Green Mining Conference Water Management and the Environment

Slides:



Advertisements
Similar presentations
Framework for the Ecological Assessment of Impacted Sediments at Mining Sites in Region 7 By Jason Gunter (R7 Life Scientist) and.
Advertisements

What's New for Whole Effluent Toxicity (WET) Bill Dimond MDEQ Aquatic Toxicology Laboratory.
Whole Effluent Toxicity NPDES Program
Approach for Including Nutrient Limitations within NDPDES Permits Dallas Grossman Division of Water Quality
By: Audella Eid Advisor: Dr. R. Zurayk Constructed Wetlands for Wastewater treatment.
The Effects of Caffeine and Triclocarban on Gammarus pseudolimnaeus Jim Fietzer Department of Biological Sciences, University of Wisconsin – Whitewater.
The Deloro Mine Site Demonstration Project K.Volchek, D.Velicogna, W.P.Wong, C.E.Brown SAIC Canada, Environment Canada NATO CCMS Pilot Study Meeting “Prevention.
Rule Change Update MPCA 1/13/ Mid-Sized ISTS (MSTS)
Methods for Incorporating Aquatic Plant Effects into Community Level Benchmarks EPA Development Team Regional Stakeholder Meetings January 11-22, 2010.
Obtaining the goals.  Identify realistic future use of all water bodies – drinking water, irrigation water, livestock watering, bathing, fishing, recipient.
INTRODUCTION Eutrophication is a natural phenomenon in which the water becomes green and degraded. It is a natural process which became a problem because.
Toxicity of Daphnia to Manganese Compared to Manganese Concentrations in Local Waters Kristel Fijolek Senior Capstone, Spring 2005.
Kiggavik Project Final Hearing Presentation
Friendly Klodnica. MAIN GOAL TO ACHIEVE CLEAN Klodnica MAIN GOAL TO ACHIEVE CLEAN Klodnica Target – former II surface water quality class, in that: BOD.
Freshwater Aquatic Organisms and Habitat ( ) Rick Palmer Senior Fisheries Biologist Sharleen Hamm Aquatic Ecologist.
Case Studies from Egypt
Ministry of the Environment Certificates of Approval for an Anaerobic Digestion Facility Post Construction DIGGING INTO BIOGAS DETAILS WORKSHOP April 5,
Formation and Treatment
Preview of the Draft River Basin Management Plan SERBD Advisory Council September 2008.
Seasonal Changes in Biogeochemistry of a Natural Wetland Receiving Drainage from an Abandoned Mine Diane McKnight and Eric August – University of Colorado.
Jericho Aquatic Discharge Assessment Presented by: Bruce Ott, Senior Environmental Scientist, AMEC Earth & Environmental.
CoastalZone.com The Use of Ecological Risk Assessments in a Watershed Level Context Thorne E. Abbott CoastalZone.com.
Charge Question 4-1: Please comment on the ecotoxicity studies selected to represent the most sensitive species in each of the risk scenarios (acute aquatic,
Environment Canada’s Intervention on the Mary River Project Water Licence Application Nunavut Water Board Final Hearing Pond Inlet, NU Mark Dahl / Anne.
1 Water Quality Regulation In South Africa MMC 25 Feb 2010.
DEREL TEMPUS DEVELOPMENT OF ENVIRONMENTAL AND RESOURCES ENGINEERING LEARNING DEVELOPMENT OF ENVIRONMENTAL AND RESOURCES ENGINEERING LEARNING.
Water Quality Criteria: Implications for Testing Russell Erickson U.S. Environmental Protection Agency Mid-Continent Ecology Division, Duluth, MN, USA.
Rapid Bioassessment Protocols for low gradient streams) for species richness, composition and pollution tolerance, as well as a composite benthic macroinvertebrate.
Initiatives in Drinking Water First Nations Water Symposium 2010 Peter Ross Environmental Health Officer First Nation and Inuit Health.
Sediment Delivery to the Watonwan River
1 Impact of Fluoride on Microorganisms in Wastewater Treatment Chandra Khatri, Valeria Ochoa and Reyes Sierra-Alvarez Department of Chemical and Environmental.
Point Source Loads and Decision Criteria for Toxics Modeling Baltimore Harbor TMDL Stakeholder Advisory Group September 10, 2002.
A quantification of groundwater seepage during drought and its importance for water quality modeling in the St. Vrain watershed Hannah Chapin Thomas Gerber.
LOCAL AUTHORITY REGULATORY ASPECTS Paul Carroll Executive Scientific Officer Waterford County Council Integrated Constructed Wetlands Awareness Seminar.
About water pollution Water supply is a complex issue in California – San Joaquin Valley, Los Angeles – Water increased by 170% from 2006 to 2010 – Water.
Managing TDS in the Upper Monongahela River Basin Project WRI 119 Paul Ziemkiewicz, PhD Director West Virginia Water Research Institute 1 West Virginia.
The Clean Water Act (1977, 1981, 1987) By: Jonas Szajowitz.
WQBELs Karen Holligan September 23, WQBELs – A Four-Piece Puzzle Numerical criteria (toxic pollutants) Water body quality Effluent fraction Bioavailable.
Dissolved Oxygen Pollution Types.
MEASUREMENT OF TOXICITY By, Dr. M. David Department of Zoology, Karnatak University Dharwad.
April 11 Science Fair: What did you like and what did you not like about conducting your science fair experiment? HOMEWORK: Write your abstract at home.
Integrated Watershed Management
Sustainable Development Goal for Water: Indicator 6.3.2
Removal efficiency of nitrate.
C.P.Martinez and L.M. Porticos
WATER POLLUTION IMPACT OF HUMAN ACTIVITIES
Environmental Laws.
Chloride in Urban Streams in Maine
Module 17: MIXING ZONES A limited area or volume of water where initial dilution of a discharge takes place and where numeric water quality criteria.
DURABILITY OF CONCRETE STRUCTURES RURAL POLYTECHNIC TARIHAL
Cara Cowan Watts Graduate Student Biosystems Engineering
State of the Harbor Kaitlyn Shaw Town of Nantucket Natural Resources Department Water Resource Specialist.
Trakya University Department of Biology EDIRNE TURKEY
Planning ACT’s Water Supply
Acute and Chronic Toxicity Testing
Impact of Meteorological Events and Sand Excavation on Turbidity and Total Suspended Solids Levels of Imo River by Dr. Chinedu E. Ihejirika Department.
Anaerobic Ammonium Oxidation (Anammox) for Nitrogen Removal
ASSESSING THE ENVIRONMENTAL CONSEQUENCE OF POTENTIAL MAJOR ACCIDENTS
Lake Clear Victor Castro Eastern Region
Can Wastewater Treatment Plants (WWTPs) cope with future nanoparticles (ENPs) loading scenarios? Valerio Cappadonaa, Rebecca Skuceb, Charles Knappa, Vernon.
Total Maximum Daily Loads
Study on non-compliance of ozone target values and potential air quality improvements in relation to ozone.
Jiří Kučera Harmonization of national legislation with Directive 91/271/EEC on urban waste water treatment Czech project of development cooperation in.
Update to Loxahatchee River Coordinating Council
Westcas position paper
Water Quality-Based Effluent Limits
Robin Youll Office for National Statistics
Update on Whole Effluent Toxicity (WET)
WHALE TAIL PIT Expansion Project
Permit View on Statement 1: Decision-making
Presentation transcript:

