chloride and ammonia water quality standards update
TRANSCRIPT
Chloride and AmmoniaWater Quality Standards Update
AMI Environmental ConferenceKansas City, MissouriMarch 10, 2011
Gregory L. Sindt, P.E.515‐233‐6100gregsi@bolton‐menk.com
Application of Standards
Standards apply to concentrations in the streamLow stream flows used as basis– 7Q10 or lowest flow in seven consecutive days in ten years (0.2% probability)
Treatment plant maximum design flow typically used as basisVery conservative approach
0
100
200
300
400
500
600
700
800
900
1000
0 500 1000 1500 2000
Acute Ch
lorid
e Stan
dard, m
g/L
Sulfate, mg/L
Acute Chloride Standard300 mg/L Hardness
1988 Guideline
EPA Jan 2009
EPA w/ Data Added
Standards Development
STATES develop water quality standards as administrative rules– Technical advisory committee approach in some states
– Public comment on draft rules
US EPA Regional Offices review and approve state standards
Standards Development
EPA develops National Guideline Criteria for many toxics (304(a) Criteria Document)– Peer reviewed– Public comment– GUIDELINES for reference by states
States are NOT required to adopt the National Criteria as state standards
Standards Development
STATES develop standards that are adequate for protection of water uses in the state– Adopt or modify EPA Guideline Criteria
Less stringent than EPA National Criteria if sensitive species included in EPA Criteria are not present in StateMore stringent than EPA National Criteria if sensitive species of significant economic or recreational benefit are present in State
Standards Development
States must review standards every three years– Revise standards to incorporate new toxicity data and EPA criteria
– Formal rule making process for standards revisions
Standards Development
Dischargers can develop “site specific” standards for its receiving stream– Develop less stringent standard by deleting data for sensitive species that would not be present in stream (species deletion procedure)
Ammonia Standards
December 2009 Draft EPA Update Document– Modification of 304(a) National Ammonia Criteria– Includes new data on freshwater mussels
Mussels extremely sensitive to ammonia
– Proposed two sets of criteriaMussels present criteriaMussels absent criteria
Ammonia Standards
Mussel present criteria very stringent– Mussels present chronic criteria only 15% of mussels absent criteria (pH 8, 25 deg. C)
– Mussel present criteria seven times more stringent than mussels absent criteria
Example at pH 8 and 25 degrees C1.8 mg/L chronic criteria mussels absent0.26 mg/L chronic criteria mussels present
– Five times more stringent than current criteria
Ammonia Standards
Public comments received in March 2011– Challenged mussel toxicity test methods for mussels
– Questioned lack of clear dose/response relationship
Ammonia Standards
EPA proposed revisions to draft document– New toxicity data on sensitive snails
Similar ammonia sensitivity as musselsSnails can live almost anywhere
– May replace the “mussels present” and “mussels absent” criteria with only one set of criteria
Criteria could be similar to draft “mussels present” for ALL STREAMS.
– Criteria will be five times more stringent than current
Ammonia Standards
Example comparison (ph 8, 25 degrees C)– 1.8 mg/L current chronic criteria– 0.26 mg/L proposed criteria
EPA schedule– February 2011 snail toxicity study peer review– Spring 2011 publish final criteria document
(Probably) single sets of acute and chronic criteria similar to “mussels present” draft criteria
Ammonia Standards
Impact of new criteria– Ammonia discharge limits on low flow streams could be very stringent (less than 0.5 mg/L)
– Consideration of mussels in criteria development will carry over to criteria for other water quality parameters
Concerns about mussel toxicity testing methods
Chloride Regulatory History
Inconsistent regulation of salts– Monitoring parameters
Total Dissolved Solids (TDS)Conductivity or increase in conductivitySpecific constituents
• Chloride• Sulfate• Expanding list
–Often ignored state standards
Chloride Standards Development
1988 EPA National Guideline Criteria– 860 mg/L acute– 230 mg/L chronic
States adopt standards– Specific standards for each state– Many states adopted the EPA guidelines
Chloride Standards Development2009 Iowa Adopts New Chloride Standards– Replaces TDS standard with chloride and sulfate– Chronic chloride standard significantly less stringent than EPA 304(a) National Guideline
– Standards less stringent for higher hardness– Standards slightly more stringent for higher sulfate– Default values (200 mg/L hardness, 63 mg/L SO4
2‐)389 mg/L chronic (230 mg/L EPA National Criteria)629 mg/L acute (860 mg/L EPA National Criteria)
Chloride Standards Development
May 2010 ‐ US EPA approved Iowa standards Chloride and sulfate standards approvedTDS deletion not yet approvedFish and Wildlife Service (FWS) may object to deleting TDS standard
Chloride Standards Development
2011 EPA plans to revise the National Criteria– Include the Iowa data in recalculating criteria– Anticipate national criteria will be similar to Iowa– Plan to publish draft criteria Spring 2011
Issues Regarding Iowa Standards
EPA has not approved deleting TDS standard– Fish and Wildlife Service may object
Antidegradation arguments– Revising the standards may be viewed as an increase in the discharge of pollutants
Issues Regarding Iowa Standards
Antibacksliding argument– New standards may be viewed as a relaxation of environmental standards
Protection of fingernail clam– Fingernail clam is most sensitive species in data base
– Some may consider standard not protective of fingernail clam
Emerging Choride/TDS Issues
EPA Benchmark for conductivity in Appalachian Streams – August 2010– Appalachia mining area concerns– Very stringent
300 uS/cm (equivalent to about 200 mg/L TDS)
Emerging Chloride/TDS Issues
Impact on fresh water mussels– Canadian draft chloride standards
Impact on glochidia life stage mussels128 mg/L chronic “benchmark”536 mg/L acute “benchmark”Included mussel glochidia data (EPA did not)
– Widespread interest in decline of mussel population in U.S.
