

casings as a mechanism for groundwater transport from depth and groundwater transport in<br />

karst aquifers. Identification of the sources of these water quality problems will be a first step<br />

in identifying safe and reliable groundwater supplies for local residents and providing data to<br />

make informed decisions by other stakeholders on long term water supplies in the region.<br />

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316 - Regional patterns and geochemical controls on shallow<br />

groundwater chemistry in Southeastern Ontario<br />

Laura M. Colgrove, Stewart M. Hamilton, & Fred J. Longstaffe<br />

Department of Earth Sciences – University of Western Ontario, London, Ontario, Canada<br />

This study reports regional chemistry for shallow groundwater from southeastern Ontario<br />

and identifies the dominant geochemical processes responsible for its variability. The database<br />

includes chemical analyses of groundwater from 264 wells located between the Frontenac<br />

Arch and the Quebec border, which were sampled as part of the Ambient Groundwater<br />

Geochemistry Program of the Ontario Geological Survey. Users of groundwater<br />

in eastern Ontario experience unusually elevated levels of many chemical constituents,<br />

including Na + , Cl - , I - , DOC, DIC and TDS. Whereas typical drinking water has TDS<br />

ranging from 500-700 ppm, 39 Eastern Ontario samples can be classified as “brackish”,<br />

ranging from 1000 – 10000 ppm, and 1 sample classified as saline at 10400 ppm. Spatial<br />

variations in groundwater chemistry show a strong correlation with the occurrence of<br />

Pleistocene (“Leda”) clays deposited by the Champlain Sea. Halogen ratios, water stable<br />

isotope compositions and major-ion proportions suggest that the regional groundwater<br />

flow system may be interacting with Champlain seawater still present in parts of the study<br />

area. Infiltrating meteoric water is confined by thickening Champlain Sea clays, and its<br />

chemistry evolves through ion exchange and mixing with Pleistocene water. Ion exchange<br />

with these clays softens the water, creating potential health-related implications for drinking<br />

water, including those associated with elevated concentrations of sodium and fluoride.<br />

Elevated DIC, DOC and I - , along with the presence of HS - and CH 4<br />

, are attributed to<br />

anaerobic decomposition of organic matter associated with the Champlain Sea clays and<br />

shale. The combined contributions of Champlain seawater and decomposition of associated<br />

organic matter has produced the highest I - concentrations so far measured in Ontario,<br />

which commonly exceed those of seawater by an order of magnitude.<br />

119 - Challenges and Issues Related to the Water Supply from the<br />

Brandon Channel Buried Valley Aquifer – Brandon, Manitoba<br />

Jeffrey J. Bell<br />

Friesen Drillers Ltd., Steinbach, Manitoba, Canada<br />

The hydrogeology and recharge characteristics of buried valley aquifers on the Canadian<br />

prairies are complex. The City of Brandon, in western Manitoba, relies on a water supply<br />

from the Assiniboine River. A large buried deposit of sand and gravel was present within a<br />

valley in the shale bedrock in Brandon. This deposit is called the Brandon Channel Aquifer.<br />

The Brandon area was once a key restriction in the northerly drainage of the vast majority<br />

of Central North America. This river system deposited a large amount of sediment. The<br />

area was subsequently glaciated several times, during the Pleistocene. These glacial events<br />

deposited related glacial deposits.<br />

Two industrial plants utilize 30,000 m 3 /day of groundwater for process and cooling applications.<br />

The aquifer is narrow in places and varies considerably in thickness and structure.<br />

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The aquifer is mostly confined; but is exposed at some places along the Assiniboine River<br />

Valley. Initially, the groundwater quality was poor with high chlorides and total dissolved<br />

solids. With the increased pumping, the quality improved. Heavier and evaporitic isotopes<br />

indicated that water from the Assiniboine River was recharging the aquifer.<br />

Two major pumping centers have developed deep drawdown zones in the potentiometric<br />

surface, where some areas indicate a strong recharge boundary from the Assiniboine River.<br />

This recharge boundary sustains the aquifer’s ability to supply large amounts of water.<br />

However, there are groundwater flows moving towards the pumping wells from other areas<br />

which still contain older glaciogenic water. Groundwater sampling shows that the groundwater<br />

in the dynamic zones is improving in quality, and indicates recharge. Over the last<br />

five years drawdown has developed in the western areas of the aquifer due to the pumping<br />

of the City of Brandon emergency supply wells. This new drawdown has dramatically<br />

altered the potentiometric surface and at some places the geochemistry.<br />

Numerous groundwater level observation wells show annual aquifer recharge with normal<br />

seasonal and climatic conditions. The network also records the effects of changing pumping<br />

rates. During the few years on several occasions, the Assiniboine River has reached<br />

flood stage, and the aquifer rises and falls very rapidly to the river water level changes.<br />

The Brandon Channel Aquifer is an important aquifer that provides substantial water<br />

supply for industrial use in the City of Brandon. The recent municipal use of the aquifer,<br />

shows that proper management is required of this complex buried valley aquifer. Therefore<br />

additional groundwater investigations should be undertaken.<br />

184 - Free convection or variable density flow within groundwater<br />

flow systems?<br />

K. Udo Weyer & James C. Ellis<br />

WDA Consultants Inc., Calgary, Alberta, Canada<br />

There exists a scientific conflict between the postulated but unproven existence of free<br />

convection under hydrodynamic on‐shore conditions and the well‐established existence of<br />

gravitational groundwater flow systems under the same conditions. The extensive literature<br />

on free convection indicates that downward directed fingers of higher density fluid may<br />

develop via free convection under hydrostatic laboratory conditions. Numerical codes have<br />

subsequently been developed which model these fingers in an hydrostatic environment.<br />

So far, there has not been any conclusive proof of the field occurrences of free convection<br />

under hydrodynamic on-shore conditions presented, despite strong claims to the contrary.<br />

The claims were mainly based on 2008 geo-electrical field measurements in the shore near<br />

sabkha (salt flat) areas in Abu Dhabi (van Dam et al., 2009).<br />

Repeat geophysical measurements in 2009 did not find the ‘fingers’ which were claimed<br />

to have existed in 2008. Subsequently a prominent proponent of free convection stated<br />

subsequently: “Hundreds of papers on theory, modelling & laboratory experiments on<br />

finger instabilities associated with free convection…. But a complete lack of conclusive<br />

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field based evidence and data” (Simmons, 2011). In January 2014 a publication by the<br />

same group of the 2009 authors claimed unexpectedly that the 2008 and 2009 geophysical<br />

measurement reflected the occurrence of free convection in the sabkha of Abu Dhabi (van<br />

Dam et al., 2014).<br />

Fortunately, the sabkha area of Abu Dhabi has been seen by sedimentologists of the petroleum<br />

industry as a natural present day laboratory to explain the huge amount of dolomitization<br />

which has occurred in the geological past. Wood et al. (2002) were the first<br />

authors conducting actual hydraulic field work in the Abu Dhabi sabkha area by drilling<br />

450 shallow (


The Ontario Geological Survey (OGS) began mapping both the overburden and shallow<br />

and deeper bedrock potable groundwater resources along the Niagara Escarpment in 2009.<br />

