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Human
Appropriation of the World's Fresh Water Supply |
"Water, water, everywhere, nor any drop to drink"
- Rhyme of the Ancient
Mariner, by Coleridge.
Jump to: [The
Water Resources of Earth] [Consumptive and
Non-Consumptive Water Use] [Human Appropriation
of Renewable Fresh Water ] [What are the Solutions?]
[Water Sustainability, Water Security][References]
The Water Resources of Earth
Over 70% of our Earth's surface is covered
by water ( we should really call our planet "Ocean" instead of "Earth").
Although water is seemingly abundant, the real issue is the amount of fresh
water available.
- 97.5% of all water on Earth is salt
water, leaving only 2.5% as fresh water
- Nearly 70% of that fresh water is
frozen in the icecaps of Antarctica
and Greenland; most of
the remainder is present as soil moisture, or lies in deep underground
aquifers as groundwater not accessible to human use.
- < 1% of the world's fresh water
(~0.007% of all water on earth) is accessible for direct human uses. This
is the water found in lakes, rivers, reservoirs and those underground
sources that are shallow enough to be tapped at an affordable cost. Only
this amount is regularly renewed by rain and snowfall, and is therefore
available on a sustainable basis.
Water as a Resource
Since antiquity, irrigation, drainage, and
impoundment
have been the three types of water control having a major impact on
landscapes and water flows. Since the dawn of irrigated agriculture at least
5000 years ago, controlling water to grow crops has been the primary
motivation for human alteration of freshwater supplies. Today, principal
demands for fresh water are for
irrigation, household and municipal water use, and
industrial uses. Most supplies come from surface runoff, although mining
of "fossil water" from underground aquifers is an important source in some
areas. The pattern of water withdrawal over the past 300 years shows the
dramatic increases in this century.
A timeline of human water use:
- 12,000 yrs. ago: hunter-gatherers
continually return to fertile river valleys
- 7,000 yrs. ago: water shortages spur
humans to invent irrigation
- 1,100 yrs ago: collapse of Mayan
civilization due to drought
- Mid 1800's: fecal contamination of
surface water causes severe health problems (typhoid, cholera) in some
major North American cities, notably
Chicago
- 1858: "Year of the Great Stink" in
London, due to sewage and wastes in Thames
- Late 1800s-early 1900: Dams became
popular as a water management tool
- 1900s: The green revolution strengthens
human dependency on irrigation for agriculture
- World War II: water quality impacted by
industrial and agricultural chemicals
- 1972:
Clean Water Act
passed; humans recognize need to protect water
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Figure 1: The water usage of
different regions of the world per capita in cubic meters.
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Consumptive and Non-Consumptive Water Use
Consumptive water use refers to water that
is not returned to streams after use. For the most part, this is water that
enters the atmospheric pool of water via evaporation (from reservoirs in
arid areas) and from plant transpiration (especially from "thirsty" crops
such as cotton and alfalfa). Irrigated agriculture is responsible for most
consumptive water use, and decreases surface run-off. An extreme example is
the Colorado River, which has
most of its water diverted to irrigated agriculture, so that in a normal
year, no water at all reaches the river’s mouth.
Agriculture is responsible for 87 % of the
total water used globally. In Asia it accounts for 86% of total annual water
withdrawal, compared with 49% in North and Central America and 38% in
Europe. Rice growing, in particular, is a heavy consumer of water: it takes
some 5000 liters of water to produce 1 kg of rice. Compared with other
crops, rice production is less efficient in the way it uses water. Wheat,
for example, consumes 4000 m3/ha, while rice consumes 7650 m3/ha.
A great deal of water use is
non-consumptive, which means that the water is returned to surface runoff.
Usually that water is contaminated however, whether used for agriculture,
domestic consumption, or industry. The WHO estimates that more than 5
million people die each year from diseases caused by unsafe drinking water,
and lack of sanitation and water for hygiene. This has economic effects as
well: an outbreak of cholera in Latin America killed hundreds of people, and
cost hundreds of millions of dollars.
Some believe that fresh water will be a
critical limiting resource for many regions in the near future. About
one-third of the world's population lives in countries that are experiencing
water stress. In Asia, where water has always been regarded as an abundant
resource, per capita availability declined by 40-60% between 1955 and 1990.
Projections suggest that most Asian countries will have severe water
problems by the year 2025. Most of Africa historically has been water-poor.
What's the problem?:
- The population is growing rapidly,
putting more pressure on our water supply (demand is increasing)
- The amount of water is effectively
reduced by pollution and contamination (supply is decreasing)
- What does the future hold? We can best
explore this question by looking carefully at the world's water
resources.
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Figure 2: This picture depicts the
global hydrological cycle adapted from Gleick. Flows are approximate
estimates and are in cubic kilometers per year. |
Human Appropriation of Renewable Fresh Water
The hydrological cycle:
- The water cycle on Earth is essentially
a closed system – we always have the same amount of water.
- You can review the
hydrologic cycle from a lecture in Global Change I. View diagrammatic
and simplified water cycle (see figure 2).
- The only parts of this cycle
appropriated by humans is water held as surface water or shallow aquifers.
