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Wastewater use in irrigated agriculture: closing the rural-urban-rural water loop

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Title: Wastewater use in irrigated agriculture: closing the rural-urban-rural water loop


1
Wastewater use in irrigated agriculture closing
the rural-urban-rural water loop
  • Presented at Departmental Seminar Series (Soil,
    Water Environmental Science), University of
    Arizona, 19 February 2007

2
Wastewater Use in Irrigated Agriculture Closing
the Rural-Urban-Rural Water Loop Christopher
Scott Udall Center for Studies in Public Policy,
and Dept. Geography Regional Development Univers
ity of Arizona
3
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Scarcity Competition for Water
  • Declining allocations of water to agriculture
  • Rapid urban growth a global phenomenon
  • Water productivity in agriculture rising (more
    crop per drop)
  • Agriculture increasingly adapting to the use of
    poorer quality water for irrigation

6
Sobering Demographics
  • 880 million additional population by 2015,
    virtually all in developing countries.
  • After 2015, all worldwide growth in population
    will take place in developing country cities.

7
Urban Explosion
  • India will soon cross the 50-50 urban-rural
    population threshold 750 million urban Indians
    by 2050.
  • China is actively planning for cities each with
    more than 100 million population.
  • Africas urban population growth rates among the
    highest in the world.
  • Latin America has been predominantly urban for
    generations.

8
Urban Water Supply Growth
Millennium Development Goals face resource
constraints (water, investment). Progress towards
sanitation goals lagging behind water supply
therefore, wastewater management is critical.
9
Definitions
  • Wastewater partially treated or untreated urban
    sewage
  • Effluent treated to secondary or tertiary
    levels (with or without disinfection)

10
Rural-Urban-Rural Water Loop
  • Transfer of water from agriculture to cities
  • Physically, often entails inter-basin transfers
  • Water rights, property regime, economic issues
  • Urban use, quality degradation depletion
  • Salinity load, even with (because of?) treatment
  • Public health risk (consumers and producers)
  • Agricultural end use of wastewater/ effluent
  • Adapt to quality (nutrients, salinity)
  • Adapt to timing (uniform throughout year)

11
Rural-Urban-Rural Loop Typology
Rural source Urban use Rural end use
Production irrigated ag. Multiple (w/ urban sprawl on ag.). Wastewater WW mixed source for in-formal urban periurb. ag. e.g. Hyderabad, India - Musi
Small-scale rural water Multiple use. Wastewater WW primary source for production irrigated ag. e.g. Mexico City - Mezquital
Production irrigated ag. Multiple use. Effluent Same ag. users as source water (i.e., water swap with treatment). e.g. Monterrey, Mex. Bajo Rio San Juan
12
Hyderabad, India
Sampling Transects III rural (25 40 km) II
periurban (10 25 km) I urban (0 10 km)
13
Hyderabad Water Footprint
14
Hyderabad Water Supply/ Demand
15
Wastewater Biogeochemistry
  • Microbial attenuation and infection
  • Coliform die-off
  • Nematode (hookworm) egg deposition
  • Heavy metals attenuation ( uptake?)
  • Deposition, re-suspension
  • Nutrient attenuation plant uptake, eutrophicn.
  • Dissolved solids concentration, deposition
  • Irrigation diversion, evaporation, return flow

16
40 Km
Hyderabad
17
Coliforms in WastewaterDec. 03 Jan. 05 (red
squares mean value)
18
Nematode Eggs in Wastewater
19
Nematode Prevalence in Farmers
20
Sediment Sampling
Mean egg load per 1 kg of sediment 410,000 (SD
240,000)
21
Heavy Metals in Sediment
Source Gerwe, Caroline. An Assessment of Heavy
Metals Contamination in the Wastewater-Irrigated
Area of the Musi River
22
Dissolved Nitrogen
23
Dissolved Oxygen
24
Total Dissolved Solids
25
TDS Seasonal Variation
26
TDS Conceptual Model
27
Irrigation Adapts to Constant Flow
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Mexico City Water Footprint
26
31
Mexico City Wastewater Sources/Fate
32
Tula Irrigation District
33
Nutrient Uptake, Salt Concentration
34
Monterrey-Bajo Río San Juan Swap
Falcon Reservoir
Marte R. Gómez Reservoir
McAllen, Texas
Bajo Río San Juan Irrigation District
Tamaulipas
El Cuchillo Reservoir
47
35
El Cuchillo
  • Constructed in 1993
  • Supplies 5 m3/s to Monterrey (to be increased to
  • 10 m3/s)
  • MR Gómez reservoir impacts