The main goal was to establish a 3D geologic model that could be used to delineate and<br />

predict locations of new groundwater resources for populations in key growth areas within<br />

the Escarpment region. The timing of the regional bedrock aquifer mapping initiative<br />

coincided with the Town of Shelburne retaining a consulting team to conduct a hydrogeological<br />

study to find additional groundwater supplies in bedrock to augment four existing<br />

wells, in order to meet future increased population and industry demands. The consultants<br />

were to review all existing hydrogeological data and select favourable areas within a 5km<br />

perimeter of the town boundary.<br />

The Shelburne groundwater exploration study also coincided with anticipated changes<br />

in the Ontario Drinking Water Standards for Arsenic levels – some of the existing bedrock<br />

wells, which ended in the interface aquifer contact zone, had produced As levels that<br />

would exceed the new standard. OGS bedrock geochemistry, petrology and SEM studies<br />

had revealed that As was naturally occurring and concentrated in microbially-precipitated<br />

framboidal pyrites in some of the rock formations of the Lockport Group – the main<br />

cliff-forming package of carbonates that hosts the potable groundwater flow zones along<br />

the Niagara Escarpment. OGS staff presented current knowledge of the regional 3D bedrock<br />

model and groundwater flow zones to the Town and consultants in December 2009.<br />

Extrapolation of the 3D geologic model into the Melancthon-Shelburne areas, along with<br />

renewed regional mapping that indicated major changes were needed to describe the bedrock<br />

stratigraphy of the area, resulted in the drilling of two cored holes to the regional<br />

bedrock aquitard – Cabot Head Formation (>95m depth).<br />

Subsequent core analysis, down-hole camera and geophysical tests, packer pumping tests<br />

and FLUTe profiling indicated potential deeper groundwater flow zones in the Goat<br />

Island and Gasport formations, with a total local thickness of 40m. A larger diameter<br />

water well was drilled and tested next to the more promising OGS-FLUTe-instrumented<br />

monitoring well, and confirmed a supply that is more than double the capacity the Town<br />

was expecting and with low As levels. Both a Municipal Class EA and Federal EA have<br />

since been completed and approved. The Town is expecting to bring the new water supply<br />

of more than 1600m 3 /day on-line in 2015.<br />

137 - Regional groundwater resources assessment in the<br />

Chaudière-Appalaches region, Québec, Canada<br />

Jean-Marc Ballard 1 , Marc-André Carrier 1 , Harold Vigneault 1 , Guillaume<br />

Légaré-Couture 1 , Michel Parent 2 , Laureline Berthot 1 Châtelaine Beaudry 1 , Marc<br />

Laurencelle 1 , Xavier Malet 1 , Annie Therrien 1 , & René Lefebvre 1<br />

1<br />

INRS, Centre Eau Terre Environnement, Québec City, Québec, Canada<br />

2<br />

Natural Resources Canada, Geological Survey of Canada, Québec City, Québec, Canada<br />

A groundwater resources assessment was carried out in the 15 600 km 2 Chaudière-Appalaches<br />

region extending south from the St. Lawrence River to the USA border. Data<br />

compilation extracted more than 20 000 well records from the governmental well database.<br />

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Well data were also extracted from over 350 documents collected from municipalities and<br />

government agencies. New fieldwork involved 11 cone penetration tests, 24 rotopercussion<br />

soundings and 9 conventional wells open in the rock aquifer. Complete chemical analyses<br />

were carried out on 131 groundwater samples, mostly collected from residential wells.<br />

Almost 200 other chemical analyses were obtained from previous or on-going projects in<br />

the study area.<br />

Over a 10 to 30 km-wide strip adjacent to the St. Lawrence River, the topography is that<br />

of a low plateau, which was covered by the Champlain Sea up to 180 m ASL, while the<br />

interior of the region is either hilly or mountainous. Farmland occupies the St. Lawrence<br />

valley and its main tributary valleys over about 22% of the region, while 60% of the region<br />

is forested, and the remainder is either urban, wetlands or water bodies. A small area is<br />

underlain by the geological province of the St. Lawrence Platform and the remainder is<br />

part of the Appalachians. Fine-grained marine sediments are present below about 100<br />

m ASL, while extensive sand blankets occur up to the Champlain Sea limit. The hilly<br />

interior is covered by relatively thin and permeable till, with glaciofluvial sediments locally<br />

present. The regional aquifer consists of fractured bedrock, whilst restricted local aquifers<br />

are in surficial sediments. In terms of water use, 70% of the 287 000 residents relies on<br />

groundwater through private wells or municipal water supply, as 64% of municipalities use<br />

groundwater from more than 300 supply wells. Groundwater provides 40% of total water<br />

use, 30% of this being used for industrial or commercial purposes, 38% residential and<br />

32% agricultural. Although groundwater is generally of good quality, naturally occurring<br />

components locally exceed provincial drinking water criteria (F, Ba and As). Seven water<br />

types were defined on the basis of the proportions of major ions. Some of these water types<br />

represent a natural geochemical evolution. However, other water types appear to indicate<br />

groundwater quality degradation that could be due to agricultural activities, deicing salts or<br />

waste water. While concentrations associated to these water types generally do not exceed<br />

standards, mitigation measures should be taken to prevent further degradation.<br />

251 - Regional hydrogeological mapping of saline and non-saline<br />

groundwater resources in the Belly River Group of the Alberta<br />

basin<br />

Nevenka Nakevska, Amandeep Singh, & Dan Palombi<br />

Alberta Geological Survey, AER, Edmonton, Alberta, Canada<br />

Characterization of saline groundwater resources is becoming increasingly important as<br />

the Government of Alberta implements its Water Conservation Policy seeking to minimize<br />

freshwater use in the energy sector. The groundwater program at the Alberta Geological<br />

Survey (part of the Alberta Energy Regulator) is re-initiating the mapping and<br />

characterization of saline aquifers using existing methodologies and improving upon them<br />

to account for variable-density groundwater.<br />

Our current study is focused on the regional mapping of hydraulic heads, total dissolved<br />

solids, and density-corrected flow directions in the Belly River Group. The Belly River<br />

Group is one of the youngest (upper Cretaceous-aged) economically important hydrocar-<br />

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on producing zone in Alberta. Toward the deformation front of the Rocky Mountains<br />

in the Alberta basin, the Belly River Group strata and lateral equivalents are known to<br />

contain saline groundwater. Updip the aquifer progressively thins and outcrops in central<br />

and east-central Alberta where non-saline groundwater exists. Hence as a regional aquifer,<br />

the Belly River Group is an important potential water source for unconventional oil and<br />

gas projects but also an important water source for domestic water users. Given the various<br />

groundwater uses of the Belly River Group and the potential for co-interference of saline<br />

and non-saline groundwater, it is important to map regional groundwater flow, salinity and<br />

where relevant, density-corrected hydraulic heads to assess current and future development<br />

scenarios for this aquifer.<br />

During the first part of the study we focused on analyzing and filtering data from two<br />

sources, water wells and petroleum exploration boreholes. Maps of hydraulic head, salinity,<br />

and temperature distribution within the Belly River Group were produced. The second<br />

part of the study focused on advancing the methodology for mapping variable-density flow<br />

using the water driving force methodology that allows for a qualitative analysis of potential<br />

effects of density-driven flow.<br />

POSTER SESSION: Surficial Geology of<br />

Southern Ontario<br />

Thursday October 29, 16:40<br />

Room: Regent<br />

276 - Emerging trends from the groundwater monitoring data<br />

collection at the Upper Thames River Conservation Authority<br />

(UTRCA)<br />

Linda P. Nicks & Karla Young<br />

Upper Thames River Conservation Authority, London, Ontario, Canada<br />

The Ontario Provincial groundwater monitoring network (PGMN) began in 2001 for<br />

the purpose of establishing a long-term, province-wide monitoring network and is a partnership<br />

between the Ministry of the Environment and Climate Change (MOECC) and<br />

Conservation Ontario. It is important to note that in contrast to meteorological and stream<br />

flow data, which may have records up to 100 years in length, continuous groundwater<br />

level records are significantly shorter. The network was designed to provide baseline data<br />

on ambient groundwater conditions in aquifers throughout Ontario and to monitor the<br />

partitioning of precipitation between runoff, groundwater recharge, and stream flow. The<br />

data can be used to obtain information on the natural groundwater level fluctuations across<br />

topographic, geologic, climatic and land-use environments, and to obtain information on<br />

the behavior of various types of aquifers under natural or anthropogenic stress. The wells<br />

were primarily instrumented between 2001 and 2003. The UTRCA maintains approximately<br />