Let us try to quantify present use.
Available renewable fresh water:
- Fossil ground water can be tapped but
is non-replenishable.
- Terrestrial replenishable fw supply
(RFWS land).
- RFWSland = ppte on land.
- Pland = evapotranspiration
from the land (ETland) and runoff to sea (R).
- Estimates of annual runoff range from
33,500 to 47, 000 km3 (Postel uses 40,000 km3).
Because it is difficult to separate
evaporation from transpiration, they are combined as evapotranspiration.
Evapotranspiration represents the water supply for all non-irrigated
vegetation, both natural and crops.
Runoff is the source for all human
diversions or withdrawals for irrigation, industry, municipal uses,
navigation, dilution, hydropower, and maintenance of aquatic life including
fisheries.
ET Estimates Appropriated
for Human Dominated Land Uses. |
Land Type
|
NPP
co-opted
(x 10^9 metric tons)
|
ET
co-opted*
(km ^3)
|
Cultivated land
|
15.0 |
5,500 ** |
Grazing land
|
11.6 |
5,800 |
Forest land
|
13.6 |
6,800 |
Human occupied areas
(lawns, parks, etc.) |
0.4 |
100** |
Total
appropriated |
40.6 |
18,200 |
Table 1: A total of
26.2% of terrestrial ET is appropriated (18,200 cubic km/69,600 cubic
km). * Assumes 2 g of biomass produced for each liter of water
evapotranspired. ** Adjusts for share of ET requirement me through
irrigation. |
Human
appropriation of evapotranspiration
Vitousek et al. (1986) estimated the
human co-option of terrestrial NPP at 40.6 billion metric tons, or more
than 30% of terrestrial NPP. This includes cropland, grazing land, and
trees harvested for fuelwood and timber. You can review
Net Primary Production (NPP) from a lecture in Global Change I.
The volume of ET required to produce a
unit of biomass =total terrestrial NPP (132 billion metric tons) divided
by terrestrial ET (70,00 km3) = 1.9 kg of biomass per ton of
ET.
The final estimate of appropriated ET
is downward corrected for irrigation (approx. 16% of world’s cropland is
irrigated ) and a rough estimate of irrigation of lawns, parks, and
human-occupied areas.
Some 18,200 km3 (26%) of
total terrestrial ET is appropriated for human use (see table 1). The
remaining 74% must meet the needs of remaining terrestrial ecosystems. |
Continental Breakdown of
Share of Global Runoff and Population |
Region
|
Total river runoff
(%)
|
Share of global river
runoff
(%)
|
Share of global
population
(%)
|
Europe |
3,240 |
8.0 |
13.0 |
Asia |
14,550 |
35.8 |
60.5 |
Africa |
4,320 |
10.6 |
12.5 |
N & C
America |
6,200 |
15.2 |
8.0 |
S America |
10,420 |
25.6 |
5.5 |
Australia& Oceania |
1,970 |
4.8 |
0.5 |
Totals |
40,700 |
100.0 |
100.0 |
Table 2
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Human appropriation of runoff
Distribution of global runoff is highly
uneven and corresponds poorly to the distribution of the world population
(see table 2). Asia has 69% of world population but 36% of global runoff.
South America has 5% of world population, 25% of runoff.
Much of runoff is inaccessible. Amazon
River accounts for 15% of runoff and is currently accessible to 25 million
people (0.4% of world’s pop). Estimate it to be 95% inaccessible. Zaire
may be 50% inaccessible. The mostly untapped northern rivers have an
average annual flow of 1815 km3/yr, consider 95% to be
inaccessible.
Together, this amounts to 7774 km3
or 19% of total annual runoff, leaving 32,900 km3
geographically accessible. Does not correct for many northern rivers with
large flows relative to their pop sizes.
Temporal availability: about 27% of
global runoff (11,100 km3) is renewable ground water and base
river flow. Remainder is flood water and harder to capture (table 3).
Present storage capacity of large dams totals 5500 km3, of
which 3500 km3 is used to regulate river runoff. Adding
together base flow and surface runoff controlled by dams gives total
stable flow. Correct for spatially inaccessible flows yields and estimate
of available runoff (AR) as 12,500 km3/yr.
Estimates of inaccessible
runoff of selected remote rivers. |
River
basin or region |
Remote
flow
(km cubed/year)
|
Amazon (95% of total flow) |
5,387 |
Zaire-Congo (50% of total) |
5,387 |
Remote undammed northern
rivers (95% of totals) |
North America
|
979 |
Eurasia
|
746 |
Total inaccessible
remote
runoff |
7,774 |
Table 3
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Water Use and Consumption
Estimates on a Global Scale, 1990 |
Sector
|
Use
(km cubed/year)
|
Consumption
(km cubed/year)
|
Agriculture* |
2,880 |
1870 |
Industry |
975 |
90 |
Municipalities |
300 |
50 |
Reservoir losses# |
275 |
275 |
Subtotal |
4,430 |
2,285 |
Instream flow needs |
275 |
275 |
Total as a percent
of AR (12,500 km cubed) |
54% |
18% |
Table 4:
*Assumes average applied water use of 12,000 (m cubed/ha) and
consumption equal to ~65% of withdrawls. #Assumes evaporation loss equal
to 5% of gross reservoir storage capacity. |
What fraction of AR is used by
humanity?
