Manitoba Water Quality Standards, Objectives, and Guidelines 2002 Dwight Williamson, Manager Water Quality Management Section Manitoba Conservation 1
Outline Brief history Review process Overview of proposed revisions Introduce concepts likely to be discussed during these hearings Ammonia objectives Overview of water quality in Red River in relation to MWQSOG 2002 Concluding comments 2
History of Program 1976-1979 1980-1982 1983-1988 1988-1990 1990-1991 2000-2003 3
Review Process Information and initial comments April 20, 2000 - September 29, 2000 Detailed technical review February 1, 2001 - October 31, 2001 Final draft review November 22, 2002 - March 31, 2003 - FINAL DRAFT - - For Additional Review and Comment - Manitoba Water Quality Standards, Objectives, and Guidelines 4
Water Quality Protection Technology-Based Approach Consistent for each major water discharge sector Best Practicable or Best Available Technology Water Quality-Based Approach Considers unique water uses, stream flow, and water quality at each site Ensures that activities do not cause exceedances of water quality objectives Includes concept of assimilative capacity 5
Assimilative Capacity and Wasteload Allocation 500 Concentration (mg/l) 400 300 200 100 Tier II - Water Quality Objective 0 0 5 10 15 20 25 30 35 40 45 50 55 Distance (km) 6
Principal Changes Three-tiered approach Surface water and groundwater quality Ecosystem health - biological communities Sediment and tissue residue guidelines 7
Tier I: Water Quality Standards Technology-based standards Municipal wastewater effluents Fecal coliform densities (200 organisms/100 ml) Biochemical Oxygen Demand (30 mg/l) Total Suspended Solids (30 mg/l) Key existing legislation is referenced, including ground water Not intended to be modified 8
Tier II: Water Quality Objectives Short list of variables (<20) Chronic and acute Common pollutants in Manitoba Good confidence for Manitoba May be modified based upon scientificallysound site-specific information Implementation Mixing zones Design low flows Three levels of protection Develop effluent discharge limitations 9
Tier II (continued) Ammonia Trace metals Chlorine Cyanide Dissolved oxygen Fecal coliform and Escherichia coli Nitrate-nitrite Sodium adsorption ratio and major ions or salts Suspended sediments and turbidity Temperature 10
Ammonia Included as a Tier II Water Quality Objective 1988 MSWQO modified from US EPA Criteria published in 1984 US EPA 1984 criteria superceded by new criteria published in 1999 MWQSOG 2002 based on US EPA 1999 11
Ammonia (continued) 12 separate objectives 6 apply to cool water assemblages 3 apply when early life stages absent 3 apply when early life stages present 6 apply to cold water assemblages 3 apply when early life stages absent 3 apply when early life stages present 12
Ammonia (continued) Include both chronic and acute 30 day average (chronic) 4 day average (chronic) 1 hour average (acute) 13
Comparison of MSWQO 1988 to MWQSOG 2002 Comparison of 1988 and 2002 Water Quality Objectives for Ammonia at ph 8.00 Total Ammonia (mg/l as N) 10 8 6 4 2 0 0 5 10 15 20 25 30 1988 MSWQO 30 Day (ELS Present) 4 Day (ELS Present) 30 Day (ELS Absent) 4 Day (ELS Absent) 1 Hour Temperature (C) 14
Implementation - Mixing Zones Not reasonable to require all objectives to be met at end-of-pipe Tier I - Water Quality Standards still apply A relatively small area is allowed for mixing to occur where not all objectives have to be met Allow a zone of passage Not cause acute lethality Others 15
Implementation - Design Low Flows Not reasonable to require wastewater treatment systems to be designed to meet objectives all of the time especially under low stream flows Recognizes that healthy aquatic life communities can withstand occasional stress and can recover 30Q10 7Q10 1Q10 16
Design Low Flows (continued) Statistical technique to identify the probability of a low flow event based upon historical hydrological record Longest period of representative historical flow record must be used to confidently predict most likely probability of future low flow event fundamental statistical principle 17
Design Low Flows (continued) Similar principle used by Manitoba for predicting the probability of other hydrological events low flows to allocate water for withdrawal high flows to protect public health and property from flood events 18