28 wells throughout the watershed with a nearly continuous record of groundwater<br />

176 IAH-CNC 2015 WATERLOO CONFERENCE


levels over this period. In addition to the PGMN, another 13 observation wells were established<br />

to investigate the interaction of groundwater and natural heritage features and many<br />

of these monitors were established as early as 1992 and have a longer period of manual<br />

water level investigation. In addition to water levels, these wells have seasonal water quality<br />

information over a significant portion of this period.<br />

Typically groundwater systems respond slowly to human actions, land use change and climate<br />

variability and a longer term perspective is needed to manage this resource. Groundwater<br />

hydrographs graphically illustrate the dynamics and interaction of the components<br />

of the hydrologic cycle. Since 2001, the region has experienced periods of high groundwater<br />

and periods of drought and trends are starting to emerge in the monitoring data.<br />

While the hydrographs and water quality address a meaningful range of conditions, not all<br />

settings are represented and many impacts remain largely unknown.<br />

Through Source Water Protection, a comprehensive water budget and review of the water<br />

quality was completed for in the Thames-Sydenham and Region Drinking Water Source<br />

Protection that incorporates the UTRCA, the Lower Thames River and St. Clair Region<br />

Conservation Authorities. To characterize the location, quality and sustainable yield of the<br />

groundwater resource, hydrographs and water quality from the region will be utilized to<br />

compare and contrast various hydrogeologic settings of southwestern Ontario.<br />

157 - A Geological and Hydrogeological Investigation of the<br />

Dundas Buried Bedrock Valley, southern Ontario<br />

A.S. Marich, E.H. Priebe, & A.F. Bajc<br />

Ontario Geological Survey, Sudbury, Ontario, Canada<br />

A multi-year investigation of the Dundas buried bedrock valley was conducted by the<br />

Ontario Geological Survey in collaboration with the Grand River Conservation Authority.<br />

Increasing pressures on groundwater resources in southern Ontario have resulted in the<br />

need for a better understanding of deeply buried aquifers. The Dundas Valley is recognized<br />

as a prominent re-entrant of the Niagara Escarpment at the west end of Lake Ontario and<br />

extends northwestward beneath the Waterloo Moraine. Parts of the valley, especially near<br />

its eastern end at Lake Ontario, are in-filled with more than 200 m of sediment. These<br />

sediments vary significantly in age from west to east. In the western part of the valley system,<br />

the deep, coarse grained sediments are pre-Late Wisconsin in age (> 25 000 years old)<br />

and those to the east are mainly late-glacial (< 13 000 years old).<br />

This study was designed to gain a greater understanding of the valley’s geometry, the infilling<br />

sediments, the hydrogeological properties of those sediments, and the waters contained<br />

within them. Following data compilation and preliminary conceptualization, a gravity survey<br />

was conducted to define possible valley locations. Key thalwegs, believed to contain<br />

deeply buried aquifers based on water well information, were targeted for further study<br />

with continuous sediment coring and monitoring well installation. Hydraulic testing and<br />

groundwater sampling for hydrochemistry and isotope tracers provided valuable insight<br />

into groundwater resource potential of the deep valley sediments from both water quality<br />

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and quantity perspectives. This work has resulted in a clearer picture of the sediment records<br />

contained within the valley and its tributaries. No single continuous aquifer exists<br />

across the entire valley length, but rather, each thalweg appears to contain aquifer segments<br />

of varied connectivity. These deeply buried aquifers are typically confined by compact tills<br />

and very fine-textured glaciolacustrine deposits. The final product of this study is an updated<br />

conceptual three-dimensional geologic model for the Dundas buried bedrock valley<br />

system that highlights potential aquifer units to be targeted for future investigation.<br />

195 - Stratigraphic record and deglacial history of the interlobate<br />

zone between Ingersoll and Cambridge, southwestern Ontario,<br />

Canada<br />

Andy F. Bajc<br />

Ontario Geological Survey, Sudbury, Ontario, Canada<br />

Stratigraphic modelling of Quaternary sediments along the interlobate zone of southwestern<br />

Ontario (Ingersoll-Cambridge) was undertaken as part of the Ontario Geological<br />

Survey’s groundwater initiative. The objective of the initiative is to develop interactive 3-D<br />

models of Quaternary geology that provide geologic frameworks for groundwater studies.<br />

The framework was developed by reviewing and compiling archival surficial and subsurface<br />

geologic information and by continuously coring 44 boreholes to bedrock.<br />

A regionally consistent and reproducible stratigraphic succession was encountered comprising<br />

an older drift package on bedrock of Early Wisconsin or Illinoian age consisting<br />

of Erie-lobe diamicton (Canning Till) and associated stratified deposits. Discontinuous,<br />

non-glacial, organic-rich stratified deposits indicating cool, interstadial conditions unconformably<br />

overlie the older drift package and suggest a period of ice withdrawal spanning<br />

the interval 23.5 to >50 ka BP. Nissouri Phase Catfish Creek Till unconformably overlies<br />

these deposits and compositionally displays a shift in provenance from early, lobate ice flow<br />

to more regional, southerly flow followed by late, lobate ice flow in response to a thinning<br />

ice sheet. Catfish Creek Till is a distinctive marker horizon in southern Ontario that commonly<br />

acts as a regional aquitard. An interlobate zone following the Highway 401 corridor<br />

represents the suture line along which the Erie-Ontario and Huron ice lobes separated<br />

following the Nissouri Phase. Stratified deposits of the Waterloo moraine accumulated<br />

along the interlobate zone in either a subglacial or ice-walled lake. Correlative deposits<br />

accumulated to the southwest in the Woodstock, Dorchester and Lakeview moraines.<br />

Progressive retreat of the Erie-Ontario and Huron ice lobes resulted in the catastrophic<br />

drainage of these lakes along either ice-marginal or subglacially-carved tunnel channels<br />

occupying the modern courses of the Thames and Middle Thames rivers and Trout Creek.<br />

A period of ice recession resulted in the widespread deposition of fine-medium textured<br />

glaciolacustrine deposits on the Erie-Ontario side of the interlobate zone with limited<br />

accumulation on the Huron side. Slight readjustments in the overall retreat of the Huron<br />

and Erie-Ontario ice lobes resulted in the deposition of Tavistock Till and Port Stanley<br />

and Wentworth tills, respectively. A series of well-developed recessional and/or terminal<br />

moraines were constructed along the retreating Erie-Ontario ice lobe resulting in the local<br />

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accumulation of thick sequences of subaquatic fan sediments capped by variably textured<br />

diamictons. Downcutting and subsequent backfilling of low-lying areas between the moraines<br />

with deltaic deposits of the Norfolk sand plain resulted in the local removal of Port<br />

Stanley and Wentworth till.<br />

270 - Sedimentology and Hydrogeology of the Paris and Galt<br />

Moraines<br />

H.E.J. Russell & D.R. Sharpe<br />

Geological Survey of Canada, Ottawa, Ontario, Canada<br />

A.F. Bajc<br />

Ontario Geological Survey, Ministry of Northern Development and Mines, Sudbury,<br />

Ontario, Canada<br />

D.I. Cummings<br />

Department of Earth Sciences, Carleton University, Ottawa, Ontario, Canada<br />

The Paris and Galt moraines extend from near Lake Erie, 130 km north towards the<br />

Caledon area, are up to 11 km wide, and have a relief of 30 m. They evolve from two distinct<br />

ridges in the south to a broad, hummocky terrain with multiple ridges and secondary<br />

landscape elements (kettle depressions, eskers, subaerial fans, channels) in the north. These<br />

geomorphic changes are mirrored by changes in sediment type, thickness, and stratigraphy.<br />