Green Mining Conference Water Management and the Environment Maria Story, P. Eng. 13 September 2018

Introduction

It became clear to me early in my career: that water quality was COMPLICATED and CONTROVERSIAL but we had to start looking at every project HOLISTICALLY to make the best decisions for the ENVIRONMENT as a WHOLE focussing on one environmental medium could have more negative impacts on other environmental media

Establishing PWQOs & CWQGs PWQO is the concentration of water quality which is protective of all forms of aquatic life and all aspects of the aquatic life cycles during indefinite exposure to the water (MOECC, 1994) CWQGs is a concentration of water to protect all forms of aquatic life and all aspects of the aquatic life cycles, including the most sensitive life stage of the most sensitive species over the long term (CCME,1999)

20 d very severe unfavourable effect 28-d LC50 7-d LOEC 14-d EC20 (growth) 21-d EC16 (reprod) 7-d LC80 14-d EC50 (growth) 20 d very severe unfavourable effect EC50

Case Studies Historic Cobalt/Coleman Mining Camp Unrealistic Effluent Limits Cobalt Constructed Wetland

Historic Cobalt Mining Camp

20 d very severe unfavourable effect 28-d LC50 7-d LOEC 14-d EC20 (growth) 21-d EC16 (reprod) 7-d LC80 14-d EC50 (growth) 20 d very severe unfavourable effect EC50

Unrealistic Effluent Limits

threshold for sub-lethal effects (12 mon) Published Chronic Toxicity Data for Unionized Ammonia Daily Effluent Limit = 0.04 mg/L Monthly Average Effluent Limit = 0.02 mg/L 62-d EC20 LOEC (4 mon) 30-d IC20 survival/growth 7-d IC20 for fry growth threshold for sub-lethal effects (12 mon) gill damage (6 wks) 7-d EC20 reduction develop

Conservatism when Establishing Effluent Limits Lowest Flow in Receiver (7Q20 = 7 d in 7300 d) Maximum Effluent Flows Maximum Effluent Concentrations Low Effluent Limits Over Engineered Resource-Intensive Treatment Systems

Two Tiered Approach Low Effluent Concentration Limits the original 0.02 and 0.04 mg/L protective during low flow conditions no flow monitoring requirements Higher Effluent Concentration Limits higher flow conditions with receiver flow monitoring requirements to ensure a specific mixing ratio and adequate assimilative capacity

Cobalt Constructed Wetland (on Ferland Tailings)

Cobalt Constructed Wetland - Loadings

Cobalt Constructed Wetland - Concentrations

The 7 words to failure are: “We have always Conclusions The 7 words to failure are: “We have always done it this way.” It is time for change.

Acknowledgements Thanks to: Agnico Eagle Mines Limited for sharing data from their surface water sampling program. and The Corporation of the Town of Cobalt for sharing data from their Industrial Sewage Works Constructed Wetland. Maria Story, P.Eng. (SEI President) maria.story@storyenvironmental.com