http://geoengineeringourclimate.com/2015/03/26/the-international-legal-framework-for-climate-engineering-working-paper/

Geoengineering Our Climate?
A Working Paper Series on the Ethics, Politics and Governance of Climate
Engineering

Reynolds (2015) – The International Legal Framework for Climate Engineering

2015-03-20 at 19.32.06

Several of the key, recurring questions which loom over climate engineering
concern how countries would interact when some of them undertake or approve
actions which might impact other countries. May a state intentionally alter
the climate? What would its obligations be before, during, and after doing
so? What if a potentially impacted country protests or claims that is had
been harmed? What if the implementing country believed that its existence
was at risk due to impending climate change? What about private actors
attempting climate engineering, perhaps for profit? Is there an existing
legal instrument under which field tests with potential transboundary
impacts could be regulated? Are countries obligated to research or
implement climate engineering in order to prevent dangerous climate change?
May states claim credit for greenhouse gases (GHG) removed from the
atmosphere via carbon dioxide removal (CDR)?

Countries prevent and resolve international disputes through a variety of
mechanisms. One particularly important mechanism for preventing and
resolving conflicts among states is international law. This chapter
describes some international law which is applicable to climate
engineering, with a focus on international environmental law. It closes
with a brief synthesis and some recommendations for future developments.
First, though, it introduces international law, and suggests why climate
engineering is such a challenge for international environmental law and its
scholars.

International Law

International law is a collection of authoritative rules governing
countries’ actions, especially those which may impact other countries. That
is, sovereign states are its subjects. With limited exceptions,
international law governs neither the actions of individual persons nor
those of national governments which have only domestic impacts. These
governments may be, however, obligated to require, regulate, or prevent
certain actions by their citizens and residents, although the states are
not necessarily responsible for the actions of their persons.

Scholars offer a wide range of explanation for how and why international
law operates, and this often shapes their conclusions as to what it can
accomplish.[1] Some assert that it is an outgrowth of the shared values and
intersubjective understandings of those individuals who craft it, and that
it thus carries strong normative power. Others claim that national leaders
develop and implement international law in response to the domestic
constituencies who support them. Finally, a third group (which includes
this author) argues that states with differing levels of power and
capabilities rationally use international law as a means to coordinate,
cooperate, and coerce because it furthers their diverse interests.

The most important characteristic of international law is that there is
neither a central legislator nor central enforcement. This is unlike the
national law with which we are most familiar, which is developed through
legislative processes and enforced through the state’s threat of force. In
contrast, international law is a set of promises, customary behaviours, and
principles among purportedly co-equal sovereign states. These rules are of
varying explicitness, detail, and “firmness”, in the sense of their
rhetorical strength and the possible consequences of their violation.
Although these consequences are sometimes explicit in a treaty, most often
international law is enforced in three general, indirect ways.[2] A victim
country might reciprocate with the same violation back at the violator.
States may also retaliate in other, unrelated areas. Finally, the violator
frequently suffers in its reputation, and states are consequently less
likely to engage with it in ways which would have been beneficial. Notably,
enforcing international law is often costly for the enforcers, compounding
the challenge.

International law traditionally has three primary sources. Treaties are
explicit agreements among states which choose to participate. Most treaties
(or similar terms, such as agreements or conventions) are between two
countries, although some have many participants, called parties. Customary
international law is what all countries consistently do out of an apparent
sense of legal obligation, and applies to all states who do not explicitly
object. Finally, general principles are the guiding ideas upon which
treaties and customs are based, but are not themselves binding on their
own. The precise substance of customs and principles are not centrally
codified and thus sometimes disputed. Beyond these, the rulings of
international tribunals and intergovernmental organizations have become
important secondary sources within the international legal system.