Continuous cores reveal that the moraine consists of a succession of intercalated sand,<br />

gravel and diamicton units. Depending on the geographic location, a variety of different<br />

units can underlie the moraine, including older tills, lacustrine mud, or glacifluvial sand<br />

and gravel. Locally, the lower contact is cryptic where the moraine overlies sedimentologically<br />

similar deposits. Outcrop data suggest northern and southern parts of the moraine are<br />

different. Within the southern glacilacustrine basin, large foresets of >10 m height occur at<br />

the base of one pit exposure. By contrast, horizontally stratified outwash gravel is common<br />

in northern pits. A stoney, sandy silt diamicton, (Wentworth Till), covers large parts of the<br />

moraine, is massive to stratified, and is locally inter-bedded with sand and gravel. Where<br />

overlain by gravel, its upper contact can be loaded, suggesting it was water-saturated and<br />

thus prone to deformation during gravel deposition. Glacifluvial deposits are present in<br />

front of and locally underneath the moraine. The moraine strata are interpreted to have<br />

been deposited during a pause in the overall retreat of the Erie-Ontario ice margin with a<br />

highly variable meltwater flux both spatially and temporally. The narrow, southern moraine<br />

ridges may represent more rapid retreat within a glacial lake basin given the scale of foresets<br />

and confining lacustrine sediment. The northern, broader hummocky terrain is interpreted<br />

to have been deposited in a terrestrial environment based on the bedding character of the<br />

glacifluvial sand and gravel.<br />

Of the numerous moraines present within the Grand River watershed, the Paris-Galt moraines<br />

represent one of the three most hydrogeologicaly significant moraines, along with<br />

the Waterloo and Orangeville. The hummocky terrain of the moraine likely contributes<br />

to enhanced infiltration and recharge; a number of local aquifers occur within the moraine<br />

sediments (e.g. St George Aquifer); and the porous substrate of the moraine enhances<br />

groundwater contribution to baseflow of the Grand River.<br />

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233 - Using geophysical logs for stratigraphic assessment of<br />

glaciated terrains in southern Ontario<br />

Heather Crow, Susan Pullan, & Hazen Russell<br />

Geological Survey of Canada, Ottawa, Ontario, Canada<br />

Downhole geophysical logs provide a means of identifying stratigraphic changes and characterizing<br />

lithological units based on variations in physical properties of sediments. A suite<br />

of logs, including natural and active spectral gamma, induced conductivity and magnetic<br />

susceptibility, fluid temperature, and P and S-wave velocities, has been collected by the<br />

Geological Survey of Canada in 55 wells drilled in glaciated terrains of southern Ontario.<br />

This dataset provides the most comprehensive downhole geophysical characterization<br />

available of Late Wisconsin stratigraphy in the province Ontario.<br />

The wells are located within the Oak Ridges, Oro, and Waterloo moraines, and boreholes<br />

range in depth from 25 – 200 m. The Quaternary stratigraphy consists of a succession of<br />

sedimentary units separated by distinct erosional surfaces that can have considerable relief<br />

due to incision by paleo-valleys. The geophysical data thus provides characterization of a<br />

range of glacial and proglacial sedimentary settings that consist of laminated muds, sand<br />

and gravel, and mud and sandy diamictons.<br />

The geophysical signatures are varied, but common patterns emerge in the log suites<br />

which can be attributed to certain glacial facies. For example, saw tooth patterns in<br />

the gamma and induction logs indicate sediment dominated by high-energy environments<br />

and rapid deposition. Hour glass and reverse hour-glass signatures are seen in<br />

lower energy, rhythmically stratified mud and fine sand. Elevated P-wave velocities in<br />

a stratigraphically young diamicton overlying lower velocity diamictons are indicative<br />

of the Newmarket Till.<br />

POSTER SESSION: Sustainability of<br />

Groundwater Resources<br />

Thursday October 29, 16:40<br />

Room: Regent<br />

118 - Groundwater Supplies from the Pierson Channel Buried<br />

Valley Aquifer<br />

Jeffery J. Bell<br />

Friesen Drillers Ltd., Steinbach, Manitoba, Canada<br />

A buried valley aquifer lies in the far southwestern corner of the Province of Manitoba,<br />

which is known as the Pierson Channel Buried Valley Aquifer. The bedrock geology in<br />

the area is the Pierre Formation, which consists of green bentonitic shale. During bedrock<br />

surface mapping by the GSC in 1970, the buried valley feature was mapped, and<br />

the thelweg of the channel was approximately determined. The entire sequence of the<br />

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channel is buried by about 100 meters of Pleistocene deposits, consisting of mainly of<br />

glacial drift. The channel is thought to be about 1.6 km wide typically.<br />

The hydrogeology of the Pierson Buried Valley Aquifer is not well understood. The aquifer<br />

was first explored in the mid 1960’s by the GSC, and the MCWS. Recently, the GSC<br />

has undertaken additional geophysical work in the area to further define the location of<br />

the channel.<br />

Test drilling that was conducted for a water supply in the area encountered approximately<br />

15 meters of well-rounded fine gravel and coarse sand. A long term pumping test was<br />

conducted, with several weeks of recovery monitoring following the cessation of pumping.<br />

Although the sand and gravel aquifer was highly transmissive, negative boundary conditions<br />

consistent with narrow valley, strip type aquifers were present early during the testing.<br />

The groundwater quality was noted to be slightly brackish, with chlorides approaching 500<br />

mg/L. Samples collected for 18 O and deuterium showed isotopically depleted groundwater<br />

approaching δ 18 O of -20.00 per mille, plotting on the meteoric water line for the area.<br />

These results indicate that the aquifer was recharged during a period of time where climatic<br />

conditions were much colder than present.<br />

Long term monitoring results conducted on the aquifer show that the geochemical changes<br />

and the response to pumping is interesting and insightful to the future development of<br />

the aquifer.<br />

This project is particularly interesting from a geology and hydrogeology point of view, as<br />

it is the first known large scale test of the Pierson Buried Valley Aquifer at high pumping<br />

rates. It is also the first known analysis of the isotope hydrogeology of the aquifer. The<br />

long term monitoring of the aquifer will also aide future research into the Pierson Buried<br />

Valley Aquifer.<br />

161 - Determining the validity of satellite-based measurements of<br />

groundwater level changes in Southern Ontario<br />

Ellen Hachborn & Jana Levison<br />

School of Engineering - University of Guelph, Guelph, Ontario, Canada<br />

Aaron Berg<br />

Department of Geography - University of Guelph, Guelph, Ontario, Canada<br />

Groundwater is an important freshwater resource for the population of Southern Ontario<br />

with over 3 million users in the Great Lakes Basin. Low water conditions are a major concern<br />

for industry, agriculture, and domestic use as many depend on groundwater for their<br />

livelihoods. Historically, low water conditions were relatively rare in Ontario, but as the<br />

demand for water increases and climate patterns shift, low water levels may become more<br />

common. Currently, drought conditions are assessed by conservation authorities and the<br />

Ministry of Natural Resources through surface water measurements according to the Ontario<br />

Low Water Response Plan (OLWRP). No techniques using satellite data have been<br />

applied to measure groundwater level changes at a regional scale in Ontario. The Gravity<br />

Recovery and Climate Experiment (GRACE) satellite mission measures variations in<br />

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Earth’s gravitational field from terrestrial mass changes and has been shown in several<br />

studies to be sensitive to changes in groundwater. The objective of this study is to examine<br />

the applicability of GRACE measurements of groundwater changes from 2003 to 2013 for<br />

identification and monitoring of low water conditions. Two regions in Southern Ontario<br />

are examined over the study period; the Cataraqui and Quinte areas in the Southeast and<br />

the Grand River and Nottawasaga Valley areas in Southcentral Ontario. The Global Land<br />

