an extensIve analysIs and evaluation of options for assuring adequate water
supplies in the Colorado River Basin was published in 2012 by the Bureau of
Reclamation, and we summarize it here. [Colorado
River Basin Water Supply and Demand Study, Executive Summary, Bureau of
Reclamation, U.S. Department of the Interior, Washington, DC, December 2012]
The report makes the
following warning: “The Colorado River is the lifeblood of the southwestern
United States….Nearly 40 million Americans rely on the Colorado River….there exists a strong potential for
significant imbalances between the supply and demand for water in the coming
decades.”
From 1906-2011, the
Colorado River had average natural flow of 16.4 maf/year. The Study was done to
predict imbalances for the next 50 years, 2010-2060. The Study area was the
hydrologic basin area plus adjoining states that receive water from the
Colorado.
Four water-supply
scenarios and six water-demand scenarios were studied to try to predict the
future needs.
WATER SUPPLY SCENARIOS
•
Observed Resampled (past 100 years).
•
Paleo Resampled (past 1250 years)
•
Paleo Conditioned (mix of Observed and Paleo)
•
Downscaled GCM (warming climate from 112 Global
Climate Models), which predicts a nine percent decrease in flow at Lees Ferry
and higher-than-historical frequency and variation in droughts, which are
predicted to have lengths of five years or more 50% of the time in the upcoming
50 years.
WATER DEMAND SCENARIOS
To get a good
depiction of future consumptive use demand, a set of six scenarios was
developed:
•
A. Current Projected
•
B. Slow Growth (18.1 maf, 49.3 million people)
•
C1. Rapid Growth 1 (20.4 maf, 76.5 million people)
•
C2. Rapid Growth 2
•
D1. Enhanced Environment 1 • D2. Enhanced Environment 2
Comparing the medians from the supply and demand scenarios, the likely
imbalance by 2060 is 3.2 maf, with a wide range of uncertainty. Some of
this can be met with reservoir storage to smooth out variability. By 2010, the
ten-year running average of demand had already exceeded the ten-year running
average of supply, and the trends were for this difference to increase.
OPTIONS AND STRATEGIES
•
Increase Supply
•
Reduce Demand
•
Modify Operations
•
Modify Governance
The criteria used to evaluate the options
were
•
Technical (feasibility, risks, viability,
flexibility)
•
Social (recreation, policy, legal,
socioeconomics)
•
Environmental (permitting, energy needs, energy
sources, other environmental factors)
•
Other (yield quantity, timing, cost, hydropower,
water quality)
Where possible they
were evaluated based on cost, $/maf, year available, and potential yields
(2035, 2060).
Adding all options
gave additional yearly flow of 5.7 maf by 2035 and 11 maf by 2060. Ruling out
some options considered infeasible gave additional flow estimates of 3.7 and 7
maf for 2035 and 2060.
Four portfolios of options were then
chosen: B, C, inclusive A=B+C, and selective D = options
shared by both B and C.
EVALUATION OF OPTIONS
Criteria came from analyzing:
•
Water delivery
•
Water quality
•
Recreational use
•
Power
•
Flood control
•
Ecological resources
Reliability was
measured against keeping Lake Mead at 1000 ft above mean sea level and keeping
the 10-year flow at Lees Ferry at 75 maf. Conclusion:
without action, it will be difficult to meet these goals using the Baseline
arrangements for the next 50 years.
Over 20,000
simulations were run for each portfolio.
Study Table 4 shows
the % of years in which the criteria were not met when analyzed using the
Baseline model and Models A,B,C,D. For all criteria except flood control, the Baseline model performed worst of the options.
Of the resource criteria, Baseline failed most often at keeping Lake Mead at
1000 feet above msl. By that criterion, all portfolios and the Baseline option
failed 30% or more of the instances, and they failed almost as often at keeping
the Colorado River flow above the targeted value. As expected logically, the inclusive Portfolio A did the best and the
exclusive Portfolio D the worst at meeting the criteria.
Study Figure 4 Shows
the various options and their cost estimates and the percentage of the
2010-2060 years in which the system is vulnerable. There are wide ranges of vulnerabilities, and the costs vary as well,
but are limited to about $2 billion to $7 billion per year.
The report does not
choose the best option, leaving that to others.
STUDY LIMITATIONS
The authors note that
the study is limited by available data, assessment methods, current models:
The Colorado River
Simulation System (CRSS) was used to model behavior and assess impacts.
The CRSS uses
historical inflows based on USGS data for four tributaries downstream of Lees
Ferry, making the Lower Basin predictions subject to substantial uncertainty.