Regardless, trying to make a sharp distinction between binding and
nonbinding international law is mostly unproductive, even though certain
components of it are clearly intended to be one or the other. Instead,
there is something of a gradation. Furthermore, countries, particularly the
powerful ones, sometimes violate explicitly binding agreements with little
consequence, especially if there is a widely shared sense that the action
was justified. Likewise, other countries, particularly the weak ones,
sometimes face sanction for actions which are not contrary to international
law. Although this implies that politics trumps international law at the
end of the day, the latter still has an impact by altering the incentives
which states face. Indeed, countries generally abide by international law.
This can be explained variously by its genuine effectiveness, its
ambiguity, or its mere embodiment of what countries would have done in its
absence.

The international law of the environment is relevant when a state’s actions
impact the environment of other states or of areas beyond national
jurisdiction and control, such as the high seas, Antarctica, or outer
space. For the most part, international environmental law is
anthropocentric, in that it protects the environment for people’s health
and for their natural resources.[3] Notably, it is intertwined with efforts
to overcome uneven economic development.[4] That is, all countries want
their own environments to be clean, but there are divisions of
international priorities: wealthy states generally emphasize global
environmental protection, while the poorer ones wish to develop
economically and are concerned that stringent international environmental
law could interfere with this.[5]

As a final note, international law as described arose when countries were
considered the exclusive actors in the international arena. In recent
decades, transnational nonstate actors have become increasingly
important—or at least recognized as such—both as sources and subjects of a
more broadly-defined system of international law.[6] Indeed, so-called
“global governance” instruments and institutions which rely less on states
than traditional law may be more effective in regulating transnational
nonstate actors, a group which includes scientists.

The Challenges of Climate
Engineering


Climate engineering presents difficulties for international environmental
law and its scholars. To some degree, this is due to its novelty: climate
engineering proposals have been seriously discussed for only a decade or
so. This situation is frequently seen with new technologies, as
international law moves slowly by design. In these cases, scholars and
practitioners are forced to interpret legal instruments which were
developed for decidedly different purposes.

I assert that climate engineering is especially challenging because it
presents three novel dynamics for international environmental law. First,
all climate engineering approaches- both CDR and SRM- could both prevent
and cause environmental harm. Removing GHGs or increasing albedo could
lower climate change risks while simultaneously creating new risks. For
example, solar climate engineering (solar radiation management, or SRM)
would unevenly compensate the temperature and precipitation anomalies of
climate change, and carbon dioxide removal methods may alter ecosystems,
crowd out food production, and create new industries of massive scales.[7]
In short, these are proposed interventions to protect humans and the
environment which may also harm humans and the environment. Indeed, both
climate change (or GHGs) and climate engineering often satisfy the
definitions of “pollution”, “damage,” or “adverse effects” which
environmental treaties try to prevent and reduce.[8] It is often unclear
how international environmental law should balance such tension.

Second, SRM climate engineering does not fit the mould of typical
environmental problem structures, which can usually be described
economically as negative externalities with the environment as their
medium. That is, some actors engage in activities which are beneficial for
them but have negative environmental consequences for others which are not
taken into consideration by the former. In the case of collective action
problems, the perpetrators are also among the victims, such as when several
countries fish on the high seas: each will harvest too much, leading to
fishery’s collapse for them all. In contrast, SRM appears to offer a large
positive externality through the reduction of climate risks whose value
would not be fully captured by the implementing actor.[9] Further, instead
of a need for collective action which brings a free rider problem, SRM
calls for collective restraint which brings a “free driver” problem.[10]
Therefore, although SRM would to some extent instigate traditional
environmental law mechanisms such as preventing, remedying, and
compensating for harm, it appears that its research and possible
implementation would primarily generate challenges such as coordination,
mutual restraint, and prevention of misuse.[11]

Finally, I suggest that there is a cultural barrier as well. The
contemporary awareness of environmental degradation which arose in the
1960s and later provided a cultural foundation for modern environmental law
is, at its core, a realization that we have not adequately accounted for
the full environmental consequences of our actions. This usually includes a
belief that certain large scale, high technology endeavours have attempted
to intervene in nature in ways which were dangerous and insufficiently
understood. Most of the environmental movement has responded by calling for
greater humility, increased scepticism of our knowledge and technology, and
placing the natural world more centrally in our decision making processes
and value systems. In this context, climate engineering “runs afoul of
almost every major trend in contemporary environmentalism”.[12] To the
extent that this is the narrative behind the rise of environmental law, a
logical reaction has been to see climate engineering not as a potential
means to reduce net climate risks but instead as the latest in a series of
hubristic technological threats to a fragile global environment.

