Environment Eassy
5 APRIL 2013 VOL 340 SCIENCE www.sciencemag.org 32
POLICYFORUM
A 1930s f ilm shows a dog running
and jumping inside a fenced enclo-
sure ( 1)—except that the dog has
a strange-shaped head, odd stripes, and a
rigid tail that can only move side-to-side.
The “dog” is actually one of the last thyla-
cines, a marsupial predator also called the
Tasmanian tiger. The fi lm was taken shortly
before humans extinguished the species for-
ever. Or did we? Recently, new technolo-
gies have made it plausible to try to revive
many recently extinct species. Scientists
around the world are discussing, and work-
ing toward, “de-extinction” ( 2).
Currently, three approaches to de-extinc-
tion seem most likely to succeed: back-
breeding, cloning, and genetic engineer-
ing. If the extinct species left closely related
descendants, it might be possible to use
selective breeding to produce progeny with
the phenotypes of the extinct species, as the
auroch project in Europe has been doing
since 2008 ( 3). With newly cheap genome
sequencing methods, one might guide back-
breeding with genome sequences from sam-
ples of the extinct species. Of course, back-
breeding will only be possible in situations
where the genetic variations of the extinct
species survive in the descendant species.
Cloning provides another possibility.
Using cryopreserved tissue from the last
known Pyrenean ibex, a Spanish group
used somatic cell nuclear transfer (SCNT)
to revive that extinct subspecies. Out of
several hundred efforts, however, only one
fetus survived to term, and it died minutes
after birth from lung abnormalities ( 4).
This example highlights two problems with
SCNT: it is neither very safe nor effi cient
and will only work if viable cell nuclei are
available. This will likely be the case in only
a few very recent extinctions.
Genetic engineering offers a third
approach. Take an extinct species—say,
the passenger pigeon—that left suffi cient
samples to allow high-quality whole-
genome sequencing. DNA in cells from a
similar living species—perhaps the band-
tailed pigeon—could be edited to match
the extinct species’ genomic sequence. The
modifi ed cells could then be used to produce
living birds that, genomically, were mainly
band-tailed pigeon but partially passenger
pigeon ( 5). By using targeted replacement
of genomic sequence ( 6) across several loci,
much of the extinct genome could be recon-
structed within several generations.
Neither the back-breeding nor genetic
engineering approaches would yield an ani-
mal that had exactly the same genome as
any member of the extinct species for many
years, if ever. The cloning approach, in the
few cases where viable nuclei are avail-
able, would produce a genomic twin to one
member of the extinct species—but only
one. Does one individual (or a set of clones)
make a “species”? Even if genomic iden-
tity is necessary, is it suffi cient? The revived
individuals would not have the same epigen-
etic makeup, microbiome, environment, or
even “culture” as their extinct predecessors.
Risks and Objections
Objections to bringing back extinct animals
fall into f ive categories: animal welfare,
health, environment, political, and moral.
Animals created in the de-extinction
process could end up suffering, either as
a result of the processes used or because
of their particular genomic variations. We
know, for example, that SCNT can lead to
high levels of deformity and early death
( 7). The Animal Welfare Act and its institu-
tional animal care and use committees limit
precisely this kind of suffering ( 8). Beyond
physical suffering, some animal advocates
might oppose de-extinction as they oppose
zoos—on the grounds that they exploit ani-
mals for unimportant human purposes, like
entertainment.
Newly de-extinct creatures might prove
excellent vectors for pathogens. An extinct
animal’s genome could also conceivably
harbor unrecognized, harmful endogenous
retroviruses.
If the species either is released or escapes
into the general environment, it might do
substantial damage. Even extinct species
that were not pests in their past environ-
ments could be today. For example, less than
200 years ago, billions of passenger pigeons
migrated each year between the eastern
United States and Canada. Today, those
regions have far more humans, far larger
urban centers, very different agriculture,
and largely transformed ecosystems. The
American chestnut, a main food source for
the passenger pigeon, is now nearly extinct
in the wild. Even in the same location, the
passenger pigeon would today be an alien,
and potentially invasive, species—perhaps
another starling or even an avian kudzu.