– Carryover of mussel toxicity concepts from the EPA ammonia criteria revisions
Other StatesStates considering Iowa Standards– Kansas– Missouri– Kentucky– Indiana
Pennsylvania 2010 revisions– 500 mg/L TDS monthly mean standard END OF PIPE for new and increased discharges
– Chloride standards may be reviewed soon
Other StatesUS EPA advising other states to consider Iowa standardsAMI and other groups could encourage other states to adopt Iowa standards
Other States
States must conduct triennial review of water quality standards– Identify new pollutants of concern– Revised existing standards based on new information
Possible resistance to revising standards– Antibacksliding
Other States
Replace TDS or conductivity standards with specific parameters ‐ chloride and sulfate
Iowa Chloride Standards
Standards Details and Implementation Information
Iowa Chloride Standards
Chloride standards as function of hardness and sulfate concentrations–Acute: (287.8) (hardness)0.205797 (sulfate)‐0.07452
–Chronic: (177.87) (hardness)0.205797 (sulfate)‐0.07452
Iowa Chloride Standards
Default values if no site specific data– 200 mg/L Hardness (10th percentile)– 63 mg/L Sulfate
– 389 mg/L chronic Chloride standard– 629 mg/L acute Chloride standard
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0 100 200 300 400 500 600 700
Acute Ch
lorid
e Stan
dard, m
g/L
Hardness, mg/L as CaCO3
Acute Chloride Standard65 mg/L Sulfate
1988 Guideline
Iowa Standard
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100
200
300
400
500
600
700
800
900
1000
0 500 1000 1500 2000
Acute Ch
lorid
e Stan
dard, m
g/L
Sulfate, mg/L
Acute Chloride Standard300 mg/L Hardness
1988 Guideline
EPA Jan 2009
EPA w/ Data Added
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100
200
300
400
500
600
700
800
900
1000
0 500 1000 1500 2000
Acute Ch
lorid
e Stan
dard, m
g/L
Sulfate, mg/L
Acute Chloride Standard300 mg/L Hardness
1988 Guideline
Iowa Standard
0
100
200
300
400
500
600
700
800
900
1000
0 500 1000 1500 2000
Acute Ch
lorid
e Stan
dard, m
g/L
Sulfate, mg/L
Acute Chloride Standard300 mg/L Hardness
1988 Guideline
EPA Jan 2009
EPA w/ Data Added
0
100
200
300
400
500
600
0 100 200 300 400 500 600 700
Chronic Ch
lorid
e Stan
dard, m
g/L
Hardness, mg/L as CaCO3
Chronic Chloride Standard65 mg/L Sulfate
1988 Guideline
Iowa Standard
0
100
200
300
400
500
600
700
800
900
1000
0 500 1000 1500 2000
Acute Ch
lorid
e Stan
dard, m
g/L
Sulfate, mg/L
Acute Chloride Standard300 mg/L Hardness
1988 Guideline
EPA Jan 2009
EPA w/ Data Added
0
100
200
300
400
500
600
0 500 1000 1500 2000
Chronic Chloride Stan
dard, m
g/L
Sulfate, mg/L
Chronic Chloride Standard300 mg/L Hardness
1988 Guideline
Iowa Standard
IDNR Compliance Approach 1
Gather data for site specific standards derivation– Stream background chloride, hardness, sulfate– Discharge effluent hardness and sulfate– 100 data points required
Once per week for two yearsTwice per week for one year
IDNR Compliance Approach 2
Source Reduction Efforts (Voluntary)– Optimize home water softeners– Remove home water softeners– Replace home softeners with exchange tanks– Soften water only on selected use points– Remove/replace central ion exchange softeners– BMPs in industries to prevent salt discharge
IDNR Compliance Approach 3
Mandatory Source ReductionEvaluate options for chloride removal at wastewater treatment plantsCompliance Schedules in NPDES permits– Extended schedules in lieu of variances
Variances from Water Quality Standards– Affordability– Wide spread social and economic impact
Compliance Alternatives
No economical method for chloride removalSource reductionFlow augmentation (allowed for meeting discharge limits that are based on water quality standards)Effluent diffuser (eliminates mixing zone limitations)
Compliance Alternatives
Variances from standards– No economic alternatives– Temporary (must be working toward compliance with the standards)
Compliance Alternatives
Site specific standards– Evaluation of receiving stream– Delete species not expected to be in the stream from the calculation of standards
– Permanent modification (as compared with variance approach)
Questions and Discussion
Gregory L. Sindt, P.E.Bolton & Menk, Inc.gregsi@bolton‐menk.com515‐233‐6100