Applicable Existing International Law

Here, I briefly review the most relevant existing international law in the
context of climate engineering. Unsurprisingly, most of this falls under
the rubric of international environmental law, although other domains will
be briefly touched upon at the section’s end. Unless otherwise stated,
these instruments and provisions apply to all climate engineering
techniques which would pose transboundary risks. However, some proposed
methods—especially some within SRM—are more likely to do so.

International Environmental Law

International environmental law is the logical starting point for
considering how international law may be able to prevent and resolve
disputes arising from climate engineering. International environmental law
is not a distinct domain but instead merely the subset of international law
which relates to how states may impact each other via the environment.
Although what is and is not an environmental matter is unclear (e.g., is
liability for harm from space activities an environmental issue?), this
need not be resolved here.

As a starting point, states’ sovereignty means that they are free to govern
their people and to manage their resources within their territory as they
deem appropriate, provided that such actions do not harm other
countries.[13] Per customary law, if an activity not otherwise contrary to
international law poses a risk of causing significant transboundary
harm—including a high chance of typical harm and a low chance of
“disastrous” harm—then the country of origin is obligated to take
appropriate measures to prevent or reduce the harm; to review and (if
appropriate) to authorize risky activities; to assess potential
environmental impacts; to notify, consult, and cooperate with those
countries likely to be affected; to notify the likely affected public; to
develop plans in case of an emergency; and to monitor an activity’s ongoing
effects.[14] In other words, the source state is to act with due diligence.
Importantly, this is not to be done solely to minimize transboundary
environmental harm but instead to equitably balance states’ interests,
including the benefits, importance, and risks of the activity; those of
available alternatives; and the costs of prevention. If an incident may
cause transboundary harm from a hazardous activity, the source state is
obligated to notify, consult with, and cooperate with the likely affected
countries in order to take appropriate response measures, while the likely
affected countries are to take all feasible measures to mitigate the
damage.[15] Afterwards, those states which have caused transboundary harm
through an action which is not contrary to international law must stop the
activity; assure that it will not reoccur; make reparations for the harm
through restitution, prompt and adequate compensation (including by strict
liability on the operators of hazardous activities), and satisfaction such
as an apology; and provide access to legal remedies for victims.[16]

Several environmental agreements would be relevant in the case of climate
engineering. Only a handful of treaties and treaty systems are discussed
here; others would be applicable only in limited geographical areas and/or
with particular climate engineering methods.[17] The most important is the
UN Framework Convention on Climate Change (UNFCCC), which now includes
essentially all countries as parties. Its objective of stabilizing
greenhouse gases at safe levels and its binding commitments clearly
indicate that CDR lies within its purview.[18] Among the commitments are
two which call for the enhancement of sinks and reservoirs.[19] The
UNFCCC’s Kyoto Protocol is more explicit, requiring its parties to research
and promote “carbon dioxide sequestration technologies and… advanced and
innovative environmentally sound technologies.”[20] The questions as to
whether particular CDR methods could be included toward a country’s
accounting of its net GHG emissions and whether they could be eligible for
credit under international emission trading systems are important yet
remain unresolved. The debates concerning the effects of forests,
agriculture, and land use on GHG concentrations have dragged on for decades
due in part to the complexity and uncertainty of their net long term
impacts; CDR methods will likely face a similarly difficult path.