The model assumed
reduced agricultural use, as such flows will be diverted to urban use instead.
This may not be correct.
A limited set of
options was considered, and future developments and technological change may
make other options important.
FUTURE CONSIDERATIONS AND NEXT STEPS
Improved modeling of
future supply and demand will continue. Demand can be assumed to increase,
making shortages more likely, and no one option is likely to be optimal.
Investment in conservation, reuse, and augmentation will be needed to improve
reliability and sustainability.
DISCLAIMER
Nothing
in the Study is to be used as part of any litigation in a variety of possible
actions outlined in this Disclaimer.
Note that although
governmental command-and-control activities might seem adequate to handle the
need for clean drinking water in the future, there are practical political and
economic factors that get in the way, as pointed out in a recent article in The City Journal:
In 2014, amid a
drought, 2/3 of California voters voted for Proposition 1, to have a bond for
$2.7 billion worth of water storage projects, as part of a larger $7 billion
Water Quality, Supply, and Infrastructure Improvement Act. Four years later, no
funding for water storage had been passed by the state water commission. This
contrasts with the relatively rapid creation of the San Luis Reservoir, with a
capacity of 2 million acre-feet, done five years from 1963-68, facing far fewer
challenges in the courts.
Mid-2018, the
California Water commission announced plans to fund projects with Proposition 1
money, only a third of the projects actually related directly to water storage.
The proposed storage sites will add a capacity of 2 million acre-feet, compared
with the annual residential water use by Californians of 4 million acre-feet
per year. The Sites Reservoir, the largest of the projects, is expected to be
completed by 2029, at a cost of about ten times the cost of the comparable San
Luis Reservoir finished in the mid-1960s in one-fourth the time. Litigation is
a major factor in the added costs and time for completion. [https://
www.city-journal.org/html/still-parched-15960.html]
SOME EQUITY ISSUES
Sharing the use of
water resources raises many possible equity issues, some of which we discuss
next. Essentially, these come down to who uses how much of the resources and how.
To make progress in analysis of policy options, the problem needs to be stated
clearly, and its boundaries marked (Hardin, 1968). We start with the simpler
cases and build from there.
A single body of water, such as a lake or
inland sea, has inlets and outlets, with users around its shores and on its
surface. Like a common grazing area of earlier times, it is susceptible to the
“tragedy of the commons,” where each user benefits more directly from using
than from contributing to its well-being, its maintenance. Biologist Garrett
Hardin (1968) popularized the term and showed that for finite resources we
cannot obtain “the greatest good for the greatest number.” Each user is tempted
to use as much as wanted and to contribute nothing. A solution is to obtain enforceable
agreements among all involved or to have rules enforced by a governing body.
Then, one must be able to verify what is being done. A lake may be in one
governmental jurisdiction, allowing simplified enforcement of one set of laws.
A larger body of water may have multiple governing authorities, requiring
agreements among them on rules of use and manner of enforcement. If the body of
water can overflow its banks, then issues of compensation for damages are
added.
The lake will likely
have inlets and outlets, and the control of these flows adds another dimension
to the complexity. What is done upstream is of particular concern, and likely
needs agreements, laws, and policing.
Similarly, a river has upstream and downstream regions,
with upstream behavior affecting the flow and its quality in the downstream
areas. Again, agreements or laws and enforcement will seem desirable.
In the case of the
“lake” or the “river,” the agreements or laws may have sharp-edge restrictions,
yes/no, or an attempt may be made to put prices on various types and amounts of
“use.” Enforcement again becomes critical.
Monitoring the level
of a lake or inland sea is relatively straightforward in comparison with
determining the carrying capacity and the amount of water carried in an aquifer, which is a region of porous
solids, liquid, and air. Again, there are inputs and outputs and issues of
capacity, volume, flow, and quality.
If these
considerations were not complex enough, we have the added issue of the degree
to which current use and users will impact future use and users and how to
manage the somewhat different concerns of the two populations, complicated
further by the likelihood of technological and demographic changes.
I will continue serializing here the Microsoft Word transcription of the final galley proof .pdf copy ot WATER WARS, and the book itself is most conveniently found at amazon.com https://www.amazon.com/Water-Wars-Sharing-Colorado-River-ebook/dp/B07VGNLSMX/ref=sr_1_1?keywords=water+wars+by+carter+and+cooper&qid=1577030877&sr=8-1
or at DWC's amazon.com author's book title list https://www.amazon.com/s?k=douglas+winslow+cooper&i=digital-text&ref=nb_sb_noss
No comments:
Post a Comment