Data Assimilation System (GLDAS) is a land surface model which contains monthly data<br />

for snowmelt and soil moisture. Monthly measurements of GRACE data when combined<br />

with the corresponding GLDAS data are used to determine the change in groundwater.<br />

The values obtained from data analyses will be compared with groundwater observations<br />

measurements (e.g. water well data from provincial monitoring networks) to determine<br />

the suitability of GRACE-derived measurements for the detection of low groundwater<br />

conditions. Preliminary results investigating Southeastern Ontario at a 26,000 km 2 scale<br />

from 2009 to 2013 showed that GRACE is sufficiently sensitive to obtain a meaningful<br />

signal during periods of low water conditions. In 2012, for example, the study area was<br />

observed to have a lower groundwater level in the late summer than any other time in the<br />

study correlating to the Province’s documentation of low water conditions during that time<br />

period. The findings of this study will be applicable to drought monitoring networks such<br />

as the OLWRP and will be useful for conservation authorities and local governments.<br />

This research will also aid studies looking at groundwater level changes in watersheds with<br />

limited well monitoring networks including remote regions and developing nations.<br />

165 - Characterising water storage change of Canada’s landmass<br />

using GRACE satellite observations<br />

Shusen Wang<br />

Canada Centre for Remote Sensing, Natural Resources Canada<br />

The GRACE satellite, a first-of-a-kind mission launched in March of 2002, has been<br />

mapping the Earth’s gravity field with an efficient and cost-effective way at an unprecedented<br />

accuracy. GRACE has enabled scientists for the first time to measure the total<br />

water storage change (TWS) of the Earth’s landmass from space. In this study, the TWS<br />

retrieved from GRACE observations for Canada’s landmass during the 11 years of 2003-<br />

2013 is used to characterize the TWS climatology. The seasonal variations and decadal<br />

trends of TWS during 2003-2013 over different regions in Canada are analyzed. A principle<br />

component analysis (PCA) is used to reveal the major variation anomalies and their<br />

drivers. Applications of the GRACE observations in water budget quantification, flood<br />

forecasting, drought monitoring, glacier and snow cover change detection, and climate<br />

change impacts assessment will be also discussed.<br />

143 - Comparison of predicted and actual impacts-dewatering of<br />

a local shallow sand aquifer-Fergus, Ontario<br />

Dwight Smikle, David Wilson, & David Hopkins<br />

R.J. Burnside and Associates Limited, Guelph, Ontario, Canada<br />

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Dewatering is required at many development sites where the installation of municipal services<br />

(i.e. water and sewage) require work be undertaken below the groundwater table. In<br />

order to assess impacts on local water resources due to pumping and obtain the necessary<br />

permits, a hydrogeological investigation for the subject lands is required. The hydrogeological<br />

assessment should include an evaluation of the predicted impacts of the dewatering<br />

activities as well as provide an outline of any contingency or mitigation processes that will<br />

be implemented for the period of dewatering.<br />

The recent installation of municipal services at a subdivision in Fergus, Ontario necessitated<br />

dewatering of the shallow unconfined sand aquifer. Because many existing residences<br />

in the area used shallow wells to obtain domestic water from the same unconfined aquifer,<br />

extensive investigation of the hydrogeologic system was undertaken to assess the impacts<br />

of dewatering on the local groundwater resources. The sensitivity of the aquifer to impacts<br />

also required implementation of a rigorous groundwater quantity and quality monitoring<br />

program that started well before dewatering and continued after the installation of services<br />

was complete. The prediction of dewatering impacts to local shallow dug wells was based<br />

on calculations using a considerable historical data set, as well as aquifer testing and a<br />

simplified hydrogeological model. The calculations indicated that limited and relatively<br />

localized impacts to groundwater resources would result from dewatering and that these<br />

impacts would be relatively short term. Comparison of the estimated impacts to actual<br />

impacts indicated that a simplified model that is based on a firm understanding of the geological<br />

and hydrogeological regimes can be used to make accurate predictions concerning<br />

the impacts of dewatering aquifers.<br />

POSTER SESSION: Vadose Zone Hydrogeolgy<br />

Thursday October 29, 16:40<br />

Room: Regent<br />

215 - An Examination of the Applicability of White’s 1932 Method<br />

to Estimate Actual Evapotranspiration Rates from Diurnal<br />

Watertable Fluctuations<br />

Jason H. Davison & Edward A. Sudicky<br />

Department of Earth and Environmental Sciences University of Waterloo, Waterloo, Ontario,<br />

Canada & Aquanty Inc., Waterloo, Ontario, Canada<br />

John C. Lin<br />

Department of Atmospheric Sciences – University of Utah, Salt Lake City, Utah, USA<br />

Water budget calculations within a watershed require a detailed understanding of the<br />

precipitation, evapotranspiration, surface water flows and groundwater fluxes. Traditional<br />

methods that estimate actual evapotranspiration rates rely on proxy information based on<br />

either remote sensing satellite data, pan evaporation tests, meteorological energy balances<br />

or eddy covariance techniques. Previously, White 1932 (USGS Open Report; see also,<br />

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Freeze and Cherry, 1979) hypothesized that diurnal watertable fluctuations commonly<br />

observed in shallow monitoring wells could be used to estimate actual evapotranspiration<br />

rates. In recent years, application of the White method has gained renewed interest in the<br />

literature, although the theoretical basis of the technique has not yet been explored to our<br />

knowledge. In order to test the applicability of White’s method, we applied HydroGeo-<br />

Sphere (HGS), a 3D fully-integrated surface and variably-saturated subsurface flow and<br />

transport model that can account for vegetation-dependent evapotranspiration processes,<br />

coupled to an Atmospheric Boundary Layer Model (ABL). ABL is a 0D time-dependent<br />

energy and water balance model. A number of test cases are examined involving different<br />

vegetation types and hydrologic conditions. Our simulations replicate the diurnal watertable<br />

oscillations commonly observed in field data, and, when the model output data are<br />

analyzed using White’s method, it is found that the results generally agree with the actual<br />

evapotranspiration computed internally within the coupled HGS-ABL model, but significant<br />

discrepancies can occur.<br />

218 – Impact of Snow Cover and Frozen Soil on Water and Gas<br />

Fluxes through Unsaturated Sands<br />

Sophie Guillon, Florent Barbecot, Marie Larocque, & Daniele L. Pinti<br />

GEOTOP, UQAM, Montréal, Québec, Canada<br />

Eric Pili<br />

CEA, DAM, DIF, Arpajon, France<br />

Seasonal freezing of part of the vadose zone and presence of seasonal snow cover is of<br />

concern for all regions in Canada. The occurrence and thickness of frozen soil and snow<br />

cover are directly responsible for water, energy and gas fluxes from the surface to aquifers<br />

and vice-versa. In these cold environments, groundwater recharge mainly occurs during<br />

the spring snowmelt and as a result of fall rain. Smaller recharge events also occur during<br />

the winter due to melting at the snow-soil interface and infiltration into frozen or partly-thawed<br />

soil. But soil water dynamics and water infiltration before the onset of spring<br />

snowmelt are neither well studied nor constrained, and they are not considered by the<br />

models currently used to calculate groundwater recharge. The intensity and duration of<br />

these winter recharge events appear to be controlled by the thickness and permeability of<br />

frozen soil and its frozen water content. Fluxes of CO 2<br />

and other trace gases such as CH 4<br />

and N 2<br />

O have been shown to occur during winter and to contribute to the annual gas<br />

budget, but they are often not measured or considered. Microbial processes, temperature<br />

and soil permeability are involved in controlling these gas fluxes, which need to be better<br />

understood and quantified. The objective of this work is to better understand the influence<br />

of soil freeze/thaw events on water infiltration and gas fluxes during winter. This presentation<br />

will describe a case study based on the monitoring of water and gas fluxes in the<br />

frozen vadose zone and in the snowpack during the winter season at an instrumented site<br />

located on a sand deposit (esker), west of Montreal (Canada). Water content, temperature,<br />

air pressure, CO 2<br />

and radon concentrations are measured in the first meters of soil and in<br />

the snowpack during winter season. Water stable isotopes depth profiles are used to identify<br />

spatial and temporal variability of water infiltration. These data are used to develop,<br />