The relationship between the UNFCCC and SRM is less clear. On one hand,
these methods would not contribute toward its objective of GHG
stabilization. On the other hand, there are several references among its
principals, priorities, and commitments which imply at least the
consideration of SRM, perhaps through research. For example, the document’s
aspirational language calls for the minimization of the “adverse effects of
climate change” in a rapid and inexpensive manner “so as to ensure global
benefits at the lowest possible cost”, for anthropocentric reasons, and in
balance with objectives such as economic development and food
production.[21] SRM may allow this to be done. Several commitments are to
undertake research and to develop and diffuse new technologies in order to
reduce uncertainty, including that of “various response strategies”.[22]
Nevertheless, the mandate for the UNFCCC is unclear with regard to SRM, and
whether its institutions will address the matter is ultimately a political
matter.[23]

The Convention on Biological Diversity (CBD) may be the most important
general environmental treaty due to its broad provisions to protect
biodiversity—which is impacted by many large scale human activities—and to
its near-universal participation.[24] Among other things, it obligates its
parties to comply with several procedural duties, such as monitoring,
concerning activities which are likely to have “significant adverse
impacts” on biodiversity, which some climate engineering methods would.[25]
Perhaps more importantly, its Conference of Parties has taken an interest,
agreeing to three statements regarding climate engineering.[26] That of the
2010 Conference is the only statement on climate engineering in general
which originated in a near-universal international legal forum. It is a
nonbinding statement of caution, asking the parties to refrain from climate
engineering that may affect biodiversity until there is scientific basis
for such work and “appropriate consideration of the associated risks”. This
request is to continue “in the absence of science based, global,
transparent and effective control and regulatory mechanisms”. It makes an
exception for small scale scientific activities.

The Environmental Modification Convention (ENMOD) is a less well-known
multilateral agreement which prohibits the military application of weather
modification methods.[27] Its definition of “environmental modification
techniques” would include most proposed large scale forms of climate
engineering, and its parties may not use these for any “military or any
other hostile use”.[28] Notably, the agreement explicitly “shall not hinder
the use of environmental modification techniques for peaceful purposes” and
encourages peaceful applications of environmental modification.[29]
Although ENMOD includes most industrialized countries among its parties, it
has no supporting infrastructure and is essentially dormant.[30]

The comprehensive UN Convention on the Law of the Sea (UNCLOS), with
near-universal participation, would govern climate engineering activities
which take place at sea or which would affect the marine environment.[31]
Under it, states’ obligation to protect the marine environment is without
qualification.[32] As noted in the previous section, its definition of
“pollution” which states are obligated to “prevent, reduce, and control”
includes climate change, GHGs, and climate engineering activities which are
likely to be harmful.[33] UNCLOS strongly supports scientific research
provided that, among other things, it does not interfere with other states’
legitimate uses of the sea and it is consistent with protection of the
marine environment.[34] The seas are divided into three zones, in which the
first twelve miles are the territorial waters of the coastal states, up to
200 miles are the quasi-territorial “exclusive economic zone”, and beyond
that are the high seas, without national jurisdiction. Ships themselves are
the jurisdiction of their flag state whose national laws apply to their
crews.

The CDR method of ocean fertilization warrants particular attention. It is
the exception to the general rule that CDR would present
well-characterized, low environmental risks and can mostly be regulated by
domestic law. It also the only (thus far) potentially high risk climate
engineering method to be repeatedly tested in the open environment.[35]
These outdoor experiments were conducted by universities and other public
research institutions during the 1990s and 2000s. However, in reaction to
private actors which intended to fertilize the oceans to try to obtain
marketable carbon credits, the parties to the London Convention and London
Protocol—which govern dumping in the high seas—developed two regulatory
systems for its parties.[36] The first is a nonbinding process under which
the states’ national environmental regulatory agency review and, if
appropriate, approve an ocean fertilization field test if it is legitimate
scientific research, has undergone adequate environmental impact
assessment, and satisfies other procedural requirements.[37] The second is
an amendment—approved but not yet in force—to the London Protocol. Under
this, its parties could either prohibit or regulate various forms of
“marine geoengineering.” To date, only ocean fertilization has been so
categorized by the parties, in its case as a regulated activity.[38]