- Withdrawals: agricultural withdrawals =
average water application rate (12,000 m3/ha) x world irrigated
area (240 x 10^6 ha in 1990) = 2880 km3. Assuming 65% is
consumed, 1870 km3.
- Industrial water use is estimated at
975 km3 and roughly 9% (90km3) is consumed.
Remainder is discharged back into environment, often polluted.
- Municipal use is estimated at 300 km3
per year, of which 50 km3 (17%) is consumed.
- Evaporation from reservoirs is
estimated to average 5% of gross storage capacity of reservoirs (5500 km3)
or 275 km3/yr.
- Instream flow needs are estimated from
pollution dilution, assuming that this suffices to meet instream needs. A
common dilution term is 28.3 liters per second per 1000 population. Using
the 1990 population yields a dilution requirement of 4700 km3.
If half of water received adequate treatment, the dilution requirement is
reduced to 2350 km3/hr.
- Combining these estimates (see table 4)
indicate that humans appropriate 54% of AR. Human use of ET (18,200 km3)
plus runoff (6780 km3) constitutes 30% of total accessible RFWS
and 23% of unadjusted RFWS.
How much can AR be increased?
Principal options are to capture and store
more flood runoff or desalinate sea water. Latter is too energy-intensive
for near future.
Worldwide, new dams (> 15 m ht) were
constructed at rate of 885 per year during 1950-80, present rate is
500/yr, and future rate is estimated at 350/yr. Over next 30 years,
assuming size of reservoirs is unchanged, new construction adds 1200 km3
to accessible supply, and raises total AR in 2025 to 13,700 km3/hr.
Assuming average per capita water demand stays unchanged, but adjusting
the pollution dilution for additional population, the total human
appropriation in 2025 would be 9830 km3/yr, or 70% of estimated
AR (compared to current 54%). Clearly we are approaching the limit of
available fresh water supply.
What are the Solutions?
Improvements in the efficiency of water
use (ex: irrigation systems often perform poorly, wasting as much as 60
percent of the total water pumped before it reaches the intended crop).
Efficient management and modern technology
can stretch even scarce water supplies much further. Israel, for example,
supports its population, its growing industrial base, and intensive
irrigation
with less than 500 cubic meters per person per year.
Water is often wasted because it is
underpriced. Direct and indirect subsidies (especially for agricultural use)
are still common in both developed and developing countries. Removing such
subsidies and letting water prices rise can provide incentives for
conservation and for the investments needed to spread more efficient
technologies.
Water Sustainability, Water Security
The six billion people of Planet Earth use
nearly 30% of the world’s total accessible renewal supply of water. By
2025, that value may reach 70%. Yet billions of people lack basic water
services, and millions die each year from water-related diseases. Water is
a basis of international conflict. What is involved in achieving water
sustainability and water security? The following lists some of the criteria
that should help us chart our direction.
- Basic human needs for water should be
fully acknowledged as a top international priority.
- Water-related diseases, including
Guinea worm, diarrhea, onchocerciasis, malaria and typhoid should be
brought under control.
- Agricultural water should be
efficiently used and allocated.
- Basic ecosystem water needs should be
identified and met.
- Serious water-related conflicts should
be resolved through formal negotiations.
Water conservation through better planning,
management, and technologies offers great promise. Fig. 4 shows per capita
water withdrawals in the U.S. from 1900 to 1995. Per capita water
withdrawals began to decline in 1985, despite continued population growth.
More efficient agricultural and industrial water use accounts for this
trend.
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Figure 3. Trends in
freshwater withdrawals, and population, for the United States,
1950-1995. Note that per capita water use peaked in 1985, and has since
declined. Source: USGS Circ. 1200) |
Figure 4 shows the projected global water
withdrawals for the year 2000. Note that estimates made 10, 20 or 30 years
ago substantially over-estimated year 2000 withdrawals. Less water demand
actually materialized, reflecting the considerable improvements in water use
over this time period. Pricing water to its real cost will achieve further
gains. Both graphs provide a basis for cautious optimism.
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Figure 4. Actual
water global withdrawals, 1960-200, and past forecasts of year 2000
water withdrawal. Past estimates have been high, because they failed to
incorporate improved efficiencies in industrial and agricultural water
use. Source: P. Gleick, The World’s Water, 1998 Island Press).
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Figure 5. Global Water
Scarcity Map. Source: World Resources Institute (WRI). |
References
- Postel, S.L., G.C. Daily and P.R.
Ehrlich. 1996. Human appropriation of renewable fresh water. Science
271:785
- Gleick, P. 2000. The World's water.
Island Press.
- Vitousek, P.M., P.R. Ehrlich, A.H.
Ehrlich and P.A. Matson. 1986. Human
appropriation of the products of
photosynthesis. BioScience 36:368-373.
All materials © 2000 by the
University of Michigan. |