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Backcountry Black Water
Management Options Analysis
Research by
Stantec Consulting Ltd. and SD Consulting Group
Presented by
Karen Rollins, BEES
• To evaluate black water management options
at remote alpine and subalpine huts in
Canada’s mountain regions
– life cycle costs
– environmental impacts
Project Goal
Black Water Management Options
1. Pit toilet
2. Barrel fly-out
3. Incinerating toilet
4. Carry-out
5. Heated chamber
composting toilet
– alpine
– subalpine
Alpine Composting
- urine separation
- urine evaporation
- solids composted
- 80% reduced
Subalpine Composting
- urine separation
- urine treated on site
- solids composted
- 90% reduced
Costs
– Construction
– Operation and
maintenance
– Total life cycle
Analysis
Environmental Impacts
0 to 5 rating
1. User health (potential for
personal contact)
2. Water quality (ground and
surface water)
3. Non-renewable energy use
(diesel, propane, fuel)
4. Aesthetics (odours, visual
impacts)
Location 1: Alpine, low use
Location 2: Alpine, high use
Location 3: Subalpine, moderate use
Locations
Location 1:
Great Cairn
Ben Ferris Hut
Selkirk Range
Mt. Sir Sandford
Alpine (6200 ft)
Low use
(100 overnights/year)
Location 2: Bow Hut
Wapta Icefields
Alpine (7710 ft)
High use (3000
overnights/yr)
Location 3: Elizabeth Parker Hut
Lake O’Hara
Subalpine
(6700 ft)
Moderate use
(800 overnights
per yr)
0
5000
10000
15000
20000
25000
30000
35000
40000
45000
$
Barrel Fly
Out
Incinerating Carry-out Composting
Construction Operation Life Cycle
Cost Comparison: Alpine 100 overnights
0
20000
40000
60000
80000
100000
120000
140000
$
Barrel Fly
Out
Incinerating Carry-out Composting
Construction Operation Life Cycle
Cost Comparison: Alpine 3000 overnights
0
10000
20000
30000
40000
50000
60000
70000
$
Pit Toilet Barrel Fly
Out
Incinerating Carry-out Composting
Construction Operation Life Cycle
Cost Comparison: Subalpine 800 overnights
0
1
2
3
4
5
Pit Toilet Incinerating Composting
Alpine
User Health Water Quality Non-renewable Energy Aesthetics
Environmental Impacts Comparison
Conclusions
• Barrel fly out and incinerating are generally more costly
than other options
• Carry out works best in locations that receive low use,
but becomes increasingly expensive in locations that
receive high use
• Composting toilets cost less and have fewer
environmental impacts than barrel fly out or incineration
and are viable options in most locations
• There is not one perfect black water management
solution for every location
BEES is facilitating additional research into:
– Composting process
– Urine separation and treatment
– Dehydration / incineration combination systems
Project Outcome
Composting Research
‘Life is like a sewer’
Precautionary approach on what comes out
Requires measuring & analysis
standardization
Controlling Variable (ongoing)
% Moisture, Temp, Aeration
Pathogen Reduction (lab)
Fecal coliform bact. (<1000col. count)
End Product = Compost?
Stability (Carbon degredation)
CO2 Evolution / Oxygen Uptake
Maturity (Nitrification NH3-NO2-NO3)
NH3 concentration
User friendly version: Solvita - $10/test
C/N not a reliable indicator of completeness
Urine Separation
Urine Facts:
1. Urine is sterile
2. There is less odour when urine and solids are
separated
3. 90% of sewage is urine (literature)
4. Little field research to validate
1. Bugaboos Mass Balance
1. Barrel fly out (regular) = 0.63kg/use
2. Urine Diversion (urinal & seat) =
0.03kg/use
Dehydration and Incinerating
Need scalable & transferable index
Evaluate performance, cost, impacts
(LCA & Mass Balance)
Mass Balance (urine d, exhaust, dehydrate, incin)
How effective truly?