The political risks are considerable,
What If Extinction Is Not Forever?
GENOMICS
Jacob S. Sherkow 1 and Henry T. Greely 2
Although new technologies may make it
possible to bring extinct species back to life,
there are ethical, legal, and social ramifi cations
to be addressed
Tasmanian tiger. By the 1930s, settlers, encouraged by government bounties, had hunted the thylacine to
extinction in the wild. Well-preserved specimens could pave a way to bringing it back.
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*Corresponding author. hgreely@stanford.edu
1Center for Law and the Biosciences, Stanford Law School, Stanford CA 94305, USA. 2Stanford University, Stanford CA 94305, USA.
Published by AAAS
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www.sciencemag.org SCIENCE VOL 340 5 APRIL 2013 33
POLICYFORUM
too. Current protection of endangered and
threatened species owes much to the argu-
ment of irreversibility. If extinctions—par-
ticularly extinctions where tissue samples
are readily available—are not forever, pres-
ervation of today’s species may not seem as
important. Also, genetics and, more broadly,
modern bioscience, could face a backlash
if citizens perceive public investments in
bioscience as being used to revive species
rather than cure human disease.
Finally, some people will complain that,
whatever its consequences, de-extinction is
just wrong—it is “playing god,” “reversing
natural selection,” or an act of hubris. Oth-
ers may argue that we cannot know enough
about the consequences to re-introduce a
species. But neither do we know the full
consequences of its extinction or its con-
tinuing nonexistence.
Benefi ts
Like the risks or objections to de-extinc-
tion, we see the benefi ts falling into fi ve cat-
egories: scientifi c knowledge, technological
advancement, concrete environmental ben-
efi ts, justice, and “wonder.” These benefi ts
are quite similar to the arguments made for
preserving currently endangered or threat-
ened species.
De-extinction could allow scientists the
unique opportunity to study living members
of previously extinct species (or, at least,
close approximations to those species), pro-
viding insights into their functioning and
evolution. Some revived species may be
translated into useful products; for exam-
ple, it is conceivable that new drugs may be
derived from extinct plants.
De-extinction could lead to techno-
logical advances. The most likely would
be improvements in genetic engineering,
such as the targeted replacement of large
stretches of genomic DNA ( 6).
Some researchers argue that “re-wild-
ing” with existing species, locally extinct in
particular habitats, can help restore extinct
or threatened ecosystems ( 9). The same can
be argued about the restoration of extinct
species. The revival of the wooly mammoth
as a major grazing animal in the Arctic, for
example, might provide substantial ben-
efi ts by helping restore an arctic steppe in
the place of the less ecologically rich tun-
dra ( 10).
Justice is a viscerally attractive argu-
ment for de-extinction, at least for species
that humans drove to extinction: We killed
them. We have the power to revive them. We
have a duty to do so. But to whom or what
do we owe that duty? Would it apply to all
species in whose extinction humans played
the sole, the leading, or a substantial role?
The last benefi t might be called “wonder,”
or, more colloquially “coolness.” This may be
the biggest attraction, and possibly the big-
gest benefi t, of de-extinction. It would surely
be very cool to see a living wooly mammoth.
And while this is rarely viewed as a substan-
tial benef it, much of what we do as indi-
viduals—even many aspects of science—
we do because it’s “cool.”
Legal Issues
We may also need to consider several legal
issues. First, would a de-extinct species be
“endangered”? The answer is unclear. In the
United States, the Endangered Species Act
provides for listing as “endangered” any
species “over utilized” for scientifi c pur-
poses, inadequately protected by current
regulations, or whose existence is threat-
ened by other “manmade factors” ( 11)—all
considerations that would seem to apply to
a newly revived species. Ironically, inter-
national organizations typically tie endan-
gered status to whether species’ population
has declined—the opposite of the concern
about newly revived species ( 12). Uncer-
tainty about the status of de-extinct species
will affect numerous civil, criminal, and
international laws.