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validate and calibrate a new numerical scheme to quantify water and heat budgets, as well<br />

as recharge during winter.<br />

252 - Spatial and temporal controls on snowmelt infiltration<br />

through the partially frozen vadose zone in an undulating prairie<br />

landscape<br />

Aaron Mohammed, Edwin Cey, & Masaki Hayashi<br />

Department of Geoscience – University of Calgary, Calgary, Alberta, Canada<br />

Groundwater recharge in the Canadian prairies is heavily dependent on depression-focused<br />

infiltration of snowmelt water into partially frozen glacial sediments. As such, soil<br />

freeze-thaw and preferential flow processes play important roles in constraining groundwater<br />

recharge. This study aims to examine the hydraulic and thermal regimes throughout<br />

the vadose zone to better understand the processes controlling infiltration, redistribution<br />

and recharge in these cold, dynamic environments.<br />

Three field sites comprising differing landscape and geologic characteristics in southern<br />

Alberta have been instrumented with soil moisture and temperature sensors, capillary wick<br />

flux-meters, and piezometers. These instrumented profiles capture the characteristic upland,<br />

mid-slope and depression features of the undulating prairie landscape. High frequency<br />

soil moisture and temperature monitoring are used to examine initiation controls, depth<br />

and rates of infiltration and subsurface flows. Soil moisture and temperature data also<br />

reveal the spatial and temporal frost depth dynamics across different topographic locations<br />

and relate timing of thaw to initiation of infiltration and soil moisture redistribution along<br />

the depression-upland transition. Combining these observations with drainage fluxes and<br />

piezometric responses constrains the effects of soil moisture distribution in the vadose zone<br />

and how it affects deeper drainage and potential recharge. The detailed field monitoring<br />

provides valuable insight into the hydraulic and thermal processes governing infiltration<br />

and recharge to shallow groundwater. Preliminary data analysis suggests that antecedent<br />

moisture and thermal profiles control the initiation and timing of infiltration during both<br />

mid-winter thaw events and spring snowmelt. Macroporosity is expected to be a critical<br />

parameter in governing water movement through frozen soils, as both thermal and hydraulic<br />

responses are frequently observed at depth prior to complete ground thaw. Understanding<br />

these processes and how they interact to constrain groundwater recharge will enable a<br />

holistic conceptual model of infiltration and recharge in the Canadian Prairies.<br />

280 - Three-phase flow characterization of hydrocarbon<br />

contaminated peat<br />

Behrad Gharedaghloo & Jonathan S. Price<br />

Department of Geography and Environmental Management – University of Waterloo,<br />

Waterloo, Ontario, Canada<br />

The potential for hydrocarbons to contaminate peatlands is increasing in Canada, particularly<br />

because of the expanding oil and gas industry and its use of pipelines and rail for<br />

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transport. The transport of hydrocarbons within both the vadose zone and saturated zone<br />

can lead to contaminated surface and ground water resources, and can adversely affect<br />

the health of plants and fauna. Peatlands, which are very common in the boreal zone,<br />

are particularly susceptible to spills since their poor mechanical strength results in weak<br />

foundations for rail beds and pipelines. There is no general agreement on the methodology<br />

to deal with hydrocarbon contamination, mostly because the methodology is dependent<br />

on the physical properties of the contaminated area, which will govern the transport of<br />

immiscible fluids. However, to deal with hydrocarbon contamination and understand its<br />

behaviour underground and particularly in the vadose zone, three-phase flow (air, water<br />

and hydrocarbon) characteristics of the surrounding media must be determined. Several<br />

studies have investigated the three-phase flow of water, air and hydrocarbon contaminants<br />

in mineral soils and rock. However, little or no such study has been done in peat. Considering<br />

that peat is composed of organic material, and its physical and chemical properties in<br />

the presence of hydrocarbons might be different from properties of soil or rock, investigation<br />

of three-phase flow characteristics of peat media is necessary. To study the multiphase<br />

characteristic of peat, water retention curves for two-phase of water and air, and capillary<br />

pressure-saturation curves for oil-air and water-oil systems were measured for peat core<br />

samples. The results from this study characterize the vertical distribution of contaminant<br />

phase, water and air in the vadose zone of peat, in the case of a hydrocarbon spill.<br />

290 - Assessing transport of in situ and applied tracers in<br />

partially saturated, macroporous soil under varying irrigation<br />

rates<br />

Edwin Cey, Danijela Mikulic, Matthew Howroyd, & Michael Callaghan<br />

Department of Geoscience, University of Calgary, Calgary, Alberta, Canada<br />

Salt contamination of soil and shallow groundwater is a major concern in western Canada,<br />

due to the large number of oil and gas production sites that have been affected by releases<br />

of produced water. Saline soil impairs plant growth and reduces agricultural productivity,<br />

requiring remediation methods that often utilize irrigation to enhance downward flushing<br />

of salt from the soil profile. Fine-grained glacial soils hamper remediation efforts because<br />

the soils have low permeability and contain macropores that cause water to bypass the<br />

soil matrix where the vast majority of the salt is stored. The purpose of this study was<br />

to examine small-scale transport processes associated with the flushing of salt from low<br />

permeability, macroporous soils under varying irrigation rates. Four large, intact soil cores<br />

were collected from an industrial remediation site and instrumented with a network of<br />

tensiometers, solution samplers, and outflow collectors. Two paired-core experiments were<br />

conducted using the same volumes of applied water, but with the water applied at different<br />

irrigation rates. Low irrigation rates were designed to prevent ponding on the soil surface<br />

and minimize the initiation of preferential flow along macropores, whereas high irrigation<br />

rates were more representative of current site remediation practices. During the irrigation<br />

period, the migration of in situ (chloride) and applied tracers (bromide, iodide, and Brilliant<br />

Blue dye) was monitored, and the final distribution of the tracers was characterized<br />

by carefully cutting and sampling the cores at the conclusion of irrigation. Image analysis<br />

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of soil dye patterns was also used to quantify dye distributions in each core and compare<br />

to the anionic tracer results. The spatial and temporal distribution of solute tracers varied<br />

as a function of the irrigation rate, with slower irrigation rates resulting in more uniform<br />

(Darcian) flow, vertically stratified tracer distributions, and greater chloride mass removal.<br />

At higher irrigation rates, the initiation of preferential flow resulted in lower chloride removal<br />

efficiency due to limitations in lateral mass exchange between macropores and the<br />

soil matrix. The results have important implications for remedial design, suggesting that<br />

properly controlled irrigation can improve salt flushing efficiency without increasing water<br />

usage or the timeframe required for soil remediation.<br />

291 - Pore-scale modelling of multiphase flow in a mixedwettability<br />

peat substrate<br />

Owen Sutton, Behrad Gharedaghloo, & Jonathan Price<br />

Geography and Environmental Management – University of Waterloo, Waterloo, Ontario,<br />

