Desalination is the process of removing dissolved salts from water.
(200) This process is able to produce drinking water from seawater and
brackish groundwater. (201) Two fundamental processes make desalination
possible: thermal and membrane. (202) The thermal process involves
heating salt water in order to produce a vapor that can then be
distilled to produce fresh water. (203) The membrane process, on the
other hand, uses actual membranes to separate the salts from freshwater.
(204) This membrane involves using one of two methods: electrodialysis
or reverse osmosis. (205) One argument proffers that desalination is one
of the very few options available for areas like the Middle East. (206)
Over time, "[d]esalination technologies have advanced rapidly in
the last decades, bringing down costs and mitigating environmental
consequences." (207) In fact, "[p]ublic private partnerships
have evolved as a means to harvest the creativity and entrepreneurship
of the private sector in partnership with public owners to integrate
finance, planning, design, construction, operations and maintenance, and
ownership in the delivery of complex projects." (208) In order to
effectively combat water shortages in both areas, Texas and the Middle
East should both expand their desalination efforts. When discussing the
expansion of the desalination effort as a possible solution to the water
shortage problem, one must consider costs and the environmental
ramifications. (209)
Often, consideration of the cost of a desalination facility focuses
on the amount of fresh water the facility produces. (210) Typically, the
measure of cost is put in terms of dollars per thousand gallons. (211)
The range of costs "[depend] not only on the costs of desalination
facilities, but on the cost of conveyance facilities and environmental
mitigation." (212) With improvements in technology, newer
desalination facilities as well as the more expensive reverse osmosis
facilities have been able to lower costs. (213)
Turning now toward the issue of environmental ramifications, the
biggest existing concern is the disposal of the briny residue that
remains after the desalination process. (214) For facilities in coastal
areas that use sea water as the material source for desalination, the
disposing of this briny residue back into the sea is a generally
accepted method of disposal. (215) The same, however, is not true for
inland desalination facilities. (216) In these situations, the inland
facilities have the burden of transporting briny residue to the nearest
seawater point or injection well. (217) In both instances, "[b]rine
disposal issues often add substantial cost to desalination
facilities...." (218) When compared to the high demand and need for
water, this cost is arguably nominal in comparison.
As the issues surrounding the longevity of water supplies increase,
water rights will need to be more clearly defined. According to the
World Water Council, the implicit right to water has not been put into
practice due to the lack of political will and the confusion over a
concrete definition of water rights. (219) An argument has been raised
"that even with major improvements in water collection and
distribution (that would provide 70 percent efficiency instead of the
current average of 45 percent worldwide), there would still be a need
for 20 percent more water, a prediction that has been termed the
'world water gap.'" (220) Unfortunately, because a number
of the available sources have already been appropriated, there are
limitations on how much additional water can be extracted from the
environment. (221)
IV. CONCLUSION
The problem is simply stated: Water resources are limited while
demand is ever growing. In order to battle this harsh truth, both Texas
and the Middle East must shift gears into a new mindset when addressing
their water regulation systems. This would include clearly defining
rights to water, increasing cooperation among neighbors, and looking to
new ways of regulating water, such as setting a reasonable use standard,
privatizing the water sector, and focusing on the development of
technologies such as desalination. (222) By formulating a clear
definition of water rights, countries will be better able to understand
the boundaries within which they are to act. Increasing cooperation
among neighbors will be the most challenging aspect of reform for both
the Texas and Middle Eastern water regulation systems. For both areas,
there is a long history that contributes to the current views of rights
to water held among neighbors.
Finally, by looking to new ways of increasing the water supply,
both Texas and the Middle East will allow for a greater likelihood of
sustaining the maximum availability of water. This will, however,
require that both areas contribute time, energy, and resources to the
continual development of access to fresh water. After looking at the
background of both Texas and Middle Eastern water regulation and the
conflicts that exist internally in both areas, it is clear that both can
benefit from the above mentioned solutions.
Although no one solution alone will suffice, in the aggregate, they
will lead to a more constant supply of water. As with any solution or
plan, the true benefit is not realized until it is implemented and given
time to take effect. The only thing that is definite is the current
systems in both Texas and the Middle East is not sufficient to sustain
the needed level of water.