Door counters & weigh scales
LCA
What value / objective
Environmental (CO2 equiv emmissions)
Human (DALY)
Capital / Operating
Eg: Barrel fly out – Golden, BC = 70-100 CO2
vs Incinerate onsite – Bugaboos, BC = 40-50 CO2
www.beeshive.org

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Karen Rollins - Backcountry Black Water Management Options Analysis

  • 1. Backcountry Black Water Management Options Analysis Research by Stantec Consulting Ltd. and SD Consulting Group Presented by Karen Rollins, BEES
  • 2. • To evaluate black water management options at remote alpine and subalpine huts in Canada’s mountain regions – life cycle costs – environmental impacts Project Goal
  • 3. Black Water Management Options 1. Pit toilet 2. Barrel fly-out 3. Incinerating toilet 4. Carry-out 5. Heated chamber composting toilet – alpine – subalpine Alpine Composting - urine separation - urine evaporation - solids composted - 80% reduced Subalpine Composting - urine separation - urine treated on site - solids composted - 90% reduced
  • 4. Costs – Construction – Operation and maintenance – Total life cycle Analysis Environmental Impacts 0 to 5 rating 1. User health (potential for personal contact) 2. Water quality (ground and surface water) 3. Non-renewable energy use (diesel, propane, fuel) 4. Aesthetics (odours, visual impacts)
  • 5. Location 1: Alpine, low use Location 2: Alpine, high use Location 3: Subalpine, moderate use Locations
  • 6. Location 1: Great Cairn Ben Ferris Hut Selkirk Range Mt. Sir Sandford Alpine (6200 ft) Low use (100 overnights/year)
  • 7.
  • 8.
  • 9.
  • 10. Location 2: Bow Hut Wapta Icefields Alpine (7710 ft) High use (3000 overnights/yr)
  • 11.
  • 12.
  • 13.
  • 14. Location 3: Elizabeth Parker Hut Lake O’Hara Subalpine (6700 ft) Moderate use (800 overnights per yr)
  • 15.
  • 16.
  • 17.
  • 18. 0 5000 10000 15000 20000 25000 30000 35000 40000 45000 $ Barrel Fly Out Incinerating Carry-out Composting Construction Operation Life Cycle Cost Comparison: Alpine 100 overnights
  • 19. 0 20000 40000 60000 80000 100000 120000 140000 $ Barrel Fly Out Incinerating Carry-out Composting Construction Operation Life Cycle Cost Comparison: Alpine 3000 overnights
  • 20. 0 10000 20000 30000 40000 50000 60000 70000 $ Pit Toilet Barrel Fly Out Incinerating Carry-out Composting Construction Operation Life Cycle Cost Comparison: Subalpine 800 overnights
  • 21. 0 1 2 3 4 5 Pit Toilet Incinerating Composting Alpine User Health Water Quality Non-renewable Energy Aesthetics Environmental Impacts Comparison
  • 22. Conclusions • Barrel fly out and incinerating are generally more costly than other options • Carry out works best in locations that receive low use, but becomes increasingly expensive in locations that receive high use • Composting toilets cost less and have fewer environmental impacts than barrel fly out or incineration and are viable options in most locations • There is not one perfect black water management solution for every location
  • 23. BEES is facilitating additional research into: – Composting process – Urine separation and treatment – Dehydration / incineration combination systems Project Outcome
  • 24. Composting Research ‘Life is like a sewer’ Precautionary approach on what comes out Requires measuring & analysis standardization Controlling Variable (ongoing) % Moisture, Temp, Aeration Pathogen Reduction (lab) Fecal coliform bact. (<1000col. count) End Product = Compost? Stability (Carbon degredation) CO2 Evolution / Oxygen Uptake Maturity (Nitrification NH3-NO2-NO3) NH3 concentration User friendly version: Solvita - $10/test C/N not a reliable indicator of completeness
  • 25. Urine Separation Urine Facts: 1. Urine is sterile 2. There is less odour when urine and solids are separated 3. 90% of sewage is urine (literature) 4. Little field research to validate 1. Bugaboos Mass Balance 1. Barrel fly out (regular) = 0.63kg/use 2. Urine Diversion (urinal & seat) = 0.03kg/use
  • 26. Dehydration and Incinerating Need scalable & transferable index Evaluate performance, cost, impacts (LCA & Mass Balance) Mass Balance (urine d, exhaust, dehydrate, incin) How effective truly? Door counters & weigh scales LCA What value / objective Environmental (CO2 equiv emmissions) Human (DALY) Capital / Operating Eg: Barrel fly out – Golden, BC = 70-100 CO2 vs Incinerate onsite – Bugaboos, BC = 40-50 CO2