In addition to treaties, countries regularly approve statements which are
not intended to be legally binding but, like the statements of the CBD’s
parties, indicate a sense of the international community. One of particular
relevance is the Provisions for Co-operation between States in Weather
Modification, approved by the UN Environmental Programme in 1980.[39]
Despite the name, its relevant definition clearly includes SRM. It is
supportive of weather modification “dedicated to the benefit of mankind
[sic] and the environment”, asks states to not use it to cause harm to the
environment of other states and areas beyond national jurisdiction, and
calls for cooperation and communication among states.

The final source of traditional international environmental law is its
general principles. These remain weakly defined and not legally binding
until they are operationalized in a particular agreement. For the case of
climate engineering, the most relevant principles (among those which are
not yet embodied as customary international law) are those of sustainable
development (states should develop their resources in a sustainable
manner), polluter pays (the source state rather than the victim should pay
for environmental harm and its prevention), common but differentiated
responsibilities (all countries have responsibilities to prevent
environmental harm but these responsibilities differ, largely based on a
state’s stage of economic development), and precaution (when confronting a
risk of serious or irreversible harm, scientific uncertainty should not be
used as a reason to postpone precautionary measures). Reasonable arguments
could be made that the research or implementation of climate engineering is
supported by or is contrary to each of these.[40] This should not be
surprising, considering the principles’ inchoate character and the peculiar
challenges which climate engineering presents for international
environmental law, described above.

Other International Law

A handful of international legal instruments outside of the environmental
domain warrant brief reference. Numerous observers have asserted that
disagreements regarding SRM could heighten tensions among states. The UN
Charter requires international disputes to be settled peacefully.[41] Of
course, if there were actually full compliance with this, then interstate
hostilities would cease. Disputes are primarily political matters which may
be settled through a variety of means such as negotiation, mediation,
arbitration, and, in some cases, international legal forums. The legal
forum with the broadest mandate is the UN General Assembly, which can take
up almost any matter but issue only nonbinding statements.[42] In contrast,
the UN Security Council is limited to the “maintenance of international
peace and security” and can issue binding, non-consensual (i.e.
majoritarian) resolutions, although five of the most powerful countries
have veto power.[43] These resolutions can be backed by the threat of
force, including sanctions and military action, which would then need to be
carried out by willing UN member states. The International Court of Justice
is another forum for dispute resolution. Although its rulings may be
enforced by the Security Council, states must consent to the court’s
jurisdiction in the case at hand before the trial of a contentious issue in
order for its later ruling to actually be binding. Finally, some treaties
contain dispute resolution forums which are applicable within their
particular scope.

Human rights agreements provide an exception to the rule that international
law governs actions which may impact other states. Under these, parties
agree to treat their own citizens and residents in a manner consistent with
various norms. One could imagine scenarios wherein climate engineering
implementation, or the withholding of it in the face of dangerous climate
change, could violate the human rights to health, life, and development.

The development of climate engineering could lead to patented inventions.
Patents, which grant their holder the exclusive right to commercially
utilize an invention, are domestically issued, while patent policy is
internationally coordinated and harmonized. National governments may take
two notable actions regarding patents as potentially controversial and
important as those for climate engineering techniques. First, they may
decide to exclude certain climate engineering methods from patentability
because they would be contrary to public morality, including “to avoid
serious prejudice to the environment”.[44] They may also choose to compel a
patent holder to license the patent due to public interest considerations,
such as on the grounds of national defence or public health.[45]

Finally, as described in the previous section, nonstate instruments and
institutions can be effective in regulating transboundary actors such as
scientists. The contours of such global governance may be emerging in the
case of climate engineering. Most notable has been the development of
explicit, nonbinding norms. Their sources are somewhat disparate: the
Oxford Principles from a handful of British academics, the Asilomar
Principles from a large meeting of climate engineering researchers and
research advocates, the report from a task force assembled by the US
Bipartisan Policy Center, and a report issued by a think tank affiliated
with the German Green Party.[46] There is remarkable overlap among these
four sets, and there are no clear disagreements among them. Among other
things, these variously call for public participation in decision making,
for open publication and independent assessment of results, and for climate
engineering to be developed in a manner which benefits the collective
public.