Tier III: Water Quality Guidelines General statements of desired quality Long list of pollutants, mainly from CCME (>100) Water quality Sediment quality Tissue residues 19
Tier III (continued) Not all pollutants of concern at present in Manitoba May not have good confidence for Manitoba Implementation More flexible than Objectives Assist to interpreting monitoring data Can be used as a basis for developing Objectives or Standards 20
Other Proposed Changes Guidance for mixing zones Adoption of both acute and chronic objectives Objectives for metals expressed as dissolved forms Definition of field crop irrigation expanded to include irrigation of parklands and golf courses Deleted irrigation category for short-term protection of medium to fine textured soils 21
Other Proposed Changes (continued) Deleted secondary recreation category Fecal coliform objective identified for protection of groundwater used for drinking purposes Guideline for ensuring biological integrity Guideline for maintenance of minimum instream flows 22
Other Proposed Changes (continued) Guideline for promoting water conservation Guideline related to non-indigenous species 23
Issues Presently Under Review Inadequate, scientificallydefensible water quality objectives for nitrogen and phosphorus Nutrient Management Strategy Once developed, adopt nutrient objectives in the MWQSOG 24
Stream Water Quality Monitoring 25
Fecal Coliform in Red River Fecal Coliform Densities in Red River near Selkirk (May 1 to September 30) 100000 10000 1000 100 10 1 26 1973-09-05 1975-09-05 1977-09-05 1979-09-05 1981-09-05 1983-09-05 1985-09-05 1987-09-05 1989-09-05 1991-09-05 1993-09-05 1995-09-05 1997-09-05 Fecal Coliform (organisms/100 m 1999-09-05 2001-09-05
Ammonia in Red River (Early Life Stages Present) Ammonia in Red River at Selkirk (Early Life Stages Present) 25.00 20.00 15.00 10.00 5.00 0.00 27 1970-06-09 1972-06-09 1974-06-09 1976-06-09 1978-06-09 1980-06-09 1982-06-09 1984-06-09 1986-06-09 1988-06-09 1990-06-09 1992-06-09 1994-06-09 1996-06-09 Total Ammonia (mg/l) 1998-06-09 2000-06-09 2002-06-09
Ammonia in Red River (Early Life Stages Absent) Ammonia in Red River at Selkirk (Early Life Stages Absent) 25.00 20.00 15.00 10.00 5.00 0.00 28 1974-12-30 1976-12-30 1978-12-30 1980-12-30 1982-12-30 1984-12-30 1986-12-30 1988-12-30 1990-12-30 1992-12-30 1994-12-30 1996-12-30 Total Ammonia (mg/l) 1998-12-30 2000-12-30
Dissolved Oxygen in Red River (Early Life Stages Present) Dissolved Oxygen in the Red River near Selkirk (Early Life Stages Present) 16.0 15.0 14.0 13.0 12.0 11.0 10.0 9.0 8.0 7.0 6.0 5.0 4.0 3.0 2.0 1.0 0.0 29 1967-01-13 1969-01-13 1971-01-13 1973-01-13 1975-01-13 1977-01-13 1979-01-13 1981-01-13 1983-01-13 1985-01-13 1987-01-13 1989-01-13 1991-01-13 1993-01-13 Dissolved Oxygen (mg/l 1995-01-13 1997-01-13 1999-01-13 2001-01-13
Dissolved Oxygen in Red River (Early Life Stages Absent) Dissolved Oxygen in the Red River near Selkirk (Early Life Stages Absent) 16.0 15.0 14.0 13.0 12.0 11.0 10.0 9.0 8.0 7.0 6.0 5.0 4.0 3.0 2.0 1.0 0.0 30 1967-01-13 1969-01-13 1971-01-13 1973-01-13 1975-01-13 1977-01-13 1979-01-13 1981-01-13 1983-01-13 1985-01-13 1987-01-13 1989-01-13 1991-01-13 1993-01-13 Dissolved Oxygen (mg/l 1995-01-13 1997-01-13 1999-01-13 2001-01-13
2,4-D in Red River 2,4-D in Red River near Selkirk 4.50 4.00 3.50 3.00 2.50 2.00 1.50 1.00 0.50 0.00 31 1984-02-23 1986-02-23 1988-02-23 1990-02-23 1992-02-23 1994-02-23 1996-02-23 2,4-D (ug/l) 1998-02-23 2000-02-23 2002-02-23
Zinc in Red River Zinc (extractable) in the Red River near Selkirk 500 450 400 350 300 250 200 150 100 50 0 32 1974-08-23 1976-08-23 1978-08-23 1980-08-23 1982-08-23 1984-08-23 1986-08-23 1988-08-23 1990-08-23 1992-08-23 1994-08-23 1996-08-23 Zinc (extractable) (µg/l 1998-08-23 2000-08-23 2002-08-23
Concluding Comments Substantive revisions incorporated to MWQSOG Final draft presently available for public review MWQSOG 2002 are the most comprehensive in Canada Represent the most current scientific information available and therefore, are being used to guide water quality management 33
Concluding Comments (continued) Water quality issues of concern bacteria ammonia dissolved oxygen nutrients 34
Concluding Comments (continued) Emerging water quality issues pharmaceuticals endocrine disrupting substances 35
Thank You 36