(1.) See Noah Arre, Safe Water is Safe Life! How Safe Are Somalis
in Water? (2001), http://www.watermagazine.com/secure/ jc/somali.rtf
(paper presented at the Eighth Congress of Somali Studies)
("Tensions over water permeate every region of the world, ranging
from clashes between urban and agricultural water users to out right
(sic) warfare in the Middle East.").
(2.) Harry Grant Potter, III, History and Evolution of the Rule of
Capture, in 100 YEARS OF RULE OF CAPTURE: FROM EAST TO GROUNDWATER
MANAGEMENT, TEXAS WATER DEVELOPMENT BOARD REPORT 361, 1 (William F.
Mullican, III & Suzanne Schwartz eds., 2004), available at
http://www.twdb.state.tx.us/publications/reports/GroundWater
Reports/GWReports/Report%20361/1%20CH%20Potter.pdf.
(3.) 81 S.W. 279, 280 (Tex. 1904).
(4.) Id.
(5.) Id. (quoting Acton v. Bundell, 152 Eng. Rep. 1223 (Ex. Ch.
1843)) ('That doctrine is thus stated: 'That the person who
owns the surface may dig therein and apply all that is there found to
his own purposes, at his free will and pleasure; and that if, in the
exercise of such right, he intercepts or drains off the water collected
from the underground springs in his neighbor's well, this
inconvenience to his neighbor falls within the description of damnum
absque injuria, which cannot become the ground of an
action.'").
(6.) Id. at 280-81; Frazier v. Brown, 12 Ohio St. 294, 311 (Ohio
1861), overruled by Cline v. American Aggregates Corp., 474 N.E.2d 324
(Ohio 1984).
(7.) East, 81 S.W. at 280.
(8.) Frazier, 12 Ohio St. at 311.
(9.) See East, 81 S.W. at 280-81.
(10.) 296 S.W. 273, 277 (Tex. 1927) ("Again, where there is
but one riparian owner, ... he may grant all of the riparian rights to
the use of the waters of such stream, even if by that use it is all
consumed by the grantee. This is for the reason that the grantor had
dominion and ownership of it. It was his property, and he could dispose
of it as he saw fit.").
(11.) Id. at 275-76.
(12.) Id. at 276.
(13.) Id. at 278.
(14.) Eric Opiela, Commentary, The Rule of Capture in Texas: An
Outdated Principle Beyond its Time, 6 U. DENV. WATER L. REV. 87, 96
(2002).
(15.) Todd H. Votteler, The Little Fish that Roared: The Endangered
Species Act, State Groundwater Law, and Private Property Rights Collide
Over the Texas Edwards Aquifer, 28 ENVTL. L. 845, 874-75 (1998)
(discussing the fundamental characteristics of property rights serving
as part of the bundle of entitlements involving the rights, privileges,
and limitations for use of a resource of the owner).
(16.) Id. (noting that an efficient property rights system has the
following characteristics: "1) universality--all resources are
privately owned, and all entitlements completely specified; 2)
exclusivity--all benefits and costs accrued as a result of owning and
using the resources should accrue to the owner, and only to the owner,
either directly or indirectly by sale to others; 3) transferability--all
property rights should be transferable from one owner to another in a
voluntary exchange; 4) enforceability--property rights should be secure
from involuntary seizure or encroachment by others").
(17.) Opiela, supra note 14, at 97.
(18.) Id.; see also Act of June 2, 1949, ch. 306, [subsection] 1,
3c(D), 1949 Tex. Gen. Laws 559, 562.
(19.) C. Richard Bath, A Commentary on Texas Water Law and Policy,
39 NAT. RESOURCES J. 121, 122 (1999).
(20.) Id.
(21.) Id.
(22.) Id.
(23.) Cynthia DeLaughter, Comment, Priming the Water Industry Pump,
37 HOUS. L. REV. 1465, 1477 (2000).
(24.) See Bath, supra note 19, at 122.
(25.) Id.
(26.) See John R. Pitts & Janet L. Hamilton, Texas Water Law
for the New Millennium, 14 NAT. RESOURCES & ENV'T 35, 35
(1999); see also Act of Sept. 1, 1997, ch. 1010, [section] 1.01, 1997
Tex. Gen. Laws 3610, 3610 (codified as amended at TEX. WATER CODE ANN.
[section] 16.05).
(27.) See DeLaughter, supra note 23, at 1479 (citation omitted).
(28.) Id. at 1478-79.
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