Synthesis and Next Steps

Some observers argue that because existing international law does not
address all potential scenarios of conflict and harm from climate
engineering, the solution is universal binding regulation of climate
engineering through legal instruments. However, it may be beneficial to
first take stock of extant law, the urgency of filling the legal gaps, and
the limits of international law. In general, the UNFCCC establishes a
framework for how CDR could contribute to the goal of stabilizing GHG
concentrations, and it might offer a foundation for the governance of SRM
as well.[47] ENMOD and the UNEP Provisions for Weather Modification point
toward the international community’s support of using large scale
interventions in weather and climatic systems for the benefit of humans and
the environment, while the 2010 CBD statement provides its sense of caution
regarding climate engineering’s potential negative environmental impacts.
Further, universal duties concerning potential transboundary harm are
well-established in customary international law, and in some cases by
specific agreements.[48] The areas beyond national jurisdiction and control
each have agreements with sufficient participation and which details their
parties’ rights and obligations.[49] Of these areas, the seas are the most
likely site for climate engineering experimentation and implementation, and
it is there that there are detailed agreements, including one with
near-universal participation and a tribunal to resolve disputes. In fact,
it is ocean fertilization—the method which poses relatively large
environmental risks and has seen the most progress in outdoor research—for
which a detailed international regulatory regime is emerging. Finally,
unilateral implementation of SRM by weak or “rogue” countries could, in
extreme scenarios, be tackled by the UN Security Council. Although not
comprehensive, this is far from a legal vacuum.

In terms of urgency, most climate engineering proposals—especially
relatively early field experiments—would affect the local environment first
and foremost; that is the domain of national law, which is well-developed
in most states, and especially in those which are likely to carry out field
tests. Those proposed methods which might be effective and have regional or
global impacts are decades away from implementation. Large scale field
research is a more pressing matter. There, the domain is highly dynamic,
and binding, detailed rules would quickly become obsolete, particularly in
the international domain which moves more slowly.

Finally, international law has limits, and not all potential international
conflicts should be subject to specific legal rules. International
politics—another means to manage conflicts—may appear sloppy, improvised,
and sometimes unjust, but it is adaptive and flexible. This may be
precisely what’s needed as climate engineering emerges.

At the same time, there are some gaps in the current international legal
system which are relatively urgent but also resolvable. First, an
international hub of scientific research could fulfil multiple beneficial
functions.[50] It could coordinate research and foster international
collaboration, a low cost means to increase transparency and trust as well
as to combat the nationalization and fragmentation of research. An
international body could also serve as an open repository of experiments’
methodologies and results. And it could provide a site for the
operationalisation of emerging research norms and possibly even their
enforcement through both “carrots” and “sticks”. Second, special
international rules for intellectual property in climate engineering should
be developed. There appears to be a consensus that patents on SRM
technologies could be problematic. Their limits should be determined, and
alternative mechanisms and incentives should be considered, before such
patents become “facts on the ground”. Third, international institutions
should resolve to what extent the various CDR methods could qualify toward
countries’ GHG emissions and for marketable credits. Lastly, a system of
compensation for transboundary harm from climate engineering—particularly
its field research—should be seriously considered.[51]

Legal scholarship can also contribute to better understanding of climate
engineering regulation. It is now almost twenty years since the first
academic article on climate engineering and international environmental
law.[52] This area has been further—and fruitfully—explored in numerous
publications, especially during the last five years. Yet national laws are
more detailed and better enforced than international law, and most effects
of early climate engineering projects will likely be experienced locally.
Explorations of the implications of national law for climate engineering
are an opportunity for work in the near future.