Second, could a revived species be pat-
ented? This answer also seems unclear.
The United States and many other coun-
tries allow patents on living organisms ( 13).
Although “products of nature” cannot be
patented, is a revived species a “product
of nature” in light of the inevitable differ-
ences from its predecessors? Additionally,
the “lost arts doctrine” may allow the pat-
enting of previously existing species if they
have been completely lost to the public ( 14).
Last, would de-extinction be regulated
and if so, how? Again, the answer is unclear.
And even if there were no legal regulation,
the concerns previously discussed could
dampen the enthusiasm for de-extinction by
some research entities, such as universities.
This could drive the efforts toward less con-
trolled, or constrained, enterprises.
What Should Be Done?
The answer to the question—What to do
about de-extinction?—depends in part on
closely def ining the question. Consider
three different “bottom-line” questions.
First, should de-extinction be publicly
funded? This answer seems, to us, “largely
no.” The potential tangible benef its from
de-extinction are too small and the poten-
tial objections are too serious to justify sub-
stantial government expenditure. One might
argue that governments fund science proj-
ects with similarly small practical relevance,
but those “cool” projects, like the Mars rov-
ers, present fewer risks and objections.
Second, should de-extinction be cate-
gorically banned? Here the answer seems a
fairly clear “no.” The risks look fairly small
and probably manageable. If people want to
devote their own time, money, and efforts to
the endeavor, the risks to the world do not
seem to justify complete prohibition.
Third, should de-extinction be regu-
lated? Here, we think the answer is “Yes—
somewhat.” The animal welfare and envi-
ronmental concerns are real. They could be
mitigated by protective action but only if
the law requires it. Bringing all de-extinc-
tion efforts under something like the Ani-
mal Welfare Act and requiring careful envi-
ronmental assessments before any planned
releases (as well as approved precautions
against inadvertent release) do seem appro-
priate. Whether other kinds of regulation
are needed is less clear, although there may
be some cases, like any attempted revival of
extinct hominid species, where special con-
trols, or bans, would be appropriate.
De-extinction is a particularly intrigu-
ing application of our increasing control
over life. We think it will happen. The most
interesting and important question is how
humanity will deal with it.
References and Notes 1. Last Tasmanian tiger, thylacine (1933);
www.youtube.com/watch?v=6vqCCI1ZF7o.
2. C. Zimmer, Natl. Geogr. (2013); http://ngm.
nationalgeographic.com/2013/04/species-revival/
zimmer-text.
3. The Tauros programme, www.taurosproject.com/.
4. J. Folch et al., Theriogenology 71, 1026 (2009).
5. M. Ridley, Wall Street Journal, 2 March 2013, p. C4.
6. H. H. Wang et al., Nat. Methods 9, 591 (2012).
7. P. Chavatte-Palmer et al., Placenta 33, (suppl.), S99
(2012).
8. 7 U.S.C. § 2131 et seq.
9. S. A. Zimov, Science 308, 796 (2005).
10. Pleistocene Park, www.pleistocenepark.ru/en/
background/.
11. 16 U.S.C. § 1533(a)(1)(A).
12. IUCN, IUCN Red List Categories and Criteria (1994);
http://www.iucnredlist.org/technical-documents/
categories-and-criteria/1994-categories-criteria.
13. Diamond v. Chakrabarty. 446 U.S. 303 (1980).
14. M. L. Rohrbaugh, AIPLA Q. J. 25, 371 (1997).
Acknowledgments: The authors participated in two work-
shops on de-extinction organized by Revive and Restore and
the National Geographic Society, one in February 2012 (H.G.)
and one in October 2012 (H.G. and J.S.). (H.G. was on the
planning committee for the second workshop.) We would like
to acknowledge the tremendous contribution the speakers at
those workshops made to our understanding of de-extinction
and the issues it raises.
10.1126/science.1236965
Published by AAAS
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(6128), 32-33. [doi: 10.1126/science.1236965]340Science Jacob S. Sherkow and Henry T. Greely (April 4, 2013) What If Extinction Is Not Forever?
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