36
Negotiated Settlement
  • 9 Oct. 1989 Monterrey, federal and Nuevo León
    governments agree to finance and construct El
    Cuchillo dam
  • 6 Sept. 1990 Tamaulipas, federal and Nuevo León
    governments agree to rationalize water use,
    preserve multiple uses of BRSJ irrigation water

37
Effluent the Bargaining Chip
  • Federal CNA allocates 189 MCM (6 m3/s) of
    effluent from Monterrey to BRSJ irrigators
  • Nuevo León assumes responsibility and cost of
    treatment in compliance with federal water
    quality standards
  • Rehabilitation of the Anzaldúas-Rhode pumping
    station on the Río Bravo
  • Relocation of downstream Tamaulipas urban water
    demand from MR Gómez reservoir (Rhode canal)

38
BRSJ Irrigation Water Productivity
39
BRSJ Irrigation Efficiency
But, growing upstream demand and capture of
wastewater will need to pipe it 100 km.
40
Wastewater Use Conclusions
  • Urban growth high tertiary treatment costs
    increasing agricultural reuse
  • Promote beneficial agricultural reuse
  • Mitigate health and environmental risk

41
Risk Mitigation
  • Secondary treatment (biosolids handling
    enforcement is essential)
  • Application method to limit irrigators exposure
  • Market wash water and handling
  • Crop restrictions non-edible and fodder. Limit
    fresh produce irrigation, e.g.

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Treatment for Compliance
  • WHO - 103 faecal coliforms/100 ml
  • Cost of treating raw sewage used for direct
    irrigation to meet WHO standard is approx US125
    per case of infection (of hepatitis, rotavirus,
    cholera, or typhoid) prevented (Fattal, Shuval,
    Laempert, 2004).
  • USEPA zero incremental risk
  • Incremental cost of further treating wastewater
    from WHO to USEPA standard approx. US450,000 per
    case of infection prevented (Fattal, Shuval,
    Laempert, 2004).

44
Policy Implications
  • Planned reuse offers no easy solutions
  • Key to success are
  • coherent legal and institutional framework
  • coordination of multiple government agencies
  • flexible application of the polluter pays
    principle
  • extension to farmers of appropriate practices for
    wastewater use
  • public awareness campaigns to build social
    acceptability for reuse

45
Wastewater Use in Irrigated Agriculture
  • http//www.cabi.org/bk_BookDisplay.asp?PID1785
  • http//www.idrc.ca/en/ev-31595-201-1-DO_TOPIC.html
  • Introduction management challenges
  • Typology and global assessment
  • Livelihoods the key driver
  • WHO health guidelines
  • Cost of guidelines compliance

46
Case Studies in the Book
  • Kenya
  • Ghana
  • Vietnam
  • Pakistan
  • Senegal
  • India
  • Bolivia
  • Mexico
  • Jordan
  • Tunisia

Formal programs of planned reuse with treatment
47
Thank you.
  • Christopher Scott
  • cascott_at_email.arizona.edu
  • 626-4393
  • Acknowledgements
  • Stephanie Buechler, UA Bureau of Applied
    Research in Anthropology
  • Pay Drechsel, International Water Management
    Institute, Ghana
  • Jeroen Ensink, London School of Hygiene and
    Tropical Medicine
  • Naser Faruqui, International Development
    Research Centre
  • Francisco Flores, Cornell University
  • Jesús R. Gastélum, UA Dept. of Civil Engineering
  • Liqa Raschid, International Water Management
    Institute
  • Daan van Rooijen, International Water Management
    Institute, Ghana
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