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Governance of Free-Driver Externalities, with Application to
Geoengineering. Scandinavian Journal of Economics. [1] See Dunoff and
Pollack 2012, ch. 3-6. [2] Guzman 2008 [3] Birnie et al. 2009, 7 [4] The
Rio Declaration—arguably the most important general document in
international environmental law—attempts to balance environmental and
development goals under the rubric of “sustainable development” and the
principle of common but differentiated responsibility. Rio Declaration on
Environment and Development, adopted June 14, 1992, 31 I.L.M. 874
[hereinafter Rio Declaration]. This latter principle is also seen in
obligations to take action to prevent dangerous climate change. United
Nations Framework Convention on Climate Change, art. 3.1, 4.1, May 9, 1992,
1771 U.N.T.S. 171 [hereinafter UNFCCC]. [5] Najam 2005 [6] Biermann and
Pattberg 2008 [7] For reviews, see McNutt et al. 2015a, McNutt et al.
2015b. [8] Convention on Long-Range Transboundary Air Pollution, art. 1,
Nov. 13, 1979, 1302 U.N.T.S. 219; United Nations Convention on the Law of
the Sea, art. 1.1.4, Dec. 10, 1982, 1833 U.N.T.S. 3 [hereinafter UNCLOS];
Vienna Convention for the Protection of the Ozone Layer, art. 1.2, Mar. 22,
1985, 1513 U.N.T.S. 293; Protocol on Environmental Protection to the
Antarctic Treaty, art. 3.2, Oct. 4, 1991, 30 I.L.M. 1461 [hereinafter
Madrid Protocol]; UNFCCC, art. 1; Convention on Biological Diversity, arts.
7(c), 8, June 5, 1992, 1760 U.N.T.S. 79 [hereinafter CBD]; Convention for
the Protection of the Marine Environment of the North-East Atlantic, art.
1(d), Sept. 22, 1992, 2354 U.N.T.S. 67. [9] Indeed, current modelling
indicates that some forms of it could greatly reduce net climate risks at
low cost and in a short time. The Intergovernmental Panel on Climate Change
recently concluded that: “Models consistently suggest that SRM would
generally reduce climate differences compared to a world with elevated
greenhouse gas concentrations and no SRM…” Boucher et al. 2013, 575. See
also Kravitz et al. 2014. [10] The term “free driver” is from Weitzman
2015. [11] See Bodansky 2012. [12] Michaelson 1998, 81 [13] Rio
Declaration, principle 2. [14] Although customary international law is not
codified, the reports of the International Law Commission are
authoritative. See International Law Commission 2001a. [15] International
Law Commission 2006 [16] Ibid; International Law Commission 2001b [17] For
a more in-depth treatment, see Bodle et al. 2013; Reynolds 2014. [18]
UNFCCC, arts 2, 4. [19] Ibid, arts. 4.1(d), 4.2(a). [20] Kyoto Protocol to
the United Nations Framework Convention on Climate Change, art. 2.1(a)(iv),
Dec. 11, 1997, 2303 U.N.T.S. 148. Note that the US is a not a party to the
Kyoto Protocol. [21] UNFCCC, arts. 1.1, 2, 3.1, 3.3. [22] Ibid, arts.
4.1(g) and (h), 4.3, 4.7, 4.8, 4.9, 11.1. [23] See Reynolds 2015 in this
volume. [24] The US is not a party. [25] CBD, art. 7(c). [26] Ninth Meeting
of the Conference of Parties to the Convention on Biological Diversity, May
19-30, 2008, Decision IX/16—Biodiversity and Climate Change 7, U.N. Doc.
UNEP/CBD/COP/DEC/IX/16 (2008); Tenth Meeting of the Conference of Parties
to the Convention on Biological Diversity, Oct. 18-29, 2010, Decision
X/33—Biodiversity and Climate Change 5, U.N. Doc. UNEP/CBD/COP/DEC/X/33
(2010); Eleventh Meeting of the Conference of Parties to the Convention on
Biological Diversity, Oct. 8-19, 2012, Decision XI/20 — Climate
