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The human footprint on water :
 agricultural, industrial, and urban
impacts on the quality of available
 water globally and in the Andean
                region
   Mark Mulligan, King’s College London,
              UNEP-WCMC
        mark.mulligan@kcl.ac.uk
                [30 mins]
The issue
• Land use and cover change affects hydrological processes
  and thus downstream users of water
• With increasing populations and human appropriation of
  land careful management of these impacts is necessary
• PES schemes are one mechanism by which downstream
  beneficiaries can pay upstream land managers for the
  hydrological services provided
• The hydrological services considered are generally water
  quantity, flow regulation and water quality
• Whilst there are reasonable data and spatial models for
  water quantity and flow regulation (in part because of the
  availability of remotely sensed data...
• Spatial water quality data and models are much less
  developed
Rules of thumb for the water service benefits of ‘protected’ areas
            Water quantity services
            •Protected ecosystems do not necessarily generate more
            rainfall than agricultural land uses.
            •Protected ecosystems may have higher evapotranspiration
            and thus lower water yields
            Thus quantity benefits difficult to prove
            Water regulation services
            •Protected ecosystems do not protect against the most destructive
            floods
            •For ‘normal’ events they do encourage more subsurface flow and
            thus more seasonally regular flow regimes
            Likely benefits especially in highly seasonal environments

            Water quality services (quantity for a purpose)
            •Protected ecosystems encourage infiltration leading to lower soil
            erosion and sedimentation
            •Unprotected land will tend to have higher inputs of pesticides,
            herbicides, fertilisers ...
            Clear benefits of PA’s: generation of higher quality water than non-
            protected areas
Quality determines quantity

1. Water quality = water availability (for a
   purpose)
2. Quantity and access can be high but if
   quality is not sufficient then water
   scarcity can still exist
3. Countries like Colombia have a lot of
   water but to what extent is it all usable
   without expensive water treatment?
Q. How can we understand the impact of human activity on water
    quality when water quality cannot be assessed from remote
                             sensing?

A1. identify the proportion of your water originating in upstream
                           protected areas
 A2. Identify the point and non point sources and calculate the
              ‘upstream human influence’ on river water
Protected areas : nature’s water filter




•12-14% of the terrestrial
surface is nominally protected
•34% of ice free areas are used
for agriculture and grazing
•The rest is ice, desert,urban or
unprotected wilderness

•Mean management budget:
$8.75 per km2*                        1872
                                    *estimated on the basis of James, A.N., Green, M.J.B. and Paine, J.R. 1999. A Global Review
                                    of Protected Area Budgets and Staffing. WCMC – World Conservation Press, Cambridge, UK. vi + 46pp
Quantifying the hydrological value of global protected areas

Protected areas may help with water quantity and regulation functions and
certainly help with water quality functions.

Protected areas provide a ‘purification function’ on the basis that they tend to
have lower human influence on water.

Assumption:
Water draining from a protected area is better (higher quality, better regulated)
than water that drains from non-protected areas

Method
1.  Combine global rainfall dataset (1km resolution) with global dataset of flow directions (Hydro1k,
    HydroSheds)
2. Route rainfall down the flow network
3.  For each pixel downstream calculate the proportion of runoff in that pixel derived from protected
    areas upstream
4.  Combine with population and urban areas datasets (CIESIN) and calculate the number of persons
    benefitting from runoff originating in protected areas
5.  Put online in Google maps/Earth : see http://www.kcl.ac.uk/geodata
6.  Repeat for other ‘contributing’ areas (forests, mountain forests, non-protected but non-
    agricultural areas etc.)
% of water originating in a protected area – WDPA 2009 (Colombia)    [gl_pc_wc_fin]




    Protected areas provide a
    ‘purification function’ on the basis
    that they tend to have lower
    human influence on water.