Canada<br />

Although a significant body of literature exists on multiphase fluid movement in typical<br />

porous media, there is a relative dearth of studies performed with highly organic soils,<br />

like peat. Given the unique wettability characteristics of peat, the properties governing<br />

multiphase flow are considered to be highly heterogeneous. The lack of knowledge<br />

about multiphase flow in peat made it difficult to make statements about processes that<br />

could be occurring over a large scale, such as the spread of LNAPL following a train<br />

derailment. Therefore, it was deemed necessary to investigate pore-scale mechanics<br />

through computational fluid dynamics simulations. The modelling was performed using<br />

a commercially available multiphysics software package. The processes of imbibition and<br />

drainage of oil-water, air-water, and oil-air are modelled for the peat substrate using various<br />

fluid contact angles determined through laboratory goniometer experiments. The<br />

peat media is represented in the model as a two-dimensional slice of a computed tomography<br />

(CT) scan. Data was collected and analyzed to understand residual saturation and<br />

capillary pressure under varying wettability regimes. This work will have the potential to<br />

aid hydrogeologists and wetland hydrologists in assessing contaminant transport in the<br />

unsaturated zone of highly organic media.<br />

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POSTER SESSION: Workshop on<br />

Groundwater Policy<br />

Thursday October 29, 16:40<br />

Room: Regent<br />

269 - A Screening Tool for Guiding Groundwater Curtailment<br />

during Water Scarcity<br />

Klaus Rathfelder, Andarge Baye, & Mike Wei<br />

British Columbia Ministry of Environment, Victoria, British Columbia, Canada<br />

Pat Lapcevic & Sylvia Barroso<br />

British Columbia Ministry of Forests, Lands and Natural Resource Operation, Nanaimo,<br />

British Columbia, Canada<br />

British Columbia is embarking on the regulation of groundwater use and groundwater<br />

licensing under authority of the recently passed Water Sustainability Act (WSA). The<br />

WSA provides a precedence of water rights based on a first-in-time, first-in-right (FIT-<br />

FIR) scheme with exceptions for essential household needs and protection of critical ecological<br />

flows. During periods of water scarcity, the provincial government has authority to<br />

order short-term curtailment of surface and groundwater use to protect ecological flows in<br />

groundwater dependent ecosystems; for example during low flows coinciding with sensitive<br />

fish runs. However, the recovery of streamflow following a reduction in groundwater<br />

pumping occurs over a period of time that can span hours to months or longer, depending<br />

on the degree of connectivity, the aquifer hydraulic properties, and the well location relative<br />

to the stream. Therefore, policies to administer groundwater curtailment during water<br />

scarcity seek to take potential action on users in accordance with FITFIR, but to apply<br />

FITFIR only where it is a likely to benefit streamflow recovery within a timeframe of<br />

interest. This paper describes a screening tool to assist water managers for guiding curtailment<br />

activities to those wells that are most likely to affect short-term streamflow recovery.<br />

The screening tool is a spreadsheet based application that uses analytical solutions of the<br />

Glover model to relate streamflow recovery to four parameters: groundwater pumping rate,<br />

well distance from the stream, aquifer transmissivity, and aquifer storativity. The output<br />

of the screening tool is a curtailment envelop that identifies pumping wells that are most<br />

likely to influence streamflow recovery in a specified curtailment period. This information<br />

provides water managers with a focus area for groundwater curtailment activities including<br />

confirmation of well locations and groundwater usage, and if necessary to take action on<br />

users based on FITFIR. The curtailment envelop has a variable distance from the stream as<br />

a function of pumping rate. It is determined as a percentage of recovery scenarios derived<br />

from input distributions of transmissivity and storativity. A benefit of the screening tool is<br />

that it can be used pre-emptively to guide collection of information on water well locations<br />

and groundwater use prior to low flow periods. Application of the tool is demonstrated for<br />

the Lower Cowichan watershed on the east coast of Vancouver Island, where surface water<br />

and groundwater use for industrial and municipal water supply has reduced streamflow<br />

during the summer dry season and has the potential to impact salmonid species.<br />

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Moments of Insight in Hydrogeology<br />

Friday October 30, 9:05 - 11:45<br />

Chair: Cathy Ryan<br />

Room: Viennese Ballroom<br />

274 - Hydrogeologists without Borders and the “GW2.0 Initiative”<br />

M. Cathryn Ryan<br />

Geoscience, University of Calgary, Calgary, Alberta, Canada<br />

Hydrogeologists without Borders (HWB) is a Canadian charity focused on linking hydrogeology<br />

to the water, sanitation and hygiene (WASH) sector. Although much of<br />

the regions of critical need worldwide are increasingly groundwater dependent, and a<br />

significant part of the international aid sector drills water wells, projects are often lacking<br />

in their hydrogeological component especially sustainable well construction. Major<br />

efforts to provide improved water supply in developing countries are thwarted because<br />

of the inability to find and develop groundwater resources - often due to the lack of hydrogeological<br />

expertise. HWB seeks to provide an updated version of the 1979 Freeze<br />

and Cherry text Groundwater as a training tool that will be available worldwide and in<br />

multiple languages. This new, online, version will be developed under an Editorial Board<br />

that includes the original co-authors, Al Freeze and John Cherry. This session will celebrate<br />

the GW2.0 initiative.<br />

126 - Groundwater redox processes: incorporating chemical<br />

thermodynamics into hydrogeology in the 1970s<br />

Richard E. Jackson<br />

Geofirma Engineering Ltd, Heidelberg, Ontario, Canada<br />

During the 1960s the groundwater geochemistry of iron became a topic of interest<br />

within the US Geological Survey through work by John Hem. William Back and Ivan<br />

Barnes of the USGS showed the evolution of Eh and Fe in the groundwater flow system<br />

of the Atlantic Coastal Plain in Maryland. In the 1970s, Mike Edmunds of the British<br />

Geological Survey in the UK measured a full suite of hydrochemical parameters in<br />

English aquifers such as the Lincolnshire Limestone. These studies showed that ferrous<br />

iron concentrations were constrained in recharge areas by dissolved oxygen (DO) and by<br />

aqueous sulphide further down the flow system. In between, an area of high dissolved<br />

ferrous iron and manganese existed due to the high solubility of FeCO 3<br />

and MnCO 3<br />

under conditions of Fe(III) and Mn(IV) oxide dissolution. Analogies with anoxic muds<br />

studied by Robert Berner of Yale University were apparent.<br />

Simultaneously Werner Stumm of Harvard University identified the thermodynamic<br />

sequences of redox reactions that occurred in the presence of an excess of either DO or<br />

dissolved organic carbon, such as petroleum hydrocarbons, although Stumm was interested<br />

in wastewater treatment systems. These sequences were adopted by Donald Thorstenson<br />

of the USGS and a group at Chalk River Nuclear Labs in Ontario (Douglas<br />

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Champ and Janis Gulens of AECL and Richard Jackson of Environment Canada) to<br />

explain the sequential occurrence of DO, nitrate, Fe, Mn and sulphide species. Stumm<br />

also provided guidance on the interpretation of Eh measurements by platinum electrodes<br />

that were problematic in most aqueous environments. Champ noted that the microbial<br />

requirements for functioning in groundwater systems were easily met by available nutrients<br />

dissolved in groundwater, while Gulens explained the effects of various sorbed<br />

species (e.g., DO, sulphide, cyanide from Zobell’s solution) on the measured Pt electrode<br />

potential. Jackson wrote the paper that appeared in 1979 in the Canadian Journal of<br />

Earth Sciences based on field data from a short (1 km) flow system he was studying at<br />

Chalk River including data from Back and Barnes and Edmunds.<br />

Thus chemical thermodynamics and electrochemical theory were incorporated into hydrogeology<br />

through the necessity understanding complex groundwater quality patterns<br />

and Eh measurements. This work in the 1970s set the stage for the adoption of monitored<br />

natural attenuation for the biodegradation of chlorinated and fuel hydrocarbons<br />

in the 1990s.<br />

115 - Temporal Scales in Groundwater Science:<br />

The Challenge to Hydrogeologists<br />

William M. Alley<br />

National Ground Water Association, San Diego, California, USA<br />

One of the great challenges facing groundwater hydrologists is to communicate the highly<br />

variable temporal characteristics of groundwater systems and their responses to human and<br />

natural stresses. Just as hydraulic conductivity spans many orders of magnitude, temporal<br />

scales range from real-time to many millennia. This presentation examines the different<br />

time scales of interest to hydrogeologists with an emphasis on how these time scales relate<br />

back to groundwater management and governance.<br />

248 - Laboratory demonstration of confined and unconfined<br />

aquifer storage characteristics<br />

Robert W. Gillham<br />

Department of Earth and Environmental Sciences, University of Waterloo, Waterloo,<br />