Climate-related geoengineering, U.N. Doc. UNEP/CBD/COP/DEC/XI/20 (2012).
[27] Convention on the Prohibition of Military or Any Other Hostile Use of
Environmental Modification Techniques, Dec. 10, 1976, 1108 U.N.T.S. 151.
[28] Ibid, arts. I.1, II. [29] Ibid, pmbl., art III. [30] The treaty
neither creates standing institutions nor calls for a regular meeting of
its parties. Review conferences were held in 1984 and 1992, but in 2014
there was insufficient interest in a third. No complaints have ever been
filed under it, and its Consultative Committee of Experts has never been
convened. [31] The US is not a party but recognizes most of it as customary
international law. [32] UNCLOS, art. 192. [33] Ibid, art. 1.1(4). [34]
Ibid, pmbl. para. 4, arts. 87.1, 88, 192, 238–240, 243, 251, 255, 257. [35]
See Doughty 2015 in this volume for a review of the one or two SRM field
tests which have occurred. [36] Convention on the Prevention of Marine
Pollution by Dumping of Wastes and Other Matter, Nov. 13, 1972, 1046
U.N.T.S. 120; Protocol to the Convention on the Prevention of Marine
Pollution by Dumping of Wastes and Other Matter 1972, Nov. 7, 1996, 11
U.K.T.S. Cm. 4078. Note that the London Protocol, presently with 45
parties, is indented to replace the London Convention, with 87 parties,
although both are in force. Most industrialized and transitional countries
are parties to at least one. [37] Resolution LC-LP.2 on the Assessment
Framework for Scientific Research Involving Ocean Fertilization, I.M.O.
Doc. LC 32/15/Annex 6 (2010). This was approved by a joint meeting of
Parties to both agreements. [38] Resolution LP.4(8) on the Amendment to the
London Protocol to Regulate the Placement of Matter for Ocean Fertilization
and Other Marine Geoengineering Activities, I.M.O. Doc. LC 35/15/Annex 4
(2013). [39] Provisions for Co-operation between States in Weather
Modification, U.N.E.P. Dec. 8/7/A, U.N. Doc. UNEP/GC/8/7/A (1980). [40] See
Reynolds 2014, where I argue that at least the latter three of these
principles supports climate engineering field research. [41] Charter of the
United Nations and Statute of the International Court of Justice, art.
2(3), June 26, 1945, 1 U.N.T.S. 16. [42] Ibid, chapter IV. [43] Ibid,
chapter V, VII. [44] Agreement on Trade-Related Aspects of Intellectual
Property Rights, art. 27.2, Apr. 15, 1994, 1869 U.N.T.S. 299 [hereinafter
TRIPS]. [45] TRIPS, the European Patent Organization, and the North
American Free Trade Agreement all permit their parties both patent
exclusions and compulsory licenses. Ibid, arts. 27.2, 31; Convention on the
Grant of European Patents, art. 53(a), Oct. 5, 1973, 1065 U.N.T.S. 199;
North American Free Trade Agreement, U.S.-Can.-Mex., art. 1709, Dec. 17,
1992, 32 I.L.M. 289; Tudor 2012. [46] Bipartisan Policy Center’s Task Force
on Climate Remediation 2011; Leinen 2011; Kössler 2012; Rayner et al. 2013
See also Hanafi and Hamburg 2013 in this volume. [47] But see Reynolds 2015
in this volume. [48] E.g. Convention on Environmental Impact Assessment in
a Transboundary Context, Feb. 25, 1991, 1989 U.N.T.S. 309. [49] UNCLOS;
Madrid Protocol; Treaty on Principles Governing the Activities of States in
the Exploration and Use of Outer Space, including the Moon and Other
Celestial Bodies, Dec. 19, 1966, 610 U.N.T.S. 205. [50] See Ghosh 2014 in
this volume. [51] See Horton et al. 2013 in this volume. [52] Bodansky 1996

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