    As you travel downstream
    from the protected areas their
    contribution to flow diminishes as
    rivers are swamped with water
    from non-protected areas




                                                see www.kcl.ac.uk/geodata
Modelling the human footprint on water




                           0.1*Pr            1.0*Pm             P non-human-influenced


                                                            Frac*Pa




       Frac*Pg         1.0*Pog
                                    1.0*Pu



         P non-human-influenced                   Frac*Pc

         Human Footprint on Water=∑Ppolluting /∑Ptotal
Roads         Mines
                            Point sources




Urban areas   Oil and gas
Pasture               Cropland
                                 Non-point sources

                  +




Protected areas   Unprotected agriculture




-                 =
% of water that is human impacted




At the global scale dominated by the human agricultural footprint
% of water that is human impacted




At the continental scale the
influence of roads and
protected areas becomes
more obvious
% of water that is human impacted




           At the national scale the
           downstream decay of
           influence away from
           agricultural and urban areas is
           clearer.
           We might expect the human
           influence to be reflected in
           higher sediment loads,
           organic and inorganic
           contaminants, incl. pesticides
           and fertiliser etc.
           This decay results from the
           dilution of human influenced
           water with runoff from less
           influenced areas.
% of water that is human impacted




       At the regional scale the distance
       decay is clear with some rivers still
       being 25% influenced by upstream
       polluting activities some 150 km
       downstream.
       The extent of the influence depends
       on the area of the polluting activity
       (though in reality the intensity of
       pollution will also be important.
       Protected areas ‘purify’ through
       dilution
       Oil wells may have a locally intense
       influence but it is soon diluted and
       fades quickly
       Takes no account of exposure levels :
       a measure of influence not of
       toxicity
% of water that is human impacted
(transparent=negligible influence)




       The human footprint on water is
       concentrated around human
       populations (roads, agric, industry,
       urban tend to coalesce).

       Thus around major cities water
       quality could be heavily influenced

       Strategic positioning of protected
       areas can have positive impacts on
       the water supply of urban areas
% of water supply to urban areas that is human impacted




At the local scale supply to urban areas is influenced by water diversions,
aqueducts, transfers etc. for which there are no data globally.
But, if we assume that rivers running into urban areas supply those areas with
water then we can map the heavily impacted urbanisations
Many of these cities will use intensive water treatment to offset these impacts
% of water supply to urban
areas that is human
impacted
    Although Colombia has a lot of
    water it also has high
    population, large urbanisation
    and intensive agriculture in the
    Andes.

    Colombia’s urban water supplies
    are thus heavily influenced by
    upstream human activity

    This necessitates costly
    diversion schemes or water
    treatment.

    Putting a natural PA buffer
    between populations and the
    mess they create can deliver
    clear water quality benefits at
    low cost.
Thank you




Questions?
% of water supply to urban
areas that is human
impacted
Methods
1. Map global distribution of threat factors (1km spatial resolution GIS database) for
   point and non point sources
2. Integrate global maps of water inputs i.e. Rainfall (from WorldClim and TRMM)
3. Integrate global maps of flow directions (Hydro1k, Hydrosheds)
4. Calculate influence of each upstream point and non-point source as :

Area of point source polluting activities+ = (mines + oilandgas + roads++*0.1 + urban)
Area of unprotected agricultural land+ = (pasture + cropland) * (1-protected)

Total polluting area per pixel (P) = max (1.0, point source polluting activities,
unprotected agricultural land)

These were summed downstream along the flow network top give Pd
The rainfall (Rf) falling on all areas was also calculated and summed downstream to
   give Rfd.
Human influence (%) = (Pd/Rfd) * 100 (the percentage of flow in a given pixel that fell
   as rain on an upstream human influenced area: a measure of the potential
   upstream influences on water quality).
+Mines= mine according to Hearn et al. (2003), Oilandgas = oil and gas field according to Hearn et al. (2003) (binary), Roads = roads (binary), Urban = urban
      area according to CIESIN et al. (2004) (binary), Pasture = pasture land according to Ramankutty et al. (2008), Cropland = cropland according to
      Ramankutty et al. (2008), Protected= nationally or internationally protected areas according to WDPA (2009) (binary).
++ roads , if present, are assumed to occupy 10% of the pixel area