Ontario, Canada<br />

Undergraduate students of hydrogeology commonly have difficulty appreciating the differences<br />

in processes of water storage and release in confined and unconfined aquifers.<br />

After several attempts to teach the concepts, but with only moderate success, a laboratory<br />

model was developed that provided a physical and visual demonstration of specific<br />

yield, specific storage and several related phenomena. As reflected in answers to exam<br />

questions, there was a dramatic improvement in the level of student understanding. A detailed<br />

description of the model and a worked example is included in: Gillham, R. W. and<br />

O’Hannesin, S. F. 1984. Apparatus for demonstrating confined and unconfined aquifer<br />

characteristics. Journal of Geological Education, 32: 261-264.<br />

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159 - Training the Next Generation of Hydrogeologists<br />

James Barker<br />

Department of Earth & Environmental Sciences, University of Waterloo, Waterloo, Ontario, Canada<br />

Training hydrogeologists involves a complex collaboration between the trainee, the<br />

training institute, employers, accreditation organizations, professional societies, and government<br />

regulators. All have important roles to play, but also all have multiple accountabilities<br />

and responsibilities and so their focus is diffuse. Should students have a broad<br />

(but therefore shallow) environmental water training or should they specialize? Should<br />

institutions provide a better underpinning in science and engineering or more practice<br />

in hydrogeology? At least the requisite course curricula for hydrogeologists is captured<br />

in professional accreditation, which can be modified as required. The next generation of<br />

hydrogeologists has no shortage of access to high quality information about the technical<br />

practice of hydrogeology, but typically has limited experience in its application. This is<br />

the shortcoming we must overcome.<br />

The participation of all parties to develop and provide experiences in hydrogeology to<br />

trainees is therefore critical. University co-op programs, (paid) apprenticeships, and ongoing<br />

experience-loaded upgrade courses for continued accreditation are all part of the<br />

solution. These need to be developed as a seamless transition from school to work place<br />

and so involvement of professional hydrogeologists throughout the training is required.<br />

Mentoring of trainees is a critical part of their early employment. Given the diversity of<br />

hydrogeologists and their firms and the market forces in play, mentoring of new hires<br />

appears to be variable and often weak.<br />

In Canada, the professional societies (IAH) should play a greater role in providing experience<br />

in the application of information in hydrogeology. This role must include leadership<br />

and, as necessary, coercion across our diverse hydrogeology community.<br />

237 - Groundwater Flownets: “This is where I first understood<br />

groundwater flow systems”<br />

Emil Frind 1 & John Molson 2<br />

1<br />

University of Waterloo, Waterloo, Ontario, Canada<br />

2<br />

Université Laval, Québec City, Québec, Canada<br />

The above comment by a former student vividly demonstrates the importance of<br />

flownet analysis in the study and teaching of groundwater flow systems. A flownet,<br />

consisting of equipotentials and streamlines, shows where the water comes from,<br />

where it goes, and what path it takes in the subsurface – in short, it gives a basic visual<br />

and quantitative understanding of a flow system. Traditionally, flownet analysis is<br />

taught in hydrogeology courses by means of graphical methods, using pencil and paper.<br />

This intuitive method works well as long as the system is isotropic, homogeneous,<br />

and there is no scale distortion – but it becomes challenging as complexities come<br />

into play. Groundwater texts often use flownets to illustrate flow systems, but rarely<br />

provide practical approaches for generating these flownets for complex situations such<br />

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as mountainous terraines, and under different scales. This may be a reason why flownet<br />

analysis is not used much in practice.<br />

Flownets can be generated very easily by means of the dual theory of analysis. This<br />

method, which comes from fluid dynamics, was first introduced in Canada in the<br />

early 1980s by the first author, and it has since been enhanced by the second author.<br />

The dual method consists of two governing equations: the standard equation for potentials,<br />

and a complementary equation, based on the Cauchy-Riemann relationship,<br />

for streamfunctions. The boundary conditions are also complementary. Because both<br />

equations have the same form, they can be solved together using the same numerical<br />

techniques. The plots of these two independent solutions give an accurate flownet<br />

for any type of flow system, even under highly complex conditions or extreme scale<br />

distortions. With some enhancements, it can also inform about groundwater age. The<br />

only limitations are that flow is within the cross-sectional plane, of uniform density,<br />

and at steady state, and the system has no internal sources or sinks. Incorporated into<br />

the model FLONET, the dual solution can be used to verify 3D solutions for more<br />

complex situations. A key feature is that the method can easily be used to test the<br />

effect of many different configurations and boundary conditions for a given system –<br />

giving answers to the ubiquitous “what if ” question – without running an expensive<br />

3D model. Above all, it is a valuable teaching tool in both the classroom and the computer<br />

lab, and as the above-mentioned former student aptly recognized, it gives a clear<br />

understanding of how a groundwater system works.<br />

311 - Unstated assumptions – a challenge for students and<br />

hidden traps for the unwary<br />

Garth van der Kamp<br />

Water Science and Technology, Environment Canada, Saskatoon, Saskatchewan, Canada<br />

In hydrogeology, as in all of human thought, there are always unstated assumptions.<br />

Often it is precisely these invisible statements that turn out to cause the failure of the<br />

bridge, or the unintended consequences of a government policy, or to be the critical<br />

flaw in a paper in Water Resources Research. But it is also these assumptions that are<br />

hardest to detect – they are smoothed over beautifully because usually the authors<br />

are not even aware of them. Hydrogeology science and its publications contain many<br />

examples of invalid unstated assumptions, as hidden traps for the unwary. Unstated<br />

assumptions which are shared by a whole community of researchers are hardest to<br />

detect – such paradigms are very interesting when they are identified, because that can<br />

lead to major advances in the science!<br />

We published a minor paper in Water Resources Research in 1969 (Carr and van der<br />

Kamp, Vol. 5, 1023-1031) which contains a fatal flaw. The source of the error was an<br />

unstated and invalid assumption in a 1950 publication by C.E. Jacob, a recognized<br />

“authority” in hydrogeology, so we could be excused. It was three years later before<br />

the error was identified by a graduate student (myself ) in an “aha!” moment while<br />

puzzling over some strange observations that could not be explained by the theory in<br />

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the 1969 paper. The unstated assumption is well hidden. When a typical fourth-year<br />

hydrogeology class is challenged to find the error in the 1969 paper the students are<br />

rarely successful.<br />

Some lessons: the word of experts and “authorities” may be wrong; the unstated assumptions<br />

are usually hidden in the opening paragraphs of a paper or in the introduction<br />

to the theory section; just because a paper has been published in a “refereed”<br />

journal is no guarantee that it is correct; pay special attention to the “outliers” in the<br />

data that are explained away, ignored or not presented at all.<br />

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NOTES:<br />

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NOTES:<br />

IAH-CNC 2015 WATERLOO CONFERENCE<br />

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NOTES:<br />

196 IAH-CNC 2015 WATERLOO CONFERENCE


International Association<br />

of Hydrogeologists -<br />

Canadian National Chapter<br />

IAH-CNC 2015 WATERLOO<br />

October 27 - 30, 2015<br />

Waterloo Inn<br />

475 King Street North<br />

Waterloo, Ontario, CANADA

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