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The human footprint on water : agricultural, industrial, and urban impacts on the quality of available water globally and in the Andean region

  • 1. The human footprint on water : agricultural, industrial, and urban impacts on the quality of available water globally and in the Andean region Mark Mulligan, King’s College London, UNEP-WCMC mark.mulligan@kcl.ac.uk [30 mins]
  • 2. The issue • Land use and cover change affects hydrological processes and thus downstream users of water • With increasing populations and human appropriation of land careful management of these impacts is necessary • PES schemes are one mechanism by which downstream beneficiaries can pay upstream land managers for the hydrological services provided • The hydrological services considered are generally water quantity, flow regulation and water quality • Whilst there are reasonable data and spatial models for water quantity and flow regulation (in part because of the availability of remotely sensed data... • Spatial water quality data and models are much less developed
  • 3. Rules of thumb for the water service benefits of ‘protected’ areas Water quantity services •Protected ecosystems do not necessarily generate more rainfall than agricultural land uses. •Protected ecosystems may have higher evapotranspiration and thus lower water yields Thus quantity benefits difficult to prove Water regulation services •Protected ecosystems do not protect against the most destructive floods •For ‘normal’ events they do encourage more subsurface flow and thus more seasonally regular flow regimes Likely benefits especially in highly seasonal environments Water quality services (quantity for a purpose) •Protected ecosystems encourage infiltration leading to lower soil erosion and sedimentation •Unprotected land will tend to have higher inputs of pesticides, herbicides, fertilisers ... Clear benefits of PA’s: generation of higher quality water than non- protected areas
  • 4. Quality determines quantity 1. Water quality = water availability (for a purpose) 2. Quantity and access can be high but if quality is not sufficient then water scarcity can still exist 3. Countries like Colombia have a lot of water but to what extent is it all usable without expensive water treatment?
  • 5. Q. How can we understand the impact of human activity on water quality when water quality cannot be assessed from remote sensing? A1. identify the proportion of your water originating in upstream protected areas A2. Identify the point and non point sources and calculate the ‘upstream human influence’ on river water
  • 6. Protected areas : nature’s water filter •12-14% of the terrestrial surface is nominally protected •34% of ice free areas are used for agriculture and grazing •The rest is ice, desert,urban or unprotected wilderness •Mean management budget: $8.75 per km2* 1872 *estimated on the basis of James, A.N., Green, M.J.B. and Paine, J.R. 1999. A Global Review of Protected Area Budgets and Staffing. WCMC – World Conservation Press, Cambridge, UK. vi + 46pp
  • 7. Quantifying the hydrological value of global protected areas Protected areas may help with water quantity and regulation functions and certainly help with water quality functions. Protected areas provide a ‘purification function’ on the basis that they tend to have lower human influence on water. Assumption: Water draining from a protected area is better (higher quality, better regulated) than water that drains from non-protected areas Method 1. Combine global rainfall dataset (1km resolution) with global dataset of flow directions (Hydro1k, HydroSheds) 2. Route rainfall down the flow network 3. For each pixel downstream calculate the proportion of runoff in that pixel derived from protected areas upstream 4. Combine with population and urban areas datasets (CIESIN) and calculate the number of persons benefitting from runoff originating in protected areas 5. Put online in Google maps/Earth : see http://www.kcl.ac.uk/geodata 6. Repeat for other ‘contributing’ areas (forests, mountain forests, non-protected but non- agricultural areas etc.)
  • 8. % of water originating in a protected area – WDPA 2009 (Colombia) [gl_pc_wc_fin] Protected areas provide a ‘purification function’ on the basis that they tend to have lower human influence on water. As you travel downstream from the protected areas their contribution to flow diminishes as rivers are swamped with water from non-protected areas see www.kcl.ac.uk/geodata
  • 9. Modelling the human footprint on water 0.1*Pr 1.0*Pm P non-human-influenced Frac*Pa Frac*Pg 1.0*Pog 1.0*Pu P non-human-influenced Frac*Pc Human Footprint on Water=∑Ppolluting /∑Ptotal
  • 10. Roads Mines Point sources Urban areas Oil and gas
  • 11. Pasture Cropland Non-point sources + Protected areas Unprotected agriculture - =
  • 12. % of water that is human impacted At the global scale dominated by the human agricultural footprint
  • 13. % of water that is human impacted At the continental scale the influence of roads and protected areas becomes more obvious
  • 14. % of water that is human impacted At the national scale the downstream decay of influence away from agricultural and urban areas is clearer. We might expect the human influence to be reflected in higher sediment loads, organic and inorganic contaminants, incl. pesticides and fertiliser etc. This decay results from the dilution of human influenced water with runoff from less influenced areas.
  • 15. % of water that is human impacted At the regional scale the distance decay is clear with some rivers still being 25% influenced by upstream polluting activities some 150 km downstream. The extent of the influence depends on the area of the polluting activity (though in reality the intensity of pollution will also be important. Protected areas ‘purify’ through dilution Oil wells may have a locally intense influence but it is soon diluted and fades quickly Takes no account of exposure levels : a measure of influence not of toxicity
  • 16. % of water that is human impacted (transparent=negligible influence) The human footprint on water is concentrated around human populations (roads, agric, industry, urban tend to coalesce). Thus around major cities water quality could be heavily influenced Strategic positioning of protected areas can have positive impacts on the water supply of urban areas
  • 17. % of water supply to urban areas that is human impacted At the local scale supply to urban areas is influenced by water diversions, aqueducts, transfers etc. for which there are no data globally. But, if we assume that rivers running into urban areas supply those areas with water then we can map the heavily impacted urbanisations Many of these cities will use intensive water treatment to offset these impacts
  • 18. % of water supply to urban areas that is human impacted Although Colombia has a lot of water it also has high population, large urbanisation and intensive agriculture in the Andes. Colombia’s urban water supplies are thus heavily influenced by upstream human activity This necessitates costly diversion schemes or water treatment. Putting a natural PA buffer between populations and the mess they create can deliver clear water quality benefits at low cost.
  • 20.
  • 21. % of water supply to urban areas that is human impacted
  • 22. Methods 1. Map global distribution of threat factors (1km spatial resolution GIS database) for point and non point sources 2. Integrate global maps of water inputs i.e. Rainfall (from WorldClim and TRMM) 3. Integrate global maps of flow directions (Hydro1k, Hydrosheds) 4. Calculate influence of each upstream point and non-point source as : Area of point source polluting activities+ = (mines + oilandgas + roads++*0.1 + urban) Area of unprotected agricultural land+ = (pasture + cropland) * (1-protected) Total polluting area per pixel (P) = max (1.0, point source polluting activities, unprotected agricultural land) These were summed downstream along the flow network top give Pd The rainfall (Rf) falling on all areas was also calculated and summed downstream to give Rfd. Human influence (%) = (Pd/Rfd) * 100 (the percentage of flow in a given pixel that fell as rain on an upstream human influenced area: a measure of the potential upstream influences on water quality). +Mines= mine according to Hearn et al. (2003), Oilandgas = oil and gas field according to Hearn et al. (2003) (binary), Roads = roads (binary), Urban = urban area according to CIESIN et al. (2004) (binary), Pasture = pasture land according to Ramankutty et al. (2008), Cropland = cropland according to Ramankutty et al. (2008), Protected= nationally or internationally protected areas according to WDPA (2009) (binary). ++ roads , if present, are assumed to occupy